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Title 50: Wildlife and Fisheries
PART 17—ENDANGERED AND THREATENED
WILDLIFE AND PLANTS
Contents
Subpart A—Introduction and General Provisions
§17.1
§17.2
§17.3
§17.4
§17.5
§17.6
§17.7
§17.8
§17.9
Purpose of regulations.
Scope of regulations.
Definitions.
Pre-Act wildlife.
Alaska natives.
State cooperative agreements. [Reserved]
Raptor exemption.
Import exemption for threatened, CITES Appendix-II wildlife.
Permit applications and information collection requirements.
Subpart B—Lists
§17.11 Endangered and threatened wildlife.
§17.12 Endangered and threatened plants.
Subpart C—Endangered Wildlife
§17.21 Prohibitions.
§17.22 Permits for scientific purposes, enhancement of propagation or survival, or for incidental taking.
§17.23 Economic hardship permits.
Subpart D—Threatened Wildlife
§17.31 Prohibitions.
§17.32 Permits—general.
§17.40 Special rules—mammals.
§17.41
§17.42
§17.43
§17.44
§17.45
§17.46
§17.47
§17.48
Special rules—birds.
Special rules—reptiles.
Special rules—amphibians.
Special rules—fishes.
Special rules—snails and clams. [Reserved]
Special rules—crustaceans.
Special rules—insects.
Special rules—common sponges and other forms. [Reserved]
Subpart E—Similarity of Appearance
§17.50 General.
§17.51 Treatment as endangered or threatened.
§17.52 Permits—similarity of appearance.
Subpart F—Endangered Plants
§17.61 Prohibitions.
§17.62 Permits for scientific purposes or for the enhancement of propagation or survival.
§17.63 Economic hardship permits.
Subpart G—Threatened Plants
§17.71 Prohibitions.
§17.72 Permits—general.
§§17.73-17.78 [Reserved]
Subpart H—Experimental Populations
§17.80
§17.81
§17.82
§17.83
§17.84
§17.85
§17.86
Definitions.
Listing.
Prohibitions.
Interagency cooperation.
Special rules—vertebrates.
Special rules—invertebrates.
Special rules—plants. [Reserved]
Subpart I—Interagency Cooperation
§17.94 Critical habitats.
§17.95 Critical habitat—fish and wildlife.
Authority: 16 U.S.C. 1361-1407; 1531-1544; and 4201-4245, unless otherwise noted.
Source: 40 FR 44415, Sept. 26, 1975, unless otherwise noted.
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Subpart A—Introduction and General Provisions
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§17.1 Purpose of regulations.
(a) The regulations in this part implement the Endangered Species Act of 1973, 87 Stat. 884, 16 U.S.C. 15311543, except for those provisions in the Act concerning the Convention on International Trade in Endangered
Species of Wild Fauna and Flora, for which regulations are provided in part 23 of this subchapter.
(b) The regulations identify those species of wildlife and plants determined by the Director to be endangered or
threatened with extinction under section 4(a) of the Act and also carry over the species and subspecies of wildlife
designated as endangered under the Endangered Species Conservation Act of 1969 (83 Stat. 275, 16 U.S.C.
668cc-1 to 6) which are deemed endangered species under section 4(c)(3) of the Act.
[40 FR 44415, Sept. 26, 1975, as amended at 42 FR 10465, Feb. 22, 1977]
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§17.2 Scope of regulations.
(a) The regulations of this part apply only to endangered and threatened wildlife and plants.
(b) By agreement between the Service and the National Marine Fisheries Service, the jurisdiction of the
Department of Commerce has been specifically defined to include certain species, while jurisdiction is shared in
regard to certain other species. Such species are footnoted in subpart B of this part, and reference is given to
special rules of the National Marine Fisheries Service for those species.
(c) The provisions in this part are in addition to, and are not in lieu of, other regulations of this subchapter B which
may require a permit or prescribe additional restrictions or conditions for the importation, exportation, and
interstate transportation of wildlife.
(d) The examples used in this part are provided solely for the convenience of the public, and to explain the intent
and meaning of the regulation to which they refer. They have no legal significance.
(e) Certain of the wildlife and plants listed in §§17.11 and 17.12 as endangered or threatened are included in
Appendix I, II or III to the Convention on International Trade in Endangered Species of Wild Fauna and Flora. The
importation, exportation and reexportation of such species are subject to additional regulations provided in part 23
of this subchapter.
[40 FR 44415, Sept. 26, 1975, as amended at 42 FR 10465, Feb. 22, 1977]
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§17.3 Definitions.
In addition to the definitions contained in part 10 of this subchapter, and unless the context otherwise requires, in
this part 17:
Act means the Endangered Species Act of 1973 (16 U.S.C. 1531-1543; 87 Stat. 884);
Adequately covered means, with respect to species listed pursuant to section 4 of the ESA, that a proposed
conservation plan has satisfied the permit issuance criteria under section 10(a)(2)(B) of the ESA for the species
covered by the plan, and, with respect to unlisted species, that a proposed conservation plan has satisfied the
permit issuance criteria under section 10(a)(2)(B) of the ESA that would otherwise apply if the unlisted species
covered by the plan were actually listed. For the Services to cover a species under a conservation plan, it must be
listed on the section 10(a)(1)(B) permit.
Alaskan Native means a person defined in the Alaska Native Claims Settlement Act (43 U.S.C. 1603(b) (85 Stat.
588)) as a citizen of the United States who is of one-fourth degree or more Alaska Indian (including Tsimshian
Indians enrolled or not enrolled in the Metlaktla Indian Community), Eskimo, or Aleut blood, or combination
thereof. The term includes any Native, as so defined, either or both of whose adoptive parents are not Natives. It
also includes, in the absence of proof of a minimum blood quantum, any citizen of the United States who is
regarded as an Alaska Native by the Native village or town of which he claims to be a member and whose father
or mother is (or, if deceased, was) regarded as Native by any Native village or Native town. Any citizen enrolled by
the Secretary pursuant to section 5 of the Alaska Native Claims Settlement Act shall be conclusively presumed to
be an Alaskan Native for purposes of this part;
Authentic native articles of handicrafts and clothing means items made by an Indian, Aleut, or Eskimo that are
composed wholly or in some significant respect of natural materials and are significantly altered from their natural
form and are produced, decorated, or fashioned in the exercise of traditional native handicrafts without the use of
pantographs, multiple carvers, or similar mass-copying devices. Improved methods of production utilizing modern
implements such as sewing machines or modern techniques at a tannery registered pursuant to §18.23(c) of this
subchapter (in the case of marine mammals) may be used as long as no large-scale mass production industry
results. Traditional native handicrafts include, but are not limited to, weaving, carving, stitching, sewing, lacing,
beading, drawing, and painting. The formation of traditional native groups, such as cooperatives, is permitted as
long as no large-scale mass production results;
Bred in captivity or captive-bred refers to wildlife, including eggs, born or otherwise produced in captivity from
parents that mated or otherwise transferred gametes in captivity, if reproduction is sexual, or from parents that
were in captivity when development of the progeny began, if development is asexual.
Captivity means that living wildlife is held in a controlled environment that is intensively manipulated by man for the
purpose of producing wildlife of the selected species, and that has boundaries designed to prevent animal, eggs or
gametes of the selected species from entering or leaving the controlled environment. General characteristics of
captivity may include but are not limited to artificial housing, waste removal, health care, protection from predators,
and artificially supplied food.
Changed circumstances means changes in circumstances affecting a species or geographic area covered by a
conservation plan or agreement that can reasonably be anticipated by plan or agreement developers and the
Service and that can be planned for (e.g., the listing of new species, or a fire or other natural catastrophic event in
areas prone to such events).
Conservation plan means the plan required by section 10(a)(2)(A) of the ESA that an applicant must submit when
applying for an incidental take permit. Conservation plans also are known as “habitat conservation plans” or
“HCPs.”
Conserved habitat areas means areas explicitly designated for habitat restoration, acquisition, protection, or other
conservation purposes under a conservation plan.
Convention means the Convention on International Trade in Endangered Species of Wild Fauna and Flora, TIAS
8249.
Enhance the propagation or survival, when used in reference to wildlife in captivity, includes but is not limited to
the following activities when it can be shown that such activities would not be detrimental to the survival of wild or
captive populations of the affected species:
(a) Provision of health care, management of populations by culling, contraception, euthanasia, grouping or
handling of wildlife to control survivorship and reproduction, and similar normal practices of animal husbandry
needed to maintain captive populations that are self-sustaining and that possess as much genetic vitality as
possible;
(b) Accumulation and holding of living wildlife that is not immediately needed or suitable for propagative or
scientific purposes, and the transfer of such wildlife between persons in order to relieve crowding or other
problems hindering the propagation or survival of the captive population at the location from which the wildlife
would be removed; and
(c) Exhibition of living wildlife in a manner designed to educate the public about the ecological role and
conservation needs of the affected species.
Endangered means a species of wildlife listed in §17.11 or a species of plant listed in §17.12 and designated as
endangered.
Harass in the definition of “take” in the Act means an intentional or negligent act or omission which creates the
likelihood of injury to wildlife by annoying it to such an extent as to significantly disrupt normal behavioral patterns
which include, but are not limited to, breeding, feeding, or sheltering. This definition, when applied to captive
wildlife, does not include generally accepted:
(1) Animal husbandry practices that meet or exceed the minimum standards for facilities and care under the
Animal Welfare Act,
(2) Breeding procedures, or
(3) Provisions of veterinary care for confining, tranquilizing, or anesthetizing, when such practices, procedures, or
provisions are not likely to result in injury to the wildlife.
Harm in the definition of “take” in the Act means an act which actually kills or injures wildlife. Such act may include
significant habitat modification or degradation where it actually kills or injures wildlife by significantly impairing
essential behavioral patterns, including breeding, feeding or sheltering.
Incidental taking means any taking otherwise prohibited, if such taking is incidental to, and not the purpose of, the
carrying out of an otherwise lawful activity.
Industry or trade in the definition of “commercial activity” in the Act means the actual or intended transfer of wildlife
or plants from one person to another person in the pursuit of gain or profit;
Native village or town means any community, association, tribe, clan or group;
Operating conservation program means those conservation management activities which are expressly agreed
upon and described in a conservation plan or its Implementing Agreement, if any, and which are to be undertaken
for the affected species when implementing an approved conservation plan, including measures to respond to
changed circumstances.
Population means a group of fish or wildlife in the same taxon below the subspecific level, in common spatial
arrangement that interbreed when mature;
Properly implemented conservation plan means any conservation plan, Implementing Agreement and permit
whose commitments and provisions have been or are being fully implemented by the permittee.
Property owner with respect to agreements outlined under §§17.22(c), 17.22(d), 17.32(c), and 17.32(d) means a
person with a fee simple, leasehold, or other property interest (including owners of water or other natural
resources), or any other entity that may have a property interest, sufficient to carry out the proposed management
activities, subject to applicable State law, on non-Federal land.
Specimen means any animal or plant, or any part, product, egg, seed or root of any animal or plant;
Subsistence means the use of endangered or threatened wildlife for food, clothing, shelter, heating, transportation
and other uses necessary to maintain the life of the taker of the wildlife, or those who depend upon the taker to
provide them with such subsistence, and includes selling any edible portions of such wildlife in native villages and
towns in Alaska for native consumption within native villages and towns;
Threatened means a species of wildlife listed in §17.11 or plant listed in §17.12 and designated as threatened.
Unforeseen circumstances means changes in circumstances affecting a species or geographic area covered by a
conservation plan or agreement that could not reasonably have been anticipated by plan or agreement developers
and the Service at the time of the conservation plan's or agreement's negotiation and development, and that result
in a substantial and adverse change in the status of the covered species.
Wasteful manner means any taking or method of taking which is likely to result in the killing or injury of endangered
or threatened wildlife beyond those needed for subsistence purposes, or which results in the waste of a substantial
portion of the wildlife, and includes without limitation the employment of a method of taking which is not likely to
assure the capture or killing of the wildlife, or which is not immediately followed by a reasonable effort to retrieve
the wildlife.
[40 FR 44415, Sept. 26, 1975, as amended at 42 FR 28056, June 1, 1977; 44 FR 54006, Sept. 17, 1979; 46 FR
54750, Nov. 4, 1981; 47 FR 31387, July 20, 1982; 50 FR 39687, Sept. 30, 1985; 63 FR 8870, Feb. 23, 1998; 63
FR 48639, Sept. 11, 1998; 69 FR 24092, May 3, 2004; 71 FR 46870, Aug. 15, 2006]
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§17.4 Pre-Act wildlife.
(a) The prohibitions defined in subparts C and D of this part 17 shall not apply to any activity involving endangered
or threatened wildlife which was held in captivity or in a controlled environment on December 28, 1973: Provided,
(1) That the purposes of such holding were not contrary to the purposes of the Act; and
(2) That the wildlife was not held in the course of a commercial activity.
Example 1. On January 25, 1974, a tourist buys a stuffed hawksbill turtle (an endangered species listed since
June, 1970), in a foreign country. On December 28, 1973, the stuffed turtle had been on display for sale. The
tourist imports the stuffed turtle into the United States on January 26, 1974. This is a violation of the Act since the
stuffed turtle was held for commercial purposes on December 28, 1973.
Example 2. On December 27, 1973 (or earlier), a tourist buys a leopard skin coat (the leopard has been listed as
endangered since March 1972) for his wife in a foreign country. On January 5, he imports it into the United States.
He has not committed a violation since on December 28, 1973, he was the owner of the coat, for personal
purposes, and the chain of commerce had ended with the sale on the 27th. Even if he did not finish paying for the
coat for another year, as long as he had possession of it, and he was not going to resell it, but was using it for
personal purposes, the Act does not apply to that coat.
Example 3. On or before December 28, 1973, a hunter kills a leopard legally in Africa. He has the leopard
mounted and imports it into the United States in March 1974. The importation is not subject to the Act. The hunter
has not engaged in a commercial activity, even though he bought the services of a guide, outfitters, and a
taxidermist to help him take, preserve, and import the leopard. This applies even if the trophy was in the
possession of the taxidermist on December 28, 1973.
Example 4. On January 15, 1974, a hunter kills a leopard legally in Africa. He has the leopard mounted and
imports it into the United States in June 1974. This importation is a violation of the Act since the leopard was not in
captivity or a controlled environment on December 28, 1973.
(b) Service officers or Customs officers may refuse to clear endangered or threatened wildlife for importation into
or exportation from the United States, pursuant to §14.53 of this subchapter, until the importer or exporter can
demonstrate that the exemption referred to in this section applies. Exempt status may be established by any
sufficient evidence, including an affidavit containing the following:
(1) The affiant's name and address;
(2) Identification of the affiant;
(3) Identification of the endangered or threatened wildlife which is the subject of the affidavit;
(4) A statement by the affiant that to the best of his knowledge and belief, the endangered or threatened wildlife
which is the subject of the affidavit was in captivity or in a controlled environment on December 28, 1973, and was
not being held for purposes contrary to the Act or in the course of a commercial activity;
(5) A statement by the affiant in the following language:
The foregoing is principally based on the attached exhibits which, to the best of my knowledge and belief, are
complete, true and correct. I understand that this affidavit is being submitted for the purpose of inducing the
Federal Government to recognize an exempt status regarding (insert description of wildlife), under the Endangered
Species Act of 1973 (16 U.S.C. 1531-1543), and regulations promulgated thereunder, and that any false
statements may subject me to the criminal penalties of 18 U.S.C. 1001.
(6) As an attachment, records or other available evidence to show:
(i) That the wildlife in question was being held in captivity or in a controlled environment on December 28, 1973;
(ii) The purpose for which the wildlife was being held; and
(iii) The nature of such holding (to establish that no commercial activity was involved).
(c) This section applies only to wildlife born on or prior to December 28, 1973. It does not apply to the progeny of
any such wildlife born after December 28, 1973.
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§17.5 Alaska natives.
(a) The provisions of subpart C of this part relating to the importation or the taking of endangered wildlife, and any
provision of subpart D of this part relating to the importation or the taking of threatened wildlife, shall not apply to:
(1) Any Indian, Aleut, or Eskimo who is an Alaskan native and who resides in Alaska; or
(2) Any non-native permanent resident of an Alaskan native village who is primarily dependent upon the taking of
wildlife for consumption or for the creation and sale of authentic native articles of handicrafts and clothing:
If the taking is primarily for subsistence purposes, and is not accomplished in a wasteful manner.
(b) Edible portions of endangered or threatened wildlife taken or imported pursuant to paragraph (a) of this section
may be sold in native villages or towns in Alaska for native consumption within native villages and towns in Alaska.
(c) Non-edible by-products of endangered or threatened wildlife taken or imported pursuant to paragraph (a) of this
section may be sold in interstate commerce when made into authentic native articles of handicrafts and clothing.
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§17.6 State cooperative agreements. [Reserved]
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§17.7 Raptor exemption.
(a) The prohibitions found in §§17.21 and 17.31 do not apply to any raptor [a live migratory bird of the
Order Falconiformes or the Order Strigiformes, other than a bald eagle (Haliaeetus leucocephalus) or a golden
eagle (Aquila chrysaetos)] legally held in captivity or in a controlled environment on November 10, 1978, or to any
of its progeny, which is:
(1) Possessed and banded in compliance with the terms of a valid permit issued under part 21 of this chapter; and
(2) Identified in the earliest applicable annual report required to be filed by a permittee under part 21 of this chapter
as in a permittee's possession on November 10, 1978, or as the progeny of such a raptor.
(b) This section does not apply to any raptor intentionally returned to the wild.
[48 FR 31607, July 8, 1983]
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§17.8 Import exemption for threatened, CITES
Appendix-II wildlife.
(a) Except as provided in a special rule in §§17.40 through 17.48 or in paragraph (b) of this section, all provisions
of §§17.31 and 17.32 apply to any specimen of a threatened species of wildlife that is listed in Appendix II of the
Convention.
(b) Import. Except as provided in a special rule in §§17.40 through 17.48, any live or dead specimen of a fish and
wildlife species listed as threatened under this part may be imported without a threatened species permit under
§17.32 provided all of the following conditions are met:
(1) The specimen was not acquired in foreign commerce or imported in the course of a commercial activity;
(2) The species is listed in Appendix II of the Convention.
(3) The specimen is imported and subsequently used in accordance with the requirements of part 23 of this
subchapter, except as provided in paragraph (b)(4) of this section.
(4) Personal and household effects (see §23.5) must be accompanied by a CITES document.
(5) At the time of import, the importer must provide to the FWS documentation that shows the specimen was not
acquired in foreign commerce in the course of a commercial activity.
(6) All applicable requirements of part 14 of this subchapter are satisfied.
[72 FR 48446, Aug. 23, 2007]
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§17.9 Permit applications and information
collection requirements.
(a) Address permit applications for activities affecting species listed under the Endangered Species Act, as
amended, as follows:
(1) Address activities affecting endangered and threatened species that are native to the United States to the
Regional Director for the Region in which the activity is to take place. You can find addresses for the Regional
Directors in 50 CFR 2.2. Send applications for interstate commerce in native endangered and threatened species
to the Regional Director with lead responsibility for the species. To determine the appropriate region, call the
nearest Regional Office:
Region 1 (Portland, OR): 503-231-6241
Region 2 (Albuquerque, NM): 505-248-6920
Region 3 (Twin Cities, MN): 612-713-5343
Region 4 (Atlanta, GA): 404-679-7313
Region 5 (Hadley, MA): 413-253-8628
Region 6 (Denver, CO): 303-236-8155, ext 263
Region 7 (Anchorage, AK): 907-786-3620
Headquarters (Washington, DC): 703-358-2106
(2) Submit permit applications for activities affecting native endangered and threatened species in international
movement or commerce, and all activities affecting nonnative endangered and threatened species, to the attention
of the Director, U.S. Fish and Wildlife Service, at the address listed for the Division of Management Authority at 50
CFR 2.1(b).
(b) The Office of Management and Budget approved the information collection requirements contained in this part
17 under 44 U.S.C. 3507 and assigned OMB Control Numbers 1018-0093 and 1018-0094. The Service may not
conduct or sponsor, and you are not required to respond to, a collection of information unless it displays a currently
valid OMB control number. We are collecting this information to provide information necessary to evaluate permit
applications. We will use this information to review permit applications and make decisions, according to criteria
established in various Federal wildlife conservation statutes and regulations, on the issuance, suspension,
revocation, or denial of permits. You must respond to obtain or retain a permit. We estimate the public reporting
burden for these reporting requirements to vary from 2 to 21⁄2 hours per response, including time for reviewing
instructions, gathering and maintaining data, and completing and reviewing the forms. Direct comments regarding
the burden estimate or any other aspect of these reporting requirements to the Service's Information Collection
Clearance Officer at the address provided at 50 CFR 2.1(b).
[63 FR 52635, Oct. 1, 1998. Redesignated at 72 FR 48446, Aug. 23, 2007, as amended at 79 FR 30417, May 27,
2014; 79 FR 43964, July 29, 2014]
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Subpart B—Lists
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§17.11 Endangered and threatened wildlife.
(a) The list in paragraph (h) of this section contains the wildlife species determined by the Service or the National
Marine Fisheries Service (NMFS) of the Department of Commerce's National Oceanic and Atmospheric
Administration (hereafter in this section referred to as “the Services”) to be endangered species or threatened
species. It also contains the wildlife species treated as endangered species or threatened species because they
are similar in appearance to and may be confused with endangered or threatened species (see §§17.50 through
17.52). The “Common name,” “Scientific name,” “Where listed,” and “Status” columns provide regulatory
information; together, they identify listed wildlife species within the meaning of the Act and describe where they are
protected. When a taxon has more than one entry, the “Where listed” or “Status” column will identify its status in
each relevant geographic area. The listing of a particular taxon includes all lower taxonomic units.
(b) “Common name” column. Although common names are included, they cannot be relied upon for identification
of any specimen, since they may vary greatly in local usage. In cases where confusion might arise, one or more
synonyms are provided in parentheses within the “Common name” column. If a species has been listed as an
Evolutionarily Significant Unit (ESU) or a Distinct Vertebrate Population Segment (DPS), the ESU or DPS names
will be provided in brackets “[ ]” following the common name.
(c) “Scientific name” column. The Services use the most recently accepted scientific name. In cases where
confusion might arise, one or more synonyms are provided in parentheses within the “Scientific name” column.
The Services rely, to the extent practicable, on the Integrated Taxonomic Information System (ITIS) to determine a
species' scientific name. ITIS incorporates the naming principles established by the International Code of
Zoological Nomenclature (see paragraph (g) of this section). If the scientific name in ITIS differs from the scientific
name adopted for use under the Convention on International Trade in Endangered Species of Wild Fauna and
Flora (CITES), the CITES nomenclature is provided in brackets “[ ]” within the “Scientific name” column following
the ITIS nomenclature.
(d) “Where listed” column. The “Where listed” column sets forth the geographic area where the species is listed for
purposes of the Act. Except when providing a geographic description of a DPS or ESU, or an experimental
population designation, “Wherever found” will be used to indicate the Act's protections apply to all individuals of
the species, wherever found.
(e) “Status” column. Within the “Status” column, the following abbreviations are used:
Abbreviation
E
T
E (S/A)
T (S/A)
XE
XN
Regulatory status the
abbreviation represents
Endangered species.
Threatened species.
Endangered based on similarity of appearance to an existing listed species.
Threatened based on similarity of appearance to an existing listed species.
Essential experimental population (See subpart H of this part).
Nonessential experimental population (See subpart H of this part).
(f) “Listing Citations and Applicable Rules” column. The “Listing Citations and Applicable Rules” column is
nonregulatory in nature and is provided for informational and navigational purposes only.
(1) Within the “Listing Citations and Applicable Rules” column, the following superscripts are used:
SuperscriptDescription of citation or rule
N
NMFS listing citation (NMFS Lead).
J
Both FWS and NMFS listing citation (Joint Jurisdiction).
CH
Critical habitat rule.
4d
Species-specific “4(d)” rule (a rule issued under the authority of section 4(d) of the Act).
Species-specific “10(j)” rule (a rule issued under the authority of section 10(j) of the
10j
Act).
(2) Listing citations contain the volume, document starting page number, and publication date of the Federal
Register publication(s) in which a species was given status, listed, or reclassified. At least since 1973, these
documents have included a statement indicating the basis for the listing, as well as the effective date(s) of the
listing or other rules that changed how the species was identified in the List in paragraph (h) of this section.
(3) “Critical habitat” and “Species-specific” rules superscripts provide cross-references to other sections in this part
or part 222, 223, or 226 of chapter II of this title where critical habitat and species-specific rules are found. The
species-specific superscripts also identify experimental populations. Experimental populations (superscript “10j”)
are a separate citation, with one of the following symbols in the “Status” column: “XE” for an essential experimental
population and “XN” for a nonessential experimental population.
(4) This column is for reference and navigational purposes only. All other appropriate rules in this part, parts 217
through 226 of chapter II of this title, and part 402 of chapter IV of this title apply, if no species-specific rules are
referenced. In addition, other rules in this title could relate to such species (for example, port-of-entry
requirements). The references in the “Listing Citations and Applicable Rules” column do not comprise a
comprehensive list of all regulations that the Services might apply to the species or to the regulations of other
Federal agencies or State or local governments.
(g) The Services will rely to the extent practicable on ITIS (http://www.itis.gov) and standard references adopted for
CITES (http://cites.org).
(h) The “List of Endangered and Threatened Wildlife” is provided in the table in this paragraph (h):
Common name Scientific name
Where listed
Listing citations
Status and applicable
rules
Mammals
Addax
Addax nasomaculatus
Wherever found
E
70 FR 52319,
9/2/2005.
Anoa, lowland
Bubalus depressicornis
Wherever found
E
Anoa, mountain
Bubalus quarlesi
Wherever found
E
Antelope, giant
sable
Hippotragus niger variani
Wherever found
E
Antelope, Tibetan Panthalops hodgsonii
Wherever found
E
Argali [All
populations
except
Kyrgyzstan,
Mongolia, and
Tajikistan]
Wherever found except
Kyrgyzstan, Mongolia, E
and Tajikistan
Ovis ammon
Argali
[Kyrgyzstan,
Mongolia, and
Tajikistan]
Ovis ammon
Kyrgyzstan, Mongolia,
T
and Tajikistan
Armadillo, giant
Priodontes maximus
Wherever found
E
Armadillo, pink
fairy
Chlamyphorus truncatus
Wherever found
E
Ass, African wild Equus africanus
Wherever found
E
Ass, Asian wild
Equus hemionus
Wherever found
E
Avahi
Avahi laniger(=entire genus)
Wherever found
E
Aye-aye
Daubentonia madagascariensis Wherever found
E
Babirusa
Babyrousa babyrussa
Wherever found
E
Baboon, gelada
Theropithecus gelada
Wherever found
T
Bandicoot, barred Perameles bougainville
Wherever found
E
Bandicoot, desert Perameles eremiana
Wherever found
E
Wherever found
E
Wherever found
E
Bandicoot, rabbit Macrotis lagotis
Wherever found
E
Banteng
Wherever found
E
Wherever found
E
Bandicoot, lesser
Macrotis leucura
rabbit
Bandicoot, pigChaeropus ecaudatus
footed
Bos javanicus
Bat, Bulmer's fruit
Aproteles bulmerae
(flying fox)
35 FR 8491,
6/2/1970.
41 FR 24061,
6/14/1976.
41 FR 24061,
6/14/1976.
71 FR 15620,
3/29/2006.
41 FR 24061,
6/14/1976;
57 FR 28014,
6/23/1992.
41 FR 24061,
6/14/1976;
57 FR 28014,
6/23/1992;
50 CFR 17.40(j).4d
41 FR 24061,
6/14/1976.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970;
42 FR 15971,
3/24/1977.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
41 FR 24061,
6/14/1976.
41 FR 45990,
10/19/1976;
50 CFR
17.40(c).4d
35 FR 18319,
12/2/1970.
38 FR 14678,
6/4/1973.
35 FR 18319,
12/2/1970.
35 FR 18319,
12/2/1970.
35 FR 18319,
12/2/1970.
35 FR 8491,
6/2/1970.
49 FR 2779,
1/23/1984.
49 FR 2779,
1/23/1984.
78 FR 61003,
10/2/2013.
41 FR 17736,
4/28/1976.
35 FR 16047,
10/13/1970.
32 FR 4001,
3/11/1967;
50 CFR
17.95(a).CH
49 FR 33881,
8/27/1984.
49 FR 33881,
8/27/1984;
70 FR 1190,
1/6/2005;
50 CFR
17.95(a).CH
53 FR 38456,
9/30/1988.
80 FR 17973,
4/2/2015;
50 CFR
17.40(o).4d
44 FR 69206,
11/30/1979.
Bat, bumblebee
Craseonycteris thonglongyai
Wherever found
E
Bat, Florida
bonneted
Eumops floridanus
Wherever found
E
Bat, gray
Myotis grisescens
Wherever found
E
Bat, Hawaiian
hoary
Lasiurus cinereus semotus
Wherever found
E
Bat, Indiana
Myotis sodalis
Wherever found
E
Wherever found
E
Fruit Bat, Mariana
(=fanihi, Mariana Pteropus mariannus mariannus Wherever found
flying fox)
T
Bat, Mexican
long-nosed
Leptonycteris nivalis
Wherever found
E
Bat, northern
long-eared
Myotis septentrionalis
Wherever found
T
Wherever found
E
Wherever found
E
80 FR 59423,
10/1/2015.
Wherever found
E
81 FR 65466,
9/22/2016.
Wherever found
E
49 FR 2779,
1/23/1984.
Wherever found
E
49 FR 2779,
1/23/1984.
Bat, little Mariana
Pteropus tokudae
fruit
Bat, Ozark big- Corynorhinus (=Plecotus)
eared
townsendii ingens
Bat, Pacific
sheath-tailed
(Mariana
Emballonura semicaudata
subspecies)
rotensis
(Payeyi,
Paischeey)
Bat, Pacific
sheath-tailed
(South Pacific
subspecies) (=
Emballonura semicaudata
peapea vai,
semicaudata
American Samoa;
= tagiti, Samoa; =
beka beka, Fiji)
Bat, Rodrigues
Pteropus rodricensis
fruit (flying fox)
Bat, Singapore
roundleaf
Hipposideros ridleyi
horseshoe
Bat, Virginia big- Corynorhinus (=Plecotus)
eared
townsendii virginianus
Wherever found
E
Bear, Baluchistan Ursus thibetanus gedrosianus
Wherever found
E
44 FR 69206,
11/30/1979;
50 CFR
17.95(a).CH
51 FR 17977,
5/16/1986.
Bear, brown
[Italy]
Ursus arctos arctos
Italy
E
Bear, brown
Ursus arctos pruinosus
Wherever found
E
Bear, grizzly
Ursus arctos horribilis
U.S.A., conterminous
(lower 48) States,
except where listed as T
an experimental
population
Bear, grizzly
Ursus arctos horribilis
U.S.A., (portions of ID
XN
and MT, see §17.84(l)).
Bear, Mexican
grizzly
Ursus arctos
Mexico
E
Bear, polar
Ursus maritimus
Wherever found
T
Beaver
(Mongolia)
Castor fiber birulai
Wherever found
E
Bison, wood
Bison bison athabascae
Wherever found,
except where listed as
T
an experimental
population
Bison, wood
Bison bison athabascae
U.S.A. (Alaska)
XN
Bobcat, Mexican Lynx (=Felis) rufus escuinapae Wherever found
E
Bontebok
(antelope)
Wherever found
E
Wherever found
E
Damaliscus pygarus (=dorcas)
dorcas
Camel, Bactrian Camelus bactrianus
41 FR 24062,
6/14/1976;
41 FR 26019,
6/24/1976.
41 FR 24062,
6/14/1976.
32 FR 4001,
3/11/1967; 35 FR
16047,
10/13/1970; 40
FR 31734,
7/28/1975; 72 FR
14866, 3/29/2007;
75 FR 14496,
3/26/2010; 82 FR
30502, 6/30/2017;
84 FR 37144,
7/31/2019; 50
CFR 17.40(b).4d
70 FR 69854;
11/17/2005, 50
CFR 17.84(l)10j.
35 FR 8491,
6/2/1970.
73 FR 28212,
5/15/2008;
50 CFR
17.40(q);4d
50 CFR
17.95(a).CH
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970;
77 FR 26191,
5/3/2012.
79 FR 26175,
5/7/2014;
50 CFR
17.84(x).10j
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
Caribou,
woodland
[Southern
Mountain DPS]
Rangifer tarandus caribou
U.S.A. (wherever
found), Canada
(southeastern British
Columbia)
E
Cat, Andean
Felis jacobita
Wherever found
E
Cat, Asian golden
Catopuma (=Felis) temminckii
(=Temminck's)
Wherever found
E
Cat, black-footed Felis nigripes
Wherever found
E
Cat, flat-headed Prionailurus (=Felis) planiceps
Wherever found
E
Wherever found
E
Wherever found
E
Cat, Iriomote
Cat, leopard
Prionailurus (=Felis)
bengalensis iriomotensis
Prionailurus (=Felis)
bengalensis bengalensis
Cat, marbled
Pardofelis (=Felis) marmorata
Wherever found
E
Cat, Pakistan
sand
Felis margarita scheffeli
Wherever found
E
Cat, tiger
Leopardus (=Felis) tigrinus
Wherever found
E
Chamois,
Apennine
Rupicapra rupicapra ornata
Wherever found
E
Cheetah
Acinonyx jubatus
Wherever found
E
Chimpanzee
Pan troglodytes
Wherever found
E
Chimpanzee,
pygmy
Pan paniscus
Wherever found
E
Chinchilla
Chinchilla brevicaudata
boliviana
Wherever found
E
Civet, Malabar
large-spotted
Viverra civettina (=megaspila c.) Wherever found
E
Deer, Bactrian
Cervus elaphus bactrianus
Wherever found
E
Deer, Barbary
Cervus elaphus barbarus
Wherever found
E
Wherever found
E
Deer, Calamianes
Axis porcinus calamianensis
(=Philippine)
48 FR 1722,
1/14/1983; 48 FR
49245,
10/25/1983; 49
FR 7390,
2/29/1984; 83 FR
52598, Oct. 2,
2019; 50 CFR
17.95(a).CH
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
44 FR 37124,
6/25/1979.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
49 FR 2779,
1/23/1984.
37 FR 6476,
3/30/1972.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970;
37 FR 6476,
3/30/1972.
41 FR 45990,
10/19/1976;
55 FR 9129,
3/12/1990;
80 FR 34500,
6/16/2015.
41 FR 45990,
10/19/1976;
55 FR 9129,
3/12/1990.
41 FR 24062,
6/14/1976.
44 FR 37124,
6/25/1979.
44 FR 37124,
6/25/1979.
44 FR 37124,
6/25/1979.
41 FR 24062,
6/14/1976.
Deer, Cedros
Island mule
Odocoileus hemionus
cedrosensis
Wherever found
E
Columbia River (Clark,
Cowlitz, Pacific,
Deer, Columbian
Skamania, and
white-tailed
Wahkiakum Counties,
Odocoileus virginianus leucurus
T
[Columbia River
WA, and Clatsop,
DPS]
Columbia, and
Multnomah Counties,
OR)
Deer, Corsican
Cervus elaphus corsicanus
Wherever found
E
red
Deer, Eld's browCervus eldi
Wherever found
E
antlered
Deer, Formosan
Cervus nippon taiouanus
Wherever found
E
sika
Deer, Indochina Axis (=Cervus) porcinus
Wherever found
E
hog
annamiticus
Deer, key
Odocoileus virginianus clavium Wherever found
E
Deer, Kuhl's
(=Bawean)
Axis porcinus kuhli
Wherever found
E
Deer, marsh
Blastocerus dichotomus
Wherever found
E
Deer, McNeill's
Cervus elaphus macneilii
Wherever found
E
Deer, musk
Moschus spp. (all species)
Afghanistan, Bhutan,
Burma, China (Tibet,
E
Yunnan), India, Nepal,
Pakistan, Sikkim
Deer, North
China sika
Cervus nippon mandarinus
Wherever found
E
Deer, pampas
Ozotoceros bezoarticus
Wherever found
E
Deer, Persian
fallow
Deer, Ryukyu
sika
Dama mesopotamica (=dama
m.)
Wherever found
E
Cervus nippon keramae
Wherever found
E
Deer, Shansi sika Cervus nippon grassianus
Wherever found
E
Deer, South
China sika
Cervus nippon kopschi
Wherever found
E
Deer, swamp
Cervus duvauceli
Wherever found
E
Deer, Visayan
Cervus alfredi
Wherever found
E
Deer, Yarkand
Cervus elaphus yarkandensis
Wherever found
E
Dhole
Cuon alpinus
Wherever found
E
Dibbler
Antechinus apicalis
Wherever found
E
40 FR 44149,
9/25/1975.
32 FR 4001,
3/11/1967;
68 FR 43647,
7/24/2003;
81 FR 71386,
10/17/2016;
50 CFR 17.40(i).4d
44 FR 37124,
6/25/1979.
35 FR 8491,
6/2/1970.
44 FR 37124,
6/25/1979.
41 FR 24062,
6/14/1976.
32 FR 4001,
3/11/1967.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
44 FR 37124,
6/25/1979.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
44 FR 37124,
6/25/1979.
44 FR 37124,
6/25/1979.
44 FR 37124,
6/25/1979.
35 FR 8491,
6/2/1970.
53 FR 33990,
9/1/1988.
44 FR 37124,
6/25/1979.
35 FR 8491,
6/2/1970.
35 FR 18319,
12/2/1970.
Dog, African wild Lycaon pictus
Wherever found
E
Dolphin, Chinese
Lipotes vexillifer
river
Wherever found
E
Dolphin, Hector's Cephalorhynchus hectori hectori Wherever found
T
Dolphin, Maui
Cephalorhynchus hectori maui
Wherever found
E
Platanista gangetica minor
Wherever found
E
Sousa chinensis taiwanensis
Wherever found
E
Drill
Mandrillus (=Papio)
leucophaeus
Wherever found
E
Dugong
Dugong dugon
Wherever found
E
Duiker, Jentink's Cephalophus jentinki
Wherever found
E
Eland, western
giant
Wherever found
E
Elephant, African Loxodonta africana
Wherever found
T
Elephant, Asian
Wherever found
E
Dolphin, South
Asian River
(Indus River
subspecies)
Dolphin,
Taiwanese
humpback
Taurotragus derbianus
derbianus
Elephas maximus
49 FR 2779,
1/23/1984.
54 FR 22906,
5/30/1989;N
54 FR 22905,
5/30/1989.
82 FR 43701,
9/19/2017;N 84
FR 13809,
4/8/2019.
82 FR 43701,
9/19/2017;N 84
FR 13809,
4/8/2019.
55 FR 50835,
12/11/1990;N
56 FR 1463,
1/14/1991.
83 FR 21182,
5/9/2018;N 84 FR
13809, 4/8/2019.
41 FR 45990,
10/19/1976.
35 FR 18319,
12/2/1970;
68 FR 70185,
12/17/2003.
44 FR 37124,
6/25/1979.
44 FR 37124,
6/25/1979.
43 FR 20499,
5/12/1978;
50 CFR
17.40(e).4d
41 FR 24062,
6/14/1976.
Ferret, blackfooted
Ferret, blackfooted
Mustela nigripes
Wherever found,
except where listed as
E
an experimental
population
Mustela nigripes
U.S.A. (WY and
specified portions of
XN
AZ, CO, MT, SD, and
UT, see §17.84(g)(9))
Fox, northern
Vulpes velox hebes
swift
Fox, San Joaquin
Vulpes macrotis mutica
kit
Canada
E
Wherever found
E
Fox, Santa
Catalina Island
Urocyon littoralis catalinae
Wherever found
T
Fox, Simien
Canis simensis
Wherever found
E
Gazelle, Arabian Gazella gazella
Wherever found
E
Gazelle, Clark's
Wherever found
E
Ammodorcas clarkei
32 FR 4001,
3/11/1967;
35 FR 8491,
6/2/1970;
56 FR 41473,
9/21/1979;
59 FR 42682,
8/18/1994;
59 FR 42696,
8/18/1994;
61 FR 11320,
3/20/1996;
63 FR 52824,
10/1/1998;
65 FR 60879,
10/13/2000;
68 FR 26498,
5/16/2003;
80 FR 66821,
10/30/2015.
56 FR 41473,
8/21/1991;
59 FR 42682,
8/18/1994;
59 FR 42696,
8/18/1994;
61 FR 11320,
3/20/1996;
63 FR 52824,
10/1/1998;
65 FR 60879,
10/13/2000;
68 FR 26498,
5/16/2003;
80 FR 66821,
10/30/2015;
50 CFR
17.84(g).10j
35 FR 8491,
6/2/1970.
32 FR 4001,
3/11/1967.
69 FR 10335,
3/5/2004;
81 FR 53515,
8/12/2016;
50 CFR
17.95(a).CH
44 FR 37124,
6/25/1979.
44 FR 37124,
6/25/1979.
35 FR 8491,
6/2/1970.
Gazelle, dama
Gazella dama
Wherever found
E
Gazella dorcas massaesyla
Wherever found
E
Gazella cuvieri
Wherever found
E
Gazelle, Pelzeln's Gazella dorcas pelzelni
Wherever found
E
Gazelle, sand
Wherever found
E
Wherever found
E
Wherever found
E
Gazelle,
Moroccan
Gazelle,
mountain
(=Cuvier's)
Gazella subgutturosa marica
Gazelle, Saudi
Gazella dorcas saudiya
Arabian
Gazelle, slenderGazella leptoceros
horned
Gibbons
Hylobates spp.
(including Nomascus )
Wherever found
E
Goral
Nemorhaedus goral
Wherever found
E
Gorilla
Gorilla gorilla
Wherever found
E
Hare, hispid
Caprolagus hispidus
Wherever found
E
Hartebeest,
Swayne's
Alcelaphus buselaphus swaynei Wherever found
E
Hartebeest, Tora Alcelaphus buselaphus tora
Wherever found
E
Hog, pygmy
Sus salvanius
Wherever found
E
Equus przewalskii
Wherever found
E
Hippocamelus antisensis
Wherever found
E
Hippocamelus bisulcus
Wherever found
E
Hutia, Cabrera's Capromys angelcabrerai
Wherever found
E
Hutia, dwarf
Capromys nana
Wherever found
E
Hutia, largeeared
Capromys auritus
Wherever found
E
Hutia, little earth Capromys sanfelipensis
Wherever found
E
Hyena, Barbary
Hyaena hyaena barbara
Wherever found
E
Hyena, brown
Parahyaena (=Hyaena) brunnea Wherever found
E
Horse,
Przewalski's
Huemul, north
Andean
Huemul, south
Andean
70 FR 52319,
9/2/2005;
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
44 FR 37124,
6/25/1979.
44 FR 37124,
6/25/1979.
44 FR 37124,
6/25/1979.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970;
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970;
41 FR 24062;
6/14/1976.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
51 FR 17977,
5/16/1986.
51 FR 17977,
5/16/1986.
51 FR 17977,
5/16/1986.
51 FR 17977,
5/16/1986.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
Ibex, Pyrenean
Capra pyrenaica pyrenaica
Wherever found
E
Ibex, Walia
Capra walie
Wherever found
E
Impala, blackfaced
Aepyceros melampus petersi
Wherever found
E
Indri
Indri indri (=entire genus)
Wherever found
E
Jaguar
Panthera onca
Wherever found
E
Jaguarundi,
Guatemalan
Jaguarundi, Gulf
Coast
Jaguarundi,
Panamanian
Jaguarundi,
Sinaloan
Herpailurus (=Felis)
yagouaroundi fossata
Herpailurus (=Felis)
yagouaroundi cacomitli
Herpailurus (=Felis)
yagouaroundi panamensis
Herpailurus (=Felis)
yagouaroundi tolteca
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Kangaroo rat,
Fresno
Dipodomys nitratoides exilis
Wherever found
E
Kangaroo rat,
giant
Dipodomys ingens
Wherever found
E
Kangaroo rat,
Morro Bay
Dipodomys heermanni
morroensis
Wherever found
E
Kangaroo rat,
San Bernardino
Merriam's
Dipodomys merriami parvus
Wherever found
E
Wherever found
E
Wherever found
E
Kangaroo rat,
Stephens'
Kangaroo rat,
Tipton
Kangaroo,
Tasmanian
forester
Dipodomys stephensi (incl. D.
cascus)
Dipodomys nitratoides
nitratoides
Macropus giganteus
tasmaniensis
Wherever found
E
Koala
Phascolarctos cinereus
Australia
T
Kouprey
Bos sauveli
Wherever found
E
Langur, capped
Trachypithecus (=Presbytis)
pileatus
Wherever found
E
Langur, Douc
Pygathrix nemaeus
Wherever found
E
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
37 FR 6476,
3/30/1972;
62 FR 39147,
7/22/1997;
50 CFR
17.95(a).CH
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
50 FR 4222,
1/30/1985;
50 CFR
17.95(a).CH
52 FR 283,
1/5/1987.
35 FR 16047,
10/13/1970;
50 CFR
17.95(a).CH
63 FR 3835,
1/27/1988;
63 FR 51005,
9/24/1988;
50 CFR
17.95(a).CH
53 FR 38465,
9/30/1988.
53 FR 25608,
7/8/1988.
38 FR 14678,
6/4/1973.
65 FR 26762,
5/9/2000.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
Langur, Francois'
Langur, golden
Langur, gray
(=entellus)
Trachypithecus (=Presbytis)
francoisi
Trachypithecus (=Presbytis)
geei
Semnopithecus (=Presbytis)
entellus
Wherever found
E
Wherever found
E
Wherever found
E
Langur, longtailed
Presbytis potenziani
Wherever found
T
Langur, Pagi
Island
Nasalis concolor
Wherever found
E
Langur, purplefaced
Presbytis senex
Wherever found
T
Lechwe, red
Kobus leche
Wherever found
T
Lemurs
Lemuridae (incl. genera Lemur,
Phaner, Hapalemur, Lepilemur,
Wherever found
Microcebus, Allocebus,
Cheirogaleus, Varecia )
E
Leopard
Panthera pardus
Wherever found,
except where it is listed E
as threatened
Leopard
[Southern Africa Panthera pardus
populations]
In Africa, in the wild,
south of, and including,
the following countries: T
Gabon, Congo, Zaire,
Uganda, Kenya
Leopard, clouded Neofelis nebulosa
Wherever found
E
Leopard, snow
Wherever found
E
Linsang, spotted Prionodon pardicolor
Wherever found
E
Lion
Wherever found
E
Uncia (=Panthera) uncia
Panthera leo leo
41 FR 45990,
10/19/1976.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
41 FR 45990,
10/19/1976;
50 CFR
17.40(c).4d
35 FR 8491,
6/2/1970.
41 FR 45990,
10/19/1976;
50 CFR
17.40(c).4d
35 FR 8491,
6/2/1970;
41 FR 24062,
6/14/1976;
45 FR 65132,
10/1/1980.
35 FR 8491,
6/2/1970;
41 FR 24062,
6/14/1976;
41 FR 26019,
6/24/1976.
35 FR 8491,
6/2/1970;
37 FR 6476,
3/30/1972;
47 FR 4204,
1/28/1982.
35 FR 8491,
6/2/1970;
37 FR 6476,
3/30/1972;
47 FR 4204,
1/28/1982;
50 CFR
17.40(f).4d
35 FR 8491,
6/2/1970;
41 FR 24062,
6/14/1976.
37 FR 6476,
3/30/1972.
41 FR 24062,
6/14/1976.
80 FR 79999,
12/23/2015.
Lion
Wherever found
T
Loris, lesser slow Nycticebus pygmaeus
Wherever found
T
Lynx, Canada
[Contiguous U.S. Lynx canadensis
DPS]
Where found within
contiguous U.S.A.
T
Lynx, Spanish
Felis pardina
Wherever found
E
Macaque,
Formosan rock
Macaca cyclopis
Wherever found
T
Macaque,
Japanese
Macaca fuscata
Wherever found
T
Macaque, liontailed
Macaca silenus
Wherever found
E
Macaque, stumpMacaca arctoides
tailed
Wherever found
T
Macaque, Toque Macaca sinica
Wherever found
T
Trichechus inunguis
Wherever found
E
Trichechus senegalensis
Wherever found
T
Manatee, West
Indian
Trichechus manatus
Wherever found
T
Mandrill
Mandrillus (=Papio) sphinx
Wherever found
E
Wherever found
E
Manatee,
Amazonian
Manatee, West
African
Panthera leo melanochaita
Mangabey, Tana
Cercocebus galeritus galeritus
River
80 FR 79999,
12/23/2015;
50 CFR
17.40(r).4d
41 FR 45990,
10/19/1976;
50 CFR
17.40(c).4d
65 FR 16053,
3/24/2000;
50 CFR
17.40(k);4d
50 CFR
17.95(a).CH
35 FR 8491,
6/2/1970.
41 FR 45990,
10/19/1976;
50 CFR
17.40(c).4d
41 FR 45990,
10/19/1976;
50 CFR
17.40(c).4d
35 FR 8491,
6/2/1970.
41 FR 45990,
10/19/1976;
50 CFR
17.40(c).4d
41 FR 45990,
10/19/1976;
50 CFR
17.40(c).4d
35 FR 8491,
6/2/1970.
44 FR 42910,
7/20/1979.
32 FR 4001,
3/11/1967;
35 FR 8491,
6/2/1970;
82 FR 16668,
4/5/2017;
50 CFR
17.108(a);
50 CFR
17.95(a).CH
41 FR 45990,
10/19/1976.
35 FR 8491,
6/2/1970.
Mangabey, whiteCercocebus torquatus
collared
Wherever found
E
Margay
Leopardus (=Felis) wiedii
Mexico southward
E
Markhor, chiltan
(=wild goat)
Capra falconeri (=aegagrus)
chiltanensis
Wherever found
E
Wherever found
T
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Markhor, straightCapra falconeri megaceros
horned
Marmoset, buffCallithrix flaviceps
headed
Marmoset,
Saguinus oedipus
cotton-top
Marmoset,
Callimico goeldii
Goeldi's
Marmoset, whiteeared (=buffy
Callithrix aurita (=jacchus a.)
tufted-ear)
Marmot,
Marmota vancouverensis
Vancouver Island
Marsupial,
Antechinomys laniger
eastern jerboa
Marsupial-mouse,
Sminthopsis psammophila
large desert
Marsupial-mouse,
Sminthopsis longicaudata
long-tailed
Marten,
Formosan yellow- Martes flavigula chrysospila
throated
Monkey, black
Colobus satanas
colobus
Monkey, black
howler
Alouatta pigra
Wherever found
T
Monkey, Diana
Cercopithecus diana
Wherever found
E
Monkey, Guizhou
Rhinopithecus brelichi
snub-nosed
Wherever found
E
Monkey, L'hoest's Cercopithecus lhoesti
Wherever found
E
Wherever found
E
Procolobus (=Colobus) preussi
Wherever found
(=badius p.)
E
Nasalis larvatus
Wherever found
E
Saimiri oerstedii
Wherever found
E
Monkey, mantled
howler
Monkey, Preuss'
red colobus
Monkey,
proboscis
Monkey, redbacked squirrel
Alouatta palliata
41 FR 45990,
10/19/1976.
37 FR 6476,
3/30/1972.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976;
79 FR
60365,10/7/2014;
50 CFR
17.40(d).4d
49 FR 2779,
1/23/1984.
41 FR 45990,
10/19/1976.
35 FR 8491,
6/2/1970.
51 FR 17977,
5/16/1986.
49 FR 2779,
1/23/1984.
35 FR 18319,
6/2/1970.
35 FR 18319,
6/2/1970.
35 FR 18319,
6/2/1970.
35 FR 8491,
6/2/1970.
41 FR 45990,
10/19/1976.
41 FR 45990,
10/19/1976;
50 CFR
17.40(c).4d
41 FR 45990,
10/19/1976.
55 FR 39414,
9/27/1990.
41 FR 45990,
10/19/1976.
41 FR 24062,
6/14/1976.
49 FR 2779,
1/23/1984.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
Monkey, redCercopithecus erythrogaster
bellied
Monkey, redeared noseCercopithecus erythrotis
spotted
Monkey, Sichuan
Rhinopithecus roxellana
snub-nosed
Wherever found
E
41 FR 45990,
10/19/1976.
Wherever found
E
41 FR 45990,
10/19/1976.
Wherever found
E
Monkey, spider
Ateles geoffroyi frontatus
Wherever found
E
Monkey, spider
Ateles geoffroyl panamensis
Wherever found
E
Monkey, Tana
Procolobus (=Colobus)
River red colobus rufomitratus (=badius r.)
Wherever found
E
Monkey, Tonkin
snub-nosed
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Rhinopithecus avunculus
Monkey, woolly
Brachyteles arachnoides
spider
Monkey, yellowLagothrix flavicauda
tailed woolly
Monkey, Yunnan
Rhinopithecus bieti
snub-nosed
Monkey, Zanzibar Procolobus (=Colobus)
red colobus
pennantii (=kirki) kirki
Mountain beaver,
Aplodontia rufa nigra
Point Arena
Mouse, Alabama Peromyscus polionotus
beach
ammobates
Mouse, Anastasia
Peromyscus polionotus phasma Wherever found
Island beach
Mouse,
Notomys aquilo
Wherever found
Australian native
Mouse,
Zyzomys pedunculatus
Wherever found
Australian native
E
E
E
Mouse,
Peromyscus polionotus
Choctawhatchee
allophrys
beach
Wherever found
E
Mouse, Field's
Pseudomys fieldi
Wherever found
E
Mouse, Gould's
Pseudomys gouldii
Wherever found
E
Mouse, Key
Largo cotton
Peromyscus gossypinus
allapaticola
Wherever found
E
Mouse, New
Holland
Pseudomys novaehollandiae
Wherever found
E
55 FR 39414,
9/27/1990.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
41 FR 45990,
10/19/1976;
55 FR 39414,
9/27/1990.
35 FR 8491,
6/2/1970.
41 FR 45990,
10/19/1976.
55 FR 39414,
9/27/1990.
35 FR 8491,
6/2/1970.
56 FR 64716,
12/12/1991.
50 FR 23872,
6/6/1985;
50 CFR
17.95(a).CH
54 FR 20598,
5/12/1989.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
50 FR 23872,
6/6/1985;
50 CFR
17.95(a).CH
35 FR 18319,
12/2/1970.
38 FR 14678,
6/4/1973.
48 FR 43040,
9/21/1983;
49 FR 34504,
8/31/1984.
35 FR 18319,
12/2/1970.
Mouse, New
Mexico meadow Zapus hudsonius luteus
jumping
Wherever found
E
Mouse, Pacific
pocket
Perognathus longimembris
pacificus
Wherever found
E
Mouse, Perdido
Key beach
Peromyscus polionotus
trissyllepsis
Wherever found
E
Wherever found
T
Reithrodontomys raviventris
Wherever found
E
Pseudomys praeconis
Wherever found
E
Pseudomys shortridgei
Wherever found
E
Mouse, smoky
Pseudomys fumeus
Wherever found
E
Mouse,
southeastern
beach
Peromyscus polionotus
niveiventris
Wherever found
T
Mouse, St.
Andrew beach
Peromyscus polionotus
peninsularis
Wherever found
E
Mouse, western
Pseudomys occidentalis
Wherever found
E
Muntjac, Fea's
Muntiacus feae
Wherever found
E
Native-cat,
eastern
Dasyurus viverrinus
Wherever found
E
Numbat
Myrmecobius fasciatus
Wherever found
E
Ocelot
Leopardus (=Felis) pardalis
Wherever found
E
Orangutan
Pongo abelii
Wherever found
E
Mouse, Preble's
Zapus hudsonius preblei
meadow jumping
Mouse, salt
marsh harvest
Mouse, Shark
Bay
Mouse,
Shortridge's
79 FR 33119,
6/10/2014;
50 CFR
17.95(a).CH
59 FR 5306,
2/3/1994;
59 FR 49752,
9/29/1994.
50 FR 23872,
6/6/1985;
50 CFR
17.95(a).CH
63 FR 26517,
5/13/1998;
78 FR 31679,
5/24/2013;
50 CFR
17.40(l);4d
50 CFR
17.95(a).CH
35 FR 16047,
10/13/1970.
35 FR 18319,
12/2/1970.
35 FR 18319,
12/2/1970.
35 FR 18319,
12/2/1970.
54 FR 20598,
5/12/1989.
63 FR 70053,
12/18/1998;
50 CFR
17.95(a).CH
35 FR 18319,
12/2/1970.
44 FR 37124,
6/25/1979.
38 FR 14678,
6/4/1973.
35 FR 18319,
12/2/1970;
38 FR 14678,
6/4/1973.
37 FR 6476,
3/30/1972;
47 FR 31670,
7/21/1982.
35 FR 8491,
6/2/1970; 83 FR
2085, 1/16/2018.
Orangutan
Pongo pygmaeus
Wherever found
E
Oryx, Arabian
Oryx leucoryx
Wherever found
E
Wherever found
E
Wherever found
E
Oryx, scimitarOryx dammah
horned
Otter, Cameroon Aonyx congicus (=congica)
clawless
microdon
Otter, giant
Pteronura brasiliensis
Wherever found
E
Otter, long-tailed
Lontra (=Lutra)
longicaudis (incl. platensis )
Wherever found
E
Otter, marine
Lontra (=Lutra) felina
Wherever found
E
Enhydra lutris kenyoni
Southwest Alaska,
from Attu Island to
Western Cook Inlet,
including Bristol Bay,
the Kodiak
Archipelago, and the
Barren Islands
T
Lontra (=Lutra) provocax
Wherever found
E
Enhydra lutris nereis
Wherever found
T
Ailuropoda melanoleuca
Wherever found
E
Pangolin,
Manis temmincki
Temnick's ground
Wherever found
E
Panther, Florida
Puma (=Felis) concolor coryi
Wherever found
E
Planigale, little
Planigale ingrami subtilissima
Wherever found
E
Planigale,
southern
Planigale tenuirostris
Wherever found
E
Pocket gopher,
Olympia
Thomomys mazama pugetensis Wherever found
T
Pocket gopher,
Roy Prairie
Thomomys mazama glacialis
T
Otter, northern
sea [Southwest
Alaska DPS]
Otter, southern
river
Otter, southern
sea
Panda, giant
Wherever found
35 FR 8491,
6/2/1970; 83 FR
2085, 1/16/2018.
35 FR 8491,
6/2/1970.
70 FR 52319,
9/2/2005.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970;
41 FR 24062,
6/24/1976.
41 FR 24062,
6/24/1976.
70 FR 46366,
8/9/2005;
50 CFR
17.40(p);4d
50 CFR
17.95(a).CH
41 FR 24062,
6/14/1976.
42 FR 2965,
1/14/1977.
49 FR 2779,
1/23/1984.
41 FR 24062,
6/14/1976.
32 FR 4001,
3/11/1967.
35 FR 18319,
12/2/1970.
35 FR 18319,
12/2/1970.
79 FR 19759,
4/9/2014;
50 CFR
17.40(a);4d
50 CFR
17.95(a).CH
79 FR 19759,
4/9/2014;
50 CFR
17.40(a).4d
Pocket gopher,
Tenino
Thomomys mazama tumuli
Wherever found
T
Pocket gopher,
Yelm
Thomomys mazama yelmensis Wherever found
T
Porcupine, thinspined
Chaetomys subspinosus
Wherever found
E
Wherever found
E
Gymnobelideus leadbeateri
Wherever found
E
Burramys parvus
Wherever found
E
Wyulda squamicaudata
Wherever found
E
Cynomys mexicanus
Wherever found
E
Prairie dog, Utah Cynomys parvidens
Wherever found
T
Pronghorn,
peninsular
Wherever found
E
Porpoise, Gulf of
California harbor Phocoena sinus
(cochito, vaquita)
Possum,
Leadbeater's
Possum,
mountain pygmy
Possum, scalytailed
Prairie dog,
Mexican
Antilocapra americana
peninsularis
Pronghorn,
Sonoran
Antilocapra americana
sonoriensis
Pronghorn,
Sonoran
Antilocapra americana
sonoriensis
Wherever found,
except where listed as
E
an experimental
population
In Arizona, an area
north of Interstate 8
and south of Interstate
10, bounded by the
Colorado River on the
west and Interstate 10
on the east; and an
XN
area south of Interstate
8, bounded by
Highway 85 on the
west, Interstates 10
and 19 on the east,
and the U.S.-Mexico
border on the south
79 FR 19759,
4/9/2014;
50 CFR
17.40(a);4d
50 CFR
17.95(a).CH
79 FR 19759,
4/9/2014;
50 CFR
17.40(a);4d
50 CFR
17.95(a).CH
35 FR 8491,
6/2/1970.
50 FR 1056,
1/9/1985;N
50 FR 1056,
1/9/1985.
51 FR 17977,
5/16/1986.
35 FR 18319,
12/2/1970.
35 FR 18319,
12/2/1970.
35 FR 8491,
6/2/1970.
38 FR 14678,
6/4/1973;
49 FR 22330,
5/29/1984;
50 CFR
17.40(g).4d
40 FR 44149,
9/25/1975.
32 FR 4001,
3/11/1967;
35 FR 8491,
6/2/1970.
76 FR 25593,
5/5/2011;
50 CFR
17.84(v).10j
Pudu
Pudu pudu
Wherever found
Puma (=mountain Puma (=Felis) concolor (all
lion)
subsp. except coryi )
U.S.A. (FL)
Puma, Costa
Rican
Puma (=Felis) concolor
costaricensis
Wherever found
Quokka
Setonix brachyurus
Wherever found
Rabbit, Columbia
Basin pygmy
Brachylagus idahoensis
[Columbia Basin
DPS]
Rabbit, Lower
Sylvilagus palustris hefneri
Keys
Rabbit, riparian
Sylvilagus bachmani riparius
brush
Rabbit, Ryukyu
Pentalagus furnessi
Rabbit, volcano
Romerolagus diazi
Rat, false water
Xeromys myoides
Rat, stick-nest
Leporillus conditor
Rat-kangaroo,
brush-tailed
Rat-kangaroo,
desert (=plain)
Rat-kangaroo,
Gaimard's
Rat-kangaroo,
Lesuer's
Rat-kangaroo,
Queensland
Bettongia penicillata
Caloprymnus campestris
Bettongia gaimardi
Bettongia lesueur
Bettongia tropica
Rhinoceros, black Diceros bicornis
Rhinoceros, great
Rhinoceros unicornis
Indian
Rhinoceros,
Rhinoceros sondaicus
Javan
Rhinoceros,
Ceratotherium simum cottoni
northern white
Rhinoceros,
Ceratotherium simum simum
southern white
Rhinoceros,
Dicerorhinus sumatrensis
Sumatran
Rice rat [Lower
FL Keys DPS]
Oryzomys palustris natator
41 FR 24062,
6/14/1976.
56 FR 40265,
8/14/1991;
T(S/A)
50 CFR
17.40(h).4d
41 FR 24062,
E
6/14/1976.
38 FR 14678,
E
6/4/1973.
E
U.S.A. (WA—Douglas,
Grant, Lincoln, Adams, E
Benton Counties)
68 FR 10388,
3/5/2003.
55 FR 25588,
6/21/1990.
65 FR 8881,
Wherever found
E
2/23/2000.
44 FR 37124,
Wherever found
E
6/25/1979.
35 FR 8491,
Wherever found
E
6/2/1970.
35 FR 18319,
Wherever found
E
12/2/1970.
38 FR 14678,
Wherever found
E
6/4/1970.
35 FR 18319,
Wherever found
E
12/2/1970.
35 FR 18319,
Wherever found
E
12/2/1970.
38 FR 14678,
Wherever found
E
6/4/1970.
35 FR 18319,
Wherever found
E
12/2/1970.
35 FR 18319,
Wherever found
E
12/2/1970.
45 FR 47352,
Wherever found
E
7/14/1980.
35 FR 18319,
Wherever found
E
12/2/1970.
35 FR 8491,
Wherever found
E
6/2/1970.
35 FR 8491,
Wherever found
E
6/2/1970.
79 FR 28847,
Wherever found
T(S/A)
5/20/2014.
35 FR 8491,
Wherever found
E
6/2/1970.
56 FR 19809,
Lower FL Keys (west
4/30/1990;
E
of Seven Mile Bridge)
50 CFR
17.95(a).CH
Wherever found
E
Saiga, Mongolian
Saiga tatarica mongolica
(antelope)
Saki, southern
Chiropotes satanas satanas
bearded
Wherever found
E
Wherever found
E
Saki, white-nosed Chiropotes albinasus
Wherever found
E
Sea lion, Steller
[Western DPS]
Eumetopias jubatus
Western DPS—see 50
E
CFR 224.101
Seal, bearded
[Beringia DPS]
Erignathus barbatus nauticus
Beringia DPS—see 50
T
CFR 223.102
Seal, bearded
[Okhotsk DPS]
Erignathus barbatus nauticus
Okhotsk DPS—see 50
T
CFR 223.102
Seal, Guadalupe
Arctocephalus townsendi
fur
Wherever found
T
Seal, Hawaiian
monk
Neomonachus schauinslandi
(=Monachus schauinslandi)
Wherever found
E
Seal,
Mediterranean
monk
Monachus monachus
Wherever found
E
Seal, ringed
(Arctic
subspecies)
Phoca (=Pusa) hispida hispida
Wherever found
T
Seal, ringed
(Baltic
subspecies)
Phoca (=Pusa) hispida botnica Wherever found
T
41 FR 24062,
6/14/1976.
51 FR 17977,
5/16/1986.
35 FR 8491,
6/2/1970.
55 FR 13488,
4/10/1990;
55 FR 50005,
12/4/1990;
62 FR 24345,
5/5/1997;N
62 FR 30772,
6/5/1997;
50 CFR
226.202;CH
50 CFR 224.103.
77 FR 76739,
12/28/2012;N
79 FR 42687,
7/23/2014.
77 FR 76739,
12/28/2012;N
79 FR 42687,
7/23/2014.
32 FR 4001,
3/11/1967;
35 FR 16047,
10/13/1970;
50 FR 51251,
12/16/1985;
55 FR 14051,
3/23/1999;N
50 CFR
223.201.4d
41 FR 51611,
11/23/1976;
55 FR 14051,
3/23/1999;N
50 CFR
226.201.CH
35 FR 8491,
6/2/1970;
55 FR 14051,
3/23/1999.N
77 FR 76705,
12/28/2012;N
79 FR 42687,
7/23/2014.
77 FR 76705,
12/28/2012;N
79 FR 42687,
7/23/2014.
Seal, ringed
(Ladoga
subspecies)
Phoca (=Pusa) hispida
ladogensis
Wherever found
E
Seal, ringed
(Okhotsk
subspecies)
Phoca (=Pusa) hispida
ochotensis
Wherever found
T
Seal, ringed
(Saimaa
subspecies)
Phoca (=Pusa) hispida
saimensis
Wherever found
E
Seal, spotted
[Southern DPS]
Phoca largha
Southern DPS—see 50
T
CFR 223.102
Seledang
Bos gaurus
Wherever found
E
Wherever found
E
Wherever found
E
Ovis vignei vignei
Wherever found
E
Ovis canadensis nelsoni
U.S.A. (CA) Peninsular
E
Ranges
Serow
Serval, Barbary
Shapo
Sheep,
Peninsular
bighorn
[Peninsular CA
DPS]
Naemorhedus (=Capricornis)
sumatraensis
Leptailurus (=Felis) serval
constantina
Sheep, Sierra
Nevada bighorn
Ovis canadensis sierrae
U.S.A. (CA)—Sierra
Nevada
E
Shou
Cervus elaphus wallichi
Wherever found
E
Shrew, Buena
Vista Lake
Sorex ornatus relictus
Wherever found
E
Siamang
Symphalangus syndactylus
Wherever found
E
Sifakas
Propithecus spp.
Wherever found
E
Sloth, Brazilian
three-toed
Bradypus torquatus
Wherever found
E
77 FR 76705,
12/28/2012;N
79 FR 42687,
7/23/2014.
77 FR 76705,
12/28/2012;N
79 FR 42687,
7/23/2014.
58 FR 26920,
5/6/1993;N 58 FR
40538, 7/28/1993.
75 FR 65239,
10/22/2010;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.212.4d
35 FR 8491,
6/2/1970.
41 FR 26019,
6/24/1976.
35 FR 8491,
6/2/1970.
41 FR 26019,
6/24/1976.
63 FR 13134,
3/18/1998;
50 CFR
17.95(a).CH
64 FR 19300,
4/20/1999;
65 FR 20,
1/3/2000;
73 FR 45534,
8/5/2008;
50 CFR
17.95(a).CH
35 FR 8491,
6/2/1970.
67 FR 10101,
3/6/2002;
50 CFR
17.95(a).CH
41 FR 24062,
6/14/1976.
35 FR 18319,
12/2/1970.
35 FR 8491,
6/2/1970.
Solenodon,
Solenodon cubanus
Cuban
Solenodon,
Solenodon paradoxus
Haitian
Squirrel, Carolina
Glaucomys sabrinus coloratus
northern flying
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Squirrel, northern Spermophilus brunneus
Idaho ground
brunneus
Wherever found
T
Stag, Barbary
Cervus elaphus barbarus
Wherever found
E
Stag, Kashmir
Cervus elaphus hanglu
Wherever found
E
Suni, Zanzibar
Neotragus moschatus
moschatus
Wherever found
E
Tahr, Arabian
Hemitragus jayakari
Wherever found
E
Tamaraw
Bubalus mindorensis
Wherever found
E
Tamarin, goldenLeontopithecus spp.
rumped
Wherever found
E
Tamarin, pied
Saguinus bicolor
Wherever found
E
Tamarin, whitefooted
Saguinus leucopus
Wherever found
T
Tapir, Asian
Tapirus indicus
Wherever found
E
Tapir, Central
American
Tapirus bairdii
Wherever found
E
Tapir, mountain
Tapirus pinchaque
Wherever found
E
Tapir, South
American
(=Brazilian)
Tapirus terrestris
Wherever found
E
Squirrel, Mount
Graham red
Tamiasciurus hudsonicus
grahamensis
Tarsier, Philippine Tarsius syrichta
Wherever found
T
Tiger
Wherever found
E
Tiger, Tasmanian Thylacinus cynocephalus
Wherever found
E
Uakari (all
species)
Cacajao spp.
Wherever found
E
Urial
Ovis musimon ophion
Wherever found
E
Panthera tigris
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
50 FR 26999,
7/1/1985.
52 FR 20994,
6/3/1987;
50 CFR
17.95(a).CH
65 FR 17780,
4/5/2000.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
44 FR 37124,
6/25/1979.
44 FR 37124,
6/25/1979.
35 FR 18319,
12/2/1970.
35 FR 8491,
6/2/1970.
41 FR 45990,
10/19/1976.
41 FR 45990,
10/19/1976;
50 CFR
17.40(c).4d
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
41 FR 45990,
10/19/1976;
50 CFR
17.40(c).4d
35 FR 8491,
6/2/1970;
37 FR 6476,
3/30/1972.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
Vicuna
[Argentina,
Vicugna vicugna
Bolivia, Chile and
Peru]
Wherever found,
except Ecudator
T
Vicuna [Ecuador
Vicugna vicugna
DPS]
Ecuador
E
Vole, Amargosa
Microtus californicus scirpensis Wherever found
Vole, Florida salt Microtus pennsylvanicus
marsh
dukecampbelli
Wallaby, banded
Lagostrophus fasciatus
hare
Wallaby, brindled
Onychogalea fraenata
nail-tailed
Wallaby, crescent
Onychogalea lunata
nail-tailed
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Whale, beluga
Delphinapterus leucas
[Cook Inlet DPS]
Cook Inlet DPS—see
50 CFR 224.101
E
Whale, blue
Wherever found
E
Whale, bowhead Balaena mysticetus
Wherever found
E
Whale, false killer
[Main Hawaiian
Pseudorca crassidens
Islands Insular
DPS]
Main Hawaiian
Islands Insular DPS— E
see 50 CFR 224.101
Whale, finback
Balaenoptera physalus
Wherever found
Whale, gray
[Western North
Pacific DPS]
Eschrichtius robustus
Western North Pacific
DPS—see 50 CFR
E
224.101
Wallaby, Parma
Macropus parma
Wallaby, western
Lagorchestes hirsutus
hare
Wallaby, yellowPetrogale xanthopus
footed rock
Balaenoptera musculus
E
35 FR 8491,
6/2/1970;
67 FR 37695,
5/30/2002;
50 CFR
17.40(m).4d
35 FR 8491,
6/2/1970;
67 FR 37695,
5/30/2002.
49 FR 45160,
11/15/1984;
50 CFR
17.95(a).CH
56 FR 1457,
1/14/1991.
35 FR 18319,
12/2/1970.
35 FR 18319,
12/2/1970.
35 FR 18319,
12/2/1970.
35 FR 18319,
12/2/1970.
35 FR 18319,
12/2/1970.
38 FR 14678,
6/4/1973.
73 FR 62919,
10/22/2008;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.220.CH
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
77 FR 70915,
11/28/2012;N 79
FR 42687,
7/23/2014; 50
CFR 226.226. CH
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970;
59 FR 31094,
6/16/1994;N
79 FR 42687,
7/23/2014.
Whale,
humpback
[Arabian Sea
DPS]
Arabian Sea DPS—
see 50 CFR 224.101
E
Whale,
humpback [Cape
Verde
Megaptera novaeangliae
Islands/Northwest
Africa DPS]
Cape Verde
Islands/Northwest
Africa DPS—see 50
CFR 224.101
E
Whale,
humpback
Megaptera novaeangliae
[Central America
DPS]
Central America DPS
E
—see 50 CFR 224.101
Whale,
humpback
[Mexico DPS]
Megaptera novaeangliae
Mexico DPS—see 50
T
CFR 223.102
Megaptera novaeangliae
Western North Pacific
DPS—see 50 CFR
E
224.101
Whale,
humpback
[Western North
Pacific DPS]
Megaptera novaeangliae
35 FR 8491,
6/2/1970;
35 FR 18319,
12/2/1970;
81 FR 62260,
9/8/2016N;
81 FR 93639,
12/21/2016.
35 FR 8491,
6/0/1970;
35 FR 18319,
12/2/1970;
81 FR 62260,
9/8/2016N;
81 FR 93639,
12/21/2016.
35 FR 8491,
6/2/1970;
35 FR 18319,
12/2/1970;
81 FR 62260,
9/8/2016N;
81 FR 93639,
12/21/2016.
35 FR 8491,
6/2/1970;
35 FR 18319,
12/2/1970;
81 FR 62260,
9/8/2016N;
81 FR 93639,
12/21/2016;
50 CFR 223.213;
50 CFR 223.214.
35 FR 8491,
6/2/1970;
35 FR 18319,
12/2/1970;
81 FR 62260,
9/8/2016N;
81 FR 93639,
12/21/2016;
50 CFR 224.103.
Whale, killer
[Southern
Resident DPS]
Orcinus orca
Southern Resident
DPS—see 50 CFR
224.101
E
Whale, North
Atlantic right
Eubalaena glacialis
Wherever found
E
Whale, North
Pacific right
Eubalaena japonica
Wherever found
E
Whale, sei
Balaenoptera borealis
Wherever found
E
Wherever found
E
Wherever found
E
Whale, Southern
Eubalaena australis
right
Whale, sperm
Physeter catodon
(=macrocephalus)
70 FR 69903,
11/18/2005;N
72 FR 16284,
4/4/2007;
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
80 CFR 7380,
2/10/2015;N
50 CFR 224.103;
50 CFR
226.206.CH
35 FR 8491,
6/2/1970;
73 FR 12024,
3/6/2008;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR 224.103;
50 CFR 224.105;
50 CFR
226.203.CH
35 FR 8491,
6/2/1970;
73 FR 12024,
3/6/2008;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.215.CH
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970;
73 FR 12024,
3/6/2008;N
76 FR 20558,
4/13/2011.
35 FR 8491,
6/2/1970.
Wolf, gray
Canis lupus
U.S.A.: All of AL, AR,
CA, CO, CT, DE, FL,
GA, IA, IN, IL, KS, KY,
LA, MA, MD, ME, MI,
MO, MS, NC, ND, NE,
NH, NJ, NV, NY, OH, E
OK, PA, RI, SC, SD,
TN, TX, VA, VT, WI,
and WV; and portions
of AZ, NM, OR, UT,
and WA as follows:
(1) Northern AZ (that
portion north of the
centerline of Interstate
Highway 40);
(2) Northern NM (that
portion north of the
centerline of Interstate
Highway 40);
(3) Western OR (that
portion of OR west of
the centerline of
Highway 395 and
Highway 78 north of
Burns Junction and
that portion of OR west
of the centerline of
Highway 95 south of
Burns Junction);
(4) Most of Utah (that
portion of UT south
and west of the
centerline of Highway
84 and that portion of
UT south of Highway
80 from Echo to the
UT/WY Stateline); and
(5) Western WA (that
portion of WA west of
the centerline of
Highway 97 and
Highway 17 north of
Mesa and that portion
of WA west of the
centerline of Highway
395 south of Mesa).
Mexico.
32 FR 4001,
3/11/1967;
38 FR 14678,
6/4/1973;
41 FR 17736,
4/28/1976;
41 FR 24062,
6/14/1976;
43 FR 9607,
3/9/1978;
80 FR 9218,
2/20/2015;
50 CFR
17.95(a).CH
Wolf, gray [MN
DPS]
Canis lupus
U.S.A. (MN)
T
Wolf, maned
Chrysocyon brachyurus
Wherever found
E
Canis lupus baileyi
Wherever found,
except where included
in an experimental
E
population as set forth
in §17.84(k)
Wolf, Mexican
Canis lupus baileyi
U.S.A. (portions of AZ
and NM)—see
XN
§17.84(k)
Wolf, red
Canis rufus
Wherever found,
except where listed as
E
an experimental
population
Wolf, red
Canis rufus
U.S.A. (portions of NC
and TN—see §17.84(c) XN
(9))
Wolf, Mexican
Wombat,
Queensland
Lasiorhinus krefftii(formerly L.
hairy-nosed (incl. barnardi and L. gillespiei )
Barnard's)
Wherever found
E
Woodrat, Key
Largo
Neotoma floridana smalli
Wherever found
E
Woodrat, riparian
(San Joaquin
Neotoma fuscipes riparia
Valley)
Wherever found
E
Yak, wild
Bos mutus (=grunniens m.)
Wherever found
E
Zebra, Grevy's
Equus grevyi
Wherever found
T
43 FR 9607,
3/9/1978;
50 CFR
17.40(d);4d
50 CFR
17.95(a).CH
35 FR 18319,
12/2/1970.
40 FR 17590,
4/21/1975;
80 FR 2488,
1/16/2015.
63 FR 1752,
1/12/1998;
80 FR 2512,
1/16/2015;
50 CFR
17.84(k).10j
32 FR 4001,
3/11/1967;
51 FR 41790,
11/19/1986;
56 FR 56325,
11/4/1991;
60 FR 18941,
4/13/1995.
51 FR 41790,
11/19/1986;
56 FR 56325,
11/4/1991;
60 FR 18941,
4/13/1995;
50 CFR
17.84(c).10j
35 FR 18319,
12/2/1970;
38 FR 14678,
6/4/1973.
48 FR 43040,
9/21/1983;
49 FR 34504,
8/31/1984.
65 FR 8881,
2/23/2000.
35 FR 8491,
6/2/1970.
44 FR 49218,
8/21/1979.
Zebra,
Hartmann's
mountain
Equus zebra hartmannae
Zebra, mountain Equus zebra zebra
Wherever found
T
Wherever found
E
44 FR 49218,
8/21/1979;
46 FR 11665,
2/10/1981.
41 FR 24062,
6/14/1976;
46 FR 11665,
2/10/1981.
Birds
Adjutant, greater Leptoptilos dubius
Wherever found
E
Akekee
(honeycreeper)
Loxops caeruleirostris
Wherever found
E
Akepa, Hawaii
Loxops coccineus
Wherever found
E
Akepa, Maui
Loxops ochraceus
Wherever found
E
Akialoa, Kauai
Hemignathus stejnegeri
Wherever found
E
Akiapolaau
Hemignathus wilsoni
Wherever found
E
Akikiki
(honeycreeper)
Oreomystis bairdi
Wherever found
E
Albatross,
Amsterdam
Diomedea amsterdamensis
Wherever found
E
Albatross, short- Phoebastria (=Diomedea)
tailed
albatrus
Wherever found
E
Alethe, Thyolo
Alethe choloensis
Wherever found
E
Grallaria milleri
Wherever found
E
Formicivora erythronotos
Wherever found
E
Blackbird, yellowAgelaius xanthomus
shouldered
Wherever found
E
Bobwhite,
masked (quail)
Colinus virginianus ridgwayi
Wherever found
E
Booby, Abbott's
Papasula (=Sula) abbotti
Wherever found
E
Bristlebird,
western
Bristlebird,
western rufous
Dasyornis longirostris
(=brachypterus l.)
Wherever found
E
Dasyornis broadbenti littoralis
Wherever found
E
Antpitta, brownbanded
Antwren, blackhooded
76 FR 50052,
8/11/2011.
75 FR 18960,
4/13/2010;
50 CFR
17.95(b).CH
35 FR 16047,
10/13/1970.
35 FR 16047,
10/13/1970.
32 FR 4001,
3/11/1967.
32 FR 4001,
3/11/1967.
75 FR 18960,
4/13/2010;
50 CFR
17.95(b).CH
60 FR 2899,
1/12/1995.
35 FR 8491,
6/2/1970;
65 FR 46643,
7/31/2000.
60 FR 2899,
1/12/1995.
78 FR 64637,
10/29/2013.
75 FR 81794,
12/28/2010.
41 FR 51019,
11/19/1976;
50 CFR
17.95(b).CH
32 FR 4001,
3/11/1967;
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
Bulbul, Mauritius
olivaceous
Bullfinch, Sao
Miguel (finch)
Bush-shrike,
Ulugura
Bushwren, New
Zealand
Bustard, great
Indian
Hypsipetes borbonicus
olivaceus
Wherever found
E
Pyrrhula pyrrhula murina
Wherever found
E
Malaconotus alius
Wherever found
T
Xenicus longipes
Wherever found
E
Ardeotis (=Choriotis) nigriceps
Wherever found
E
Cahow
Pterodroma cahow
Wherever found
E
Wherever found
E
U.S.A. (FL)
T
Cinclodes, royal Cinclodes aricomae
Wherever found
E
Cockatoo,
Philippine
Cacatua haematuropygia
Wherever found
E
Cockatoo,
salmon-crested
Cacatua moluccensis
Wherever found
T
Cockatoo, white Cacatua alba
Wherever found
T
Cockatoo, yellowCacatua sulphurea
crested
Wherever found
E
Condor, Andean Vultur gryphus
Wherever found
E
Condor,
California
Gymnogyps californianus
U.S.A. only, except
where listed as an
experimental
population
E
Condor,
California
Gymnogyps californianus
U.S.A. (specific
portions of Arizona,
Nevada, and Utah)—
see §17.84(j)
XN
Coot, Hawaiian
Fulica americana alai
Wherever found
E
Cotinga, banded Cotinga maculata
Wherever found
E
Cotinga, whitewinged
Xipholena atropurpurea
Wherever found
E
Courser, Jerdon's Rhinoptilus bitorquatus
Wherever found
E
Capercaillie,
Tetrao urogallus cantabricus
Cantabrian
Caracara,
crested,
Polyborus plancus audubonii
(Audubon's) [FL
DPS]
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
60 FR 2899,
1/12/1995.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
76 FR 50052,
8/11/2011.
52 FR 25229,
7/6/1987.
77 FR 43434,
7/24/2012.
79 FR 35870,
6/24/2014.
76 FR 30758,
5/26/2011;
50 CFR
17.41(c).4d
79 FR 35870,
6/24/2014;
50 CFR
17.41(c).4d
79 FR 35870,
6/24/2014.
35 FR 18319,
12/2/1970.
32 FR 4001,
3/11/1967;
61 FR 54045,
10/16/1996;
50 CFR
17.95(b).CH
61 FR 54045,
10/16/1996;
50 CFR
17.84(j).10j
35 FR 16047,
10/13/1970.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
76 FR 50052,
8/11/2011.
Crane, blacknecked
Crane, Cuba
sandhill
Grus nigricollis
Wherever found
E
Grus canadensis nesiotes
Wherever found
E
Grus monacha
Wherever found
E
Crane, Japanese Grus japonensis
Wherever found
E
Crane,
Mississippi
sandhill
Grus canadensis pulla
Wherever found
E
Grus leucogeranus
Wherever found
E
Grus vipio
Wherever found
E
Crane, hooded
Crane, Siberian
white
Crane, whitenaped
Crane, whooping Grus americana
Wherever found,
except where listed as
E
an experimental
population
Crane, whooping Grus americana
U.S.A. (AL, AR, CO,
FL, GA, ID, IL, IN, IA,
KY, LA, MI, MN, MS,
XN
MO, NC, NM, OH, SC,
TN, UT, VA, WI, WV,
western half of WY)
Creeper, Hawaii Oreomystis mana
Wherever found
E
Creeper, Molokai Paroreomyza flammea
Wherever found
E
Creeper, Oahu
Paroreomyza maculata
Wherever found
E
Crow, Hawaiian
Corvus hawaiiensis
Wherever found
E
Crow, Mariana
Corvus kubaryi
Wherever found
E
Crow, whitenecked
Corvus leucognaphalus
Wherever found
E
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
35 FR 18319,
12/2/1970.
35 FR 8491,
6/2/1970.
38 FR 14678,
6/4/1973;
50 CFR
17.95(b).CH
35 FR 18319,
12/2/1970.
41 FR 24062,
6/14/1976.
32 FR 4001,
3/11/1967;
35 FR 8491,
3/9/1978;
50 CFR
17.95(b).CH
58 FR 5561,
1/22/1993;
62 FR 38932,
7/21/1997;
66 FR 33903,
6/26/2001;
76 FR 6066,
2/3/2011;
50 CFR
17.84(h).10j
40 FR 44149,
9/25/1975.
35 FR 16047,
10/13/1970.
35 FR 16047,
10/13/1970.
32 FR 4001,
3/11/1967.
49 FR 33881,
8/27/1984;
50 CFR
17.95(b).CH
56 FR 13598,
4/3/1991.
Cuckoo, yellowbilled [Western
DPS]
Cuckoo-shrike,
Mauritius
Cuckoo-shrike,
Reunion
Curassow, bluebilled
Curassow, razorbilled
Curassow, redbilled
Curassow,
Trinidad whiteheaded
Curlew, Eskimo
Coccyzus americanus
Western DPS: U.S.A.
(AZ, CA, CO (western),
ID, MT (western), NM
(western), NV, OR, TX
(western), UT, WA, WY
(western)); Canada
(British Columbia
T
(southwestern); Mexico
(Baja California, Baja
California Sur,
Chihuahua, Durango
(western), Sinaloa,
Sonora)
Coquus typicus
Wherever found
E
Coquus newtoni
Wherever found
E
Crax alberti
Wherever found
E
Mitu mitu mitu
Wherever found
E
Crax blumenbachii
Wherever found
E
Pipile pipile pipile
Wherever found
E
Numenius borealis
Curlew, slenderNumenius tenuirostris
billed
Dove, clovenDrepanoptila holosericea
feathered
Dove, Grenada
Leptotila rufaxilla wellsi
gray-fronted
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Duck, Hawaiian
Anas wyvilliana
Wherever found
E
Duck, Laysan
Anas laysanensis
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Duck, pinkRhodonessa caryophyllacea
headed
Duck, whiteCairina scutulata
winged wood
Eagle, Greenland Haliaeetus albicilla
white-tailed
groenlandicus
Eagle, harpy
Harpia harpyja
Eagle,
Haliaeetus vociferoides
Madagascar sea
Eagle,
Madagascar
Eutriorchis astur
serpent
79 FR 59991,
10/3/2014.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
78 FR 64637,
10/29/2013.
41 FR 24062,
6/14/1976.
35 FR 18319,
12/2/1970.
35 FR 8491,
6/2/1970.
32 FR 4001,
3/11/1967;
35 FR 8491,
6/2/1970.
76 FR 50052,
8/11/2011.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
32 FR 4001,
3/11/1967.
32 FR 4001,
3/11/1967.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
60 FR 2899,
1/12/1995.
60 FR 2899,
1/12/1995.
Eagle, Philippine Pithecophaga jefferyi
Wherever found
E
Eagle, Spanish
imperial
Aquila heliaca adalberti
Wherever found
E
Egret, Chinese
Egretta eulophotes
Wherever found
E
Eider, spectacled Somateria fischeri
Wherever found
T
Eider, Steller's
[AK Breeding
DPS]
Polysticta stelleri
U.S.A. (AK breeding
population only)
T
Elepaio, Oahu
Chasiempis ibidis
Wherever found
E
Falcon, Eurasian
Falco peregrinus peregrinus
peregrine
Wherever found
E
Falcon, northern
Falco femoralis septentrionalis
aplomado
Wherever found,
except where listed as
E
an experimental
population
Falcon, northern
Falco femoralis septentrionalis
aplomado
Finch, Laysan
(honeycreeper)
Finch, Nihoa
(honeycreeper)
Fire-eye, fringedbacked
Flamingo,
Andean
Flycatcher,
Euler's
Flycatcher,
Seychelles
paradise
Flycatcher,
southwestern
willow
U.S.A. (AZ, NM)
XN
Telespyza cantans
Wherever found
E
Telespyza ultima
Wherever found
E
Pyriglena atra
Wherever found
E
Phoenicoparrus andinus
Wherever found
E
Empidonax euleri johnstonei
Wherever found
E
Terpsiphone corvina
Wherever found
E
Empidonax traillii extimus
Wherever found
E
Flycatcher, Tahiti Pomarea nigra
Wherever found
E
Fody, Mauritius
Wherever found
E
Fody, Rodrigues Foudia flavicans
Wherever found
E
Fody, Seychelles
Foudia sechellarum
(weaver-finch)
Wherever found
E
Foudia rubra
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
58 FR 27474,
5/10/1993;
50 CFR
17.95(b).CH
62 FR 31748,
6/11/1997;
50 CFR
17.95(b).CH
65 FR 20760,
4/18/2000;
50 CFR
17.95(b).CH
41 FR 24062,
6/14/1976.
51 FR 6686,
2/25/1986.
71 FR 42298,
7/26/2006;
50 CFR
17.84(p).10j
32 FR 4001,
3/11/1967.
32 FR 4001,
3/11/1967.
75 FR 81794,
12/28/2010.
75 FR 50814,
8/17/2010.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
60 FR 10695,
2/27/1995;
50 CFR
17.95(b).CH
35 FR 8491,
6/2/1970.
60 FR 2899,
1/12/1995.
60 FR 2899,
1/12/1995.
35 FR 8491,
6/2/1970.
Francolin,
Djibouti
Frigatebird,
Andrew's
Gallinule,
Hawaiian
common (Alae
ula)
Francolinus ochropectus
Wherever found
E
Fregata andrewsi
Wherever found
E
Gallinula chloropus (=galeata)
sandvicensis
Wherever found
E
60 FR 2899,
1/12/1995.
41 FR 24062,
6/14/1976.
32 FR 4001,
3/11/1967.
58 FR 16742,
3/30/1993;
50 CFR
17.41(b);4d
50 CFR
17.95(b).CH
32 FR 4001,
3/11/1967; 84 FR
69918,
12/19/2019; 50
CFR 17.41(d)4d.
35 FR 8491,
6/2/1970.
Gnatcatcher,
Polioptila californica californica Wherever found
coastal California
T
Goose, Hawaiian
Branta sandvicensis
(Nene)
Wherever found
T
Accipiter fasciatus natalis
Wherever found
E
Accipiter gentilis laingi
British Columbia,
Canada
T
77 FR 45870,
8/1/2012.
Quisicalus palustris
Wherever found
E
35 FR 8491,
6/2/1970.
Amytornis goyderi
Wherever found
E
35 FR 8491,
6/2/1970.
Grebe, Alaotra
Tachybaptus rufoflavatus
Wherever found
E
Grebe, Atitlan
Podilymbus gigas
Wherever found
E
Grebe, Junín
Podiceps taczanowskii
Wherever found
E
Wherever found
E
Wherever found
E
75 FR 81794,
12/28/2010.
U.S.A. (AS)
E
81 FR 65466,
9/22/2016.
Goshawk,
Christmas Island
Goshawk, Queen
Charlotte [British
Columbia DPS]
Grackle, slenderbilled
Grasswren,
Eyrean
(flycatcher)
Greenshank,
Tringa guttifer
Nordmann's
Ground-cuckoo,
southeastern
Neomorphus geoffroyi dulcis
rufous-vented
Ground-dove,
friendly (=
tuaimeo)
Gallicolumba stairi
(American
Samoa DPS)
Guan, cauca
Penelope perspicax
Wherever found
E
Guan, horned
Oreophasis derbianus
Wherever found
E
Penelope albipennis
Wherever found
E
Agelastes meleagrides
Wherever found
T
Guan, whitewinged
Guineafowl,
white-breasted
60 FR 2899,
1/12/1995.
35 FR 8491,
6/2/1970.
77 FR 43434,
7/24/2012.
41 FR 24062,
6/14/1976.
78 FR 64637,
10/29/2013.
35 FR 8491,
6/2/1970.
55 FR 39858,
9/28/1990.
60 FR 2899,
1/12/1995.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
Gull, Audouin's
Larus audouinii
Wherever found
E
Gull, relict
Larus relictus
Wherever found
E
Wherever found
E
Buteo platypterus brunnescens Wherever found
E
59 FR 46710,
9/9/1994.
Accipiter striatus venator
Wherever found
E
59 FR 46710,
9/9/1994.
Ramphodon (=Glaucis) dohrnii Wherever found
E
41 FR 24062,
6/14/1976.
Phaethornis malaris
margarettae
Wherever found
E
Palmeria dolei
Wherever found
E
Honeyeater,
helmeted
Hornbill,
helmeted
Hummingbird,
Honduran
emerald
Lichenostomus melanops
cassidix (=Meliphaga c.)
Wherever found
E
Buceros (=Rhinoplax) vigil
Wherever found
E
Amazilia luciae
Wherever found
E
Ibis, giant
Pseudibis gigantea
Wherever found
E
Nipponia nippon
Wherever found
E
Geronticus eremita
Wherever found
E
Drepanis coccinea
Wherever found
T
Kagu
Rhynochetos jubatus
Wherever found
E
Kakapo
Strigops habroptilus
Wherever found
E
Kestrel, Mauritius Falco punctatus
Wherever found
E
Kestrel,
Seychelles
Wherever found
E
Kingfisher, Guam Halcyon cinnamomina
Micronesian
cinnamomina
Wherever found
E
Kite, Cuba hook- Chondrohierax uncinatus
billed
wilsonii
Wherever found
E
Hawk, Galapagos Buteo galapagoensis
Hawk, Puerto
Rican broadwinged
Hawk, Puerto
Rican sharpshinned
Hermit, hookbilled
(hummingbird)
Hermit,
Margaretta's
Honeycreeper,
crested
(Akohekohe)
Ibis, Japanese
crested
Ibis, northern
bald
Iiwi
(honeycreeper)
Falco araea
75 FR 81794,
12/28/2010.
32 FR 4001,
3/11/1967;
50 CFR
17.95(b).CH
35 FR 18319,
12/2/1970.
41 FR 24062,
6/14/1976.
80 FR 45086,
7/29/2015.
73 FR 3146,
1/16/2008.
35 FR 8491,
6/2/1970.
55 FR 39858,
9/28/1990.
82 FR 43873,
9/20/2017.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
49 FR 33881,
8/27/1984;
69 FR 62943,
10/28/2004;
50 CFR
17.95(b).CH
35 FR 8491,
6/2/1970.
Kite, Grenada
hook-billed
Chondrohierax uncinatus mirus Wherever found
E
Kite, snail
(Everglade)
Rostrhamus sociabilis plumbeus U.S.A. (FL)
E
Knot, rufa red
Calidris canutus rufa
Wherever found
T
Kokako
(wattlebird)
Callaeas cinerea
Wherever found
E
Lark, Raso
Alauda razae
Wherever found
E
Lark, streaked
horned
Eremophila alpestris strigata
Wherever found
T
Macaw, bluethroated
Ara glaucogularis
Wherever found
E
Macaw, glaucous Anodorhynchus glaucus
Wherever found
E
Macaw, great
green
Wherever found
E
Macaw, hyacinth Anodorhynchus hyacinthinus
Wherever found
T
Macaw, indigo
Wherever found
E
Macaw, little blue Cyanopsitta spixii
Wherever found
E
Macaw, military
Ara militaris
Wherever found
E
Macaw, scarlet
Ara macao cyanoptera
Wherever found
E
Macaw, scarlet
[Northern DPS]
Macaw, scarlet
[Southern DPS]
Macaw, scarlet
[Subspecies
crosses]
Magpie-robin,
Seychelles
(thrush)
Ara ambiguus
Anodorhynchus leari
35 FR 8491,
6/2/1970.
32 FR 4001,
3/11/1967;
50 CFR
17.95(b).CH
79 FR 73705,
12/11/2014.
35 FR 8491,
6/2/1970.
60 FR 2899,
1/12/1995.
78 FR 61451,
10/3/2013;
50 CFR
17.41(a);4d
50 CFR
17.95(b).CH
78 FR 61208,
10/3/2013.
41 FR 24062,
6/14/1976.
80 FR 59975,
10/2/2015.
83 FR 39894,
8/13/2018; 50
CFR 17.41(c)4d.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
80 FR 59975,
10/2/2015.
84 FR 6278,
2/26/2019.
Colombia (northwest of
84 FR 6278,
the Andes), Costa Rica
Ara macao macao
T
2/26/2019; 50
(Pacific slope),
CFR 17.41(c).4d
Panama (mainland)
Bolivia, Brazil,
Colombia (southeast of
84 FR 6278,
the Andes), Ecuador,
Ara macao macao
T(S/A) 2/26/2019; 50
French Guiana,
CFR 17.41(c).4d
Guyana, Peru,
Suriname, Venezuela
Costa Rica, Nicaragua
84 FR 6278,
Ara macao macaoX Ara macao
(Atlantic slope border T(S/A) 2/26/2019; 50
cyanoptera
region)
CFR 17.41(c).4d
Copsychus sechellarum
Malimbe, Ibadan Malimbus ibadanensis
Wherever found
E
35 FR 8491,
6/2/1970.
Wherever found
E
60 FR 2899,
1/12/1995.
Malkoha, redfaced (cuckoo)
Mao (= maomao)
(honeyeater)
Megapode,
Maleo
Megapode,
Micronesian (=La
Perouse's)
Merganser,
Brazilian
Millerbird, Nihoa
(old world
warbler)
Mockingbird,
Socorro
Moorhen,
Mariana common
Phaenicophaeus
pyrrhocephalus
Wherever found
E
Gymnomyza samoensis
Wherever found
E
Macrocephalon maleo
Wherever found
E
Megapodius laperouse
Wherever found
E
35 FR 8491,
6/2/1970.
Mergus octosetaceus
Wherever found
E
75 FR 81794,
12/28/2010.
Acrocephalus familiaris kingi
Wherever found
E
32 FR 4001,
3/11/1967.
Mimus Graysoni
Wherever found
E
Gallinula chloropus guami
Wherever found
E
Murrelet, marbled
[CA, OR, WA
Brachyramphus marmoratus
DPS]
U.S.A. (CA, OR, WA)
T
Nightjar, Puerto
Rican
Caprimulgus noctitherus
Wherever found
E
Nukupuu, Kauai Hemignathus hanapepe
Wherever found
E
Nukupuu, Maui
Hemignathus affinis
Wherever found
E
Sitta ledanti
Wherever found
E
Moho braccatus
Wherever found
E
Wherever found
E
Struthio camelus spatzi
Wherever found
E
Psittirostra psittacea
Wherever found
E
Otus rutilus capnodes
Wherever found
E
Owl, giant scops Mimizuku (=Otus) gurneyi
Wherever found
E
Owl, Madagascar
Tyto soumagnei
red
Wherever found
E
Owl, Mexican
spotted
Wherever found
T
Nuthatch,
Algerian
`O`o, Kauai
(honeyeater)
Ostrich, Arabian Struthio camelus syriacus
Ostrich, West
African
`O`u
(honeycreeper)
Owl, Anjouan
scops
Strix occidentalis lucida
35 FR 8491,
6/2/1970.
81 FR 65466,
9/22/2016.
35 FR 8491,
6/2/1970.
73 FR 3146,
1/16/2008.
49 FR 33881,
8/27/1984.
57 FR 45337,
10/1/1992;
50 CFR
17.95(b).CH
38 FR 14678,
6/4/1973.
32 FR 4001,
3/11/1967;
35 FR 16047,
10/13/1970.
35 FR 16047,
10/13/1970.
60 FR 2899,
1/12/1995.
32 FR 4001,
3/11/1967.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
32 FR 4001,
3/11/1967.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
55 FR 39858,
9/28/1990.
58 FR 14248,
3/16/1993;
50 CFR
17.95(b).CH
Owl, northern
spotted
55 FR 26114,
6/26/1990;
50 CFR
17.95(b).CH
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
60 FR 2899,
1/12/1995.
32 FR 4001,
3/11/1967;
50 CFR
17.95(b).CH
Strix occidentalis caurina
Wherever found
T
Owl, Seychelles Otus magicus (=insularis)
scops
insularis
Wherever found
E
Owlet, Morden's Otus ireneae
Wherever found
E
Oystercatcher,
Canarian black
Haematopus meadewaldoi
Wherever found
E
Palila
(honeycreeper)
Loxioides bailleui
Wherever found
E
Wherever found
E
73 FR 3146,
1/16/2008.
Wherever found
E
35 FR 8491,
6/2/1970.
Parakeet, Forbes' Cyanoramphus auriceps forbesi Wherever found
E
Parakeet, golden Aratinga guarouba
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Parrot, Bahaman
Amazona leucocephala
or Cuban
Wherever found
E
Parrot, ground
Pezoporus wallicus
Wherever found
E
Parrot, imperial
Amazona imperialis
Wherever found
E
Geopsittacus occidentalis
Wherever found
E
Amazona vittata
Wherever found
E
Amazona rhodocorytha
Wherever found
E
Pionopsitta pileata
Wherever found
E
Amazona arausiaca
Wherever found
E
Paradiseflycatcher,
Eutrichomyias rowleyi
caerulean
Parakeet, bluethroated (=ochre- Pyrrhura cruentata
marked)
Parakeet, goldenPsephotus chrysopterygius
shouldered
Parakeet,
Psittacula echo
Mauritius
Parakeet, Norfolk Cyanoramphus cookii
Island
(=novaezelandiae c.)
Parakeet,
Neophema chrysogaster
orange-bellied
Parakeet,
Psephotus pulcherrimus
paradise
Parrot, night
(=Australian)
Parrot, Puerto
Rican
Parrot, redbrowed
Parrot, redcapped
Parrot, rednecked
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
55 FR 39858,
9/28/1990.
35 FR 18319,
12/2/1970.
35 FR 18319,
12/2/1970.
35 FR 8491,
6/2/1970;
41 FR 24062,
6/14/1976.
38 FR 14678,
6/4/1973.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
32 FR 4001,
3/11/1967.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
44 FR 37124,
6/25/1979.
Parrot, redspectacled
Amazona pretrei pretrei
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Rhynchopsitta pachyrhyncha
Mexico
E
Amazona vinacea
Wherever found
E
Parrot, red-tailed Amazona brasiliensis
Parrot,
Seychelles lesser Coracopsis nigra barklyi
vasa
Parrot, St.
Amazona guildingii
Vincent
Parrot, St. Lucia Amazona versicolor
Parrot, thickbilled
Parrot,
vinaceousbreasted
Parrot, yellowbilled
Amazona collaria
Wherever found
T
Parrotbill, Maui
(Kiwikiu)
Pseudonestor xanthophrys
Wherever found
E
Wherever found
E
Wherever found
T
Wherever found
T
Wherever found
E
Wherever found
T
Penguin, African Spheniscus demersus
Penguin, erectEudyptes sclateri
crested
Penguin,
Eudyptes pachyrhynchus
Fiordland crested
Penguin,
Spheniscus mendiculus
Galapagos
Penguin,
Spheniscus humboldti
Humboldt
Penguin,
southern
rockhopper [New Eudyptes chrysocome
Zealand-Australia
DPS]
Penguin, whiteEudyptula minor albosignata
flippered
Penguin, yellowMegadyptes antipodes
eyed
New Zealand-Australia
DPS, associated with
T
the Campbell Plateau
and Macquarie Island
Wherever found
T
Wherever found
T
Petrel, Chatham Pterodroma axillaris
Wherever found
E
Petrel, Fiji
Pseudobulweria macgillivrayi
Wherever found
E
Petrel,
Galapagos
Pterodroma phaeopygia
Wherever found
T
Petrel, Hawaiian Pterodroma sandwichensis
Wherever found
E
Petrel, Madeira
Wherever found
E
Pterodroma madeira
41 FR 24062,
6/14/1976.
55 FR 39858,
9/28/1990.
60 FR 2899,
1/12/1995.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
78 FR 15624,
3/12/2013;
50 CFR
17.41(c).4d
32 FR 4001,
3/11/1967;
50 CFR
17.95(b).CH
75 FR 59645,
9/28/2010.
75 FR 45497,
8/3/2010.
75 FR 45497,
8/3/2010.
35 FR 8491,
6/2/1970.
75 FR 45497,
8/3/2010.
76 FR 9681,
2/22/2011.
75 FR 45497,
8/3/2010.
75 FR 45497,
8/3/2010.
74 FR 46914,
9/14/2009.
74 FR 46914,
9/14/2009.
75 FR 235,
1/5/2010.
32 FR 4001,
3/11/1967.
60 FR 2899,
1/12/1995.
Petrel, magenta
74 FR 46914,
9/14/2009.
60 FR 2899,
1/12/1995.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
55 FR 39858,
9/28/1990.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 18319,
12/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
Pterodroma magentae
Wherever found
E
Pterodroma aterrima
Wherever found
E
Syrmaticus humaie
Wherever found
E
Tragopan blythii
Wherever found
E
Crossoptilon mantchuricum
Wherever found
E
Tragopan caboti
Wherever found
E
Pheasant, cheer Catreus wallichii
Wherever found
E
Lophophorus lhuysii
Wherever found
E
Lophura edwardsi
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
76 FR 50052,
8/11/2011.
Wherever found
E
41 FR 24062,
6/14/1976.
Columba mayeri
Wherever found
E
Columba inornata wetmorei
Wherever found
E
Columba junoniae
Wherever found
T
Pipile jacutinga
Wherever found
E
Petrel,
Mascarene black
Pheasant, bartailed
Pheasant, Blyth's
tragopan
Pheasant, brown
eared
Pheasant,
Cabot's tragopan
Pheasant,
Chinese monal
Pheasant,
Edward's
Pheasant, Elliot's Syrmaticus ellioti
Pheasant,
Lophura imperialis
imperial
Pheasant,
Syrmaticus mikado
Mikado
Pheasant,
Polyplectron emphanum
Palawan peacock
Pheasant,
Lophophorus sclateri
Sclater's monal
Pheasant,
Lophura swinhoii
Swinhoe's
Pheasant,
Tragopan melanocephalus
western tragopan
Pheasant, white
Crossoptilon crossoptilon
eared
Pigeon, Azores
Columba palumbus azorica
wood
Pigeon, Chatham Hemiphaga novaeseelandiae
Island
chathamensis
Pigeon,
Marquesan
Ducula galeata
imperial
Pigeon, Mindoro
imperial (=zone- Ducula mindorensis
tailed)
Pigeon, pink
Pigeon, Puerto
Rican plain
Pigeon, whitetailed laurel
Piping-guan,
black-fronted
60 FR 2899,
1/12/1995.
35 FR 16047,
10/13/1970.
60 FR 2899,
1/12/1995.
41 FR 24062,
6/14/1976.
Pitta, Gurney's
Pitta gurneyi
Wherever found
E
Pitta, Koch's
Pitta kochi
Wherever found
E
Phytotoma raimondii
Wherever found
E
Thinornis novaeseelandiae
Wherever found
E
Plantcutter,
Peruvian
Plover, New
Zealand shore
73 FR 3146,
1/16/2008.
41 FR 24062,
6/14/1976.
77 FR 43434,
7/24/2012.
35 FR 8491,
6/2/1970.
Plover, piping
[Great Lakes
Charadrius melodus
watershed DPS]
Great Lakes,
watershed in States of
IL, IN, MI, MN, NY, OH, E
PA, and WI and
Canada (Ont.)
50 FR 50726,
12/11/1985;
50 CFR
17.95(b).CH
Plover, piping
[Atlantic Coast
and Northern
Great Plains
populations]
Wherever found,
except those areas
where listed as
endangered
T
50 FR 50726,
12/11/1985;
50 CFR
17.95(b).CH
Pacific Coast
population DPS—
U.S.A. (CA, OR, WA), T
Mexico (within 50 miles
of Pacific coast)
58 FR 12864,
3/5/1993;
50 CFR
17.95(b).CH
Charadrius melodus
Plover, western
snowy [Pacific
Charadrius alexandrinus
Coast population nivosus
DPS]
Pochard,
Aythya innotata
Madagascar
Po`ouli
Melamprosops phaeosoma
(honeycreeper)
Prairie-chicken,
Tympanuchus cupido attwateri
Attwater's greater
Puffleg, blackEriocnemis nigrivestis
breasted
Quail, Merriam's
Cyrtonyx montezumae merriami
Montezuma
Quetzel,
Pharomachrus mocinno
resplendent
Rail, Aukland
Rallus pectoralis muelleri
Island
Rail, California
Rallus longirostris obsoletus
clapper
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Rail, Guam
Rallus owstoni
Wherever found,
except where listed as
E
an experimental
population
Rail, Guam
Rallus owstoni
Rota
XN
Rail, Junín
Laterallus tuerosi
Wherever found
E
60 FR 2899,
1/12/1995.
40 FR 44149,
9/25/1975.
32 FR 4001,
3/11/1967.
75 FR 43844,
7/27/2010.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
35 FR 16047,
10/13/1970.
49 FR 14354,
4/11/1984;
49 FR 33881,
8/27/1984;
54 FR 43966,
10/30/1989.
54 FR 43966,
10/30/1989;
50 CFR
17.84(f).10j
77 FR 43434,
7/24/2012.
Rail, light-footed
Rallus longirostris levipes
clapper
34 FR 5034,
3/8/1969;
35 FR 16047,
10/13/1970.
41 FR 24062,
6/14/1976.
32 FR 4001,
3/11/1967.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
60 FR 2899,
1/12/1995.
U.S.A. only
E
Gallirallus (=Tricholimnas)
sylvestris
Wherever found
E
Rallus longirostris yumanensis
U.S.A. only
E
Rhea (=Pterocnemia) pennata
Wherever found
E
Petroica traversi
Wherever found
E
Arcanator orostruthus
Wherever found
T
Petroica multicolor multicolor
Wherever found
E
Picathartes oreas
Wherever found
E
Picathartes gymnocephalus
Wherever found
E
Uratelornis chimaera
Wherever found
E
Centrocercus minimus
Wherever found
T
Scrub-bird, noisy Atrichornis clamosus
Wherever found
E
Scrub-jay, Florida Aphelocoma coerulescens
Wherever found
T
Copsychus niger cebuensis
Wherever found
E
Puffinus heinrothi
Wherever found
T
Puffinus auricularis newelli
Wherever found
T
40 FR 44149,
9/25/1975.
Lanius ludovicianus mearnsi
Wherever found
E
42 FR 40682,
8/11/1977.
Siskin, red
Carduelis cucullata
Wherever found
E
Sparrow, Cape
Sable seaside
Ammodramus maritimus
mirabilis
Wherever found
E
Sparrow, Florida
grasshopper
Sparrow, San
Clemente sage
Sparrowhawk,
Anjouan Island
Ammodramus savannarum
floridanus
Wherever found
E
Amphispiza belli clementeae
Wherever found
T
Accipiter francesii pusillus
Wherever found
E
Rail, Lord Howe
wood
Rail, Yuma
clapper
Rhea, lesser
(incl. Darwin's)
Robin, Chatham
Island
Robin, dappled
mountain
Robin, scarletbreasted
(flycatcher)
Rockfowl, greynecked
Rockfowl, whitenecked
Roller, long-tailed
ground
Sage-grouse,
Gunnison
Shama, Cebu
black (thrush)
Shearwater,
Heinroth's
Shearwater,
Newell's
Townsend's
Shrike, San
Clemente
loggerhead
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
79 FR 69191,
11/20/2014;
50 CFR
17.95(b).CH
35 FR 8491,
6/2/1970.
52 FR 20715,
6/3/1987.
35 FR 8491,
6/2/1970.
75 FR 235,
1/5/2010.
41 FR 24062,
6/14/1976.
32 FR 4001,
3/11/1967;
50 CFR
17.95(b).CH
51 FR 27492,
7/31/1986.
42 FR 40682,
8/11/1977.
35 FR 8491,
6/2/1970.
Starling, Ponape
Aplonis pelzelni
mountain
Starling,
Rothschild's
Leucopsar rothschildi
(myna)
Wherever found
E
35 FR 8491,
6/2/1970.
Wherever found
E
35 FR 8491,
6/2/1970.
Stilt, black
Himantopus novaezelandiae
Wherever found
E
Stilt, Hawaiian
Himantopus mexicanus
(=himantopus) knudseni
Wherever found
E
Stork, oriental
white
Ciconia boyciana (=ciconia b.)
Wherever found
E
Stork, wood
[Southeast U.S.
DPS]
Mycteria americana
U.S.A. (AL, FL, GA,
MS, NC, SC)
T
Storm-petrel,
band-rumped
(Hawaii DPS)
Oceanodroma castro
U.S.A. (HI)
E
Wherever found
E
Aerodramus vanikorensis
bartschi
Wherever found
E
Nemosia rourei
Wherever found
E
Anas aucklandica nesiotis
Wherever found
E
Sterna antillarum browni
Wherever found
E
Sunbird, Marungu Nectarinia prigoginei
Swiftlet, Mariana
gray
Tanager, cherrythroated
Teal, Campbell
Island flightless
Tern, California
least
Tern, least
[Interior DPS]
Sterna antillarum
Tern, roseate
[Northeast U.S.
Sterna dougallii dougallii
nesting
population DPS]
Tern, roseate
[Western
Hemisphere
DPS]
Sterna dougallii dougallii
Thicketbird, longTrichocichla rufa
legged
Thrasher, whiteRamphocinclus brachyurus
breasted
Thrush, large
Myadestes myadestinus
Kauai
U.S.A. (AR, CO, IA, IL,
IN, KS, KY, LA—Miss.
R. and tribs. N of Baton
Rouge, MS—Miss. R.,
E
MO, MT, ND, NE, NM,
OK, SD, TN, TX—
except within 50 miles
of coast)
U.S.A. (Atlantic Coast
south to NC), Canada
E
(Newf., N.S, Que.),
Bermuda
Western Hemisphere
and adjacent oceans,
incl. U.S.A. (FL, PR,
T
VI), where not listed as
endangered
Wherever found
E
Wherever found
E
Wherever found
E
73 FR 3146,
1/16/2008.
35 FR 16047,
10/13/1970.
35 FR 8491,
6/2/1970.
49 FR 7332,
2/28/1984;
79 FR 37077,
6/30/2014.
81 FR 67786,
9/30/2016.
60 FR 2899,
1/12/1995.
49 FR 33881,
8/27/1984.
75 FR 81794,
12/28/2010.
41 FR 24062,
6/14/1976.
35 FR 16047,
10/13/1970;
35 FR 8491,
6/2/1970.
50 FR 21784,
5/28/1985.
52 FR 42064,
11/2/1987.
52 FR 42064,
11/2/1987.
73 FR 3146,
1/16/2008.
35 FR 8491,
6/2/1970.
35 FR 16047,
10/13/1970.
Wherever found
E
35 FR 16047,
10/13/1970.
Turnagra capensis
Wherever found
E
35 FR 8491,
6/2/1970.
Myadestes palmeri
Wherever found
E
Cichlherminia lherminieri
sanctaeluciae
Wherever found
E
Turdus olivaceous helleri
Wherever found
E
Wherever found
E
Leptasthenura xenothorax
Wherever found
E
Anairetes alpinus
Wherever found
E
Hemitriccus kaempferi
Wherever found
E
Pipilo crissalis eremophilus
Wherever found
T
Camarhynchus pauper
Wherever found
E
Cinclocerthia ruficauda
gutturalis
Wherever found
E
Tauraco bannermani
Wherever found
E
Streptopelia picturata rostrata
Wherever found
E
Vanga, Pollen's
Xenopirostris polleni
Wherever found
T
Vanga, Van
Dam's
Xenopirostris damii
Wherever found
T
Vireo, least Bell's Vireo bellii pusillus
Wherever found
E
Wherever found
E
38 FR 14678,
6/4/1973.
Wherever found
E
60 FR 2899,
1/12/1995.
Thrush, Molokai Myadestes lanaiensis rutha
Thrush, New
Zealand
(wattlebird)
Thrush, small
Kauai
Thrush, St. Lucia
forest
Thrush, Taita
Tinamou, solitary Tinamus solitarius
Tit-spinetail,
white-browed
Tit-tyrant, ashbreasted
Tody-tyrant,
Kaempfer's
Towhee, Inyo
California
Tree-finch,
medium
Trembler,
Martinique
(thrasher)
Turaco,
Bannerman's
Turtle-dove,
Seychelles
Wanderer, plain
(collaredPedionomous torquatus
hemipode)
Warbler, Aldabra
(old world
Nesillas aldabranus
warbler)
Warbler (wood),
Vermivora bachmanii
Bachman's
Wherever found
E
Warbler (wood),
Dendroica petechia petechia
Barbados yellow
Wherever found
E
32 FR 4001,
3/11/1967.
75 FR 50814,
8/17/2010.
60 FR 2899,
1/12/1995.
41 FR 24062,
6/14/1976.
77 FR 43434,
7/24/2012.
77 FR 43434,
7/24/2012.
75 FR 81794,
12/28/2010.
52 FR 28780,
8/3/1987;
50 CFR
17.95(b).CH
75 FR 43853,
7/27/2010.
35 FR 8491,
6/2/1970.
60 FR 2899,
1/12/1995.
60 FR 2899,
1/12/1995.
60 FR 2899,
1/12/1995.
60 FR 2899,
1/12/1995.
51 FR 16474,
5/2/1986;
50 CFR
17.95(b).CH
32 FR 4001,
3/11/1967;
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
Warbler, elfinwoods
Setophaga angelae
Wherever found
T
Wherever found
E
Acrocephalus percernis
aquilonis
Wherever found
E
Acrocephalus luscinia
Wherever found
E
Bebrornis rodericanus
Wherever found
E
35 FR 8491,
6/2/1970.
Leucopeza semperi
Wherever found
E
35 FR 8491,
6/2/1970.
Bebrornis sechellensis
Wherever found
E
35 FR 8491,
6/2/1970.
Platysteira laticincta
Wherever found
E
Wherever found
E
Psophodes nigrogularis
Wherever found
E
Zosterops conspicillatus
conspicillatus
Wherever found
E
Zosterops albogularis
Wherever found
E
Rukia longirostra
Wherever found
E
Wherever found
E
Zosterops modesta
Wherever found
E
Campephilus imperialis
Wherever found
E
Campephilus principalis
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Warbler (wood),
Dendroica chrysoparia
golden-cheeked
Warbler, Eiao
Marquesas reedWarbler,
nightingale reed,
(old world
warbler)
Warbler,
Rodrigues (old
world warbler)
Warbler (wood),
Semper's
Warbler,
Seychelles (old
world warbler)
Wattle-eye,
banded
Weaver, Clarke's Ploceus golandi
Whipbird,
western
White-eye,
bridled
White-eye,
Norfolk Island
White-eye,
Ponape greater
White-eye, Rota
Zosterops rotensis
bridled
White-eye,
Seychelles
Woodpecker,
imperial
Woodpecker,
ivory-billed
81 FR 40534,
6/22/2016;
50 CFR
17.41(e).4d
55 FR 18844,
5/4/1990;
55 FR 53153,
12/27/1990.
76 FR 50052,
8/11/2011.
35 FR 8491,
6/2/1970;
35 FR 18319,
12/2/1970.
Woodpecker, redPicoides borealis
cockaded
Woodpecker,
Dryocopus javensis richardsi
Tristam's
Wood-quail,
Odontophorus strophium
gorgeted
60 FR 2899,
1/12/1995.
60 FR 2899,
1/12/1995.
35 FR 8491,
6/2/1970.
49 FR 33881,
8/27/1984.
41 FR 24062,
6/14/1976.
35 FR 8491,
6/2/1970.
69 FR 3022,
1/22/2004;
50 CFR
17.95(b).CH
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
32 FR 4001,
3/11/1967;
35 FR 8491,
6/2/1970.
35 FR 16047,
10/13/1970.
35 FR 8491,
6/2/1970.
78 FR 64637,
10/29/2013.
Woodstar,
Chilean
Woodstar,
Esmeraldas
Wren,
Guadeloupe
house
Wren, St. Lucia
house
75 FR 50814,
8/17/2010.
78 FR 64637,
10/29/2013.
Eulidia yarrellii
Wherever found
E
Chaetocercus berlepschi
Wherever found
E
Troglodytes aedon
guadeloupensis
Wherever found
E
35 FR 8491,
6/2/1970.
Troglodytes aedon mesoleucus Wherever found
E
35 FR 8491,
6/2/1970.
Reptiles
Alligator,
American
Alligator mississippiensis
Wherever found
Alligator, Chinese Alligator sinensis
Wherever found
Anole, Culebra
Island giant
Anolis roosevelti
Wherever found
Boa, Jamaican
Epicrates subflavus
Wherever found
Boa, Mona
Epicrates monensis monensis
Wherever found
Boa, Puerto
Epicrates inornatus
Rican
Boa, Round
Bolyeria multocarinata
Island (unnamed)
Boa, Round
Casarea dussumieri
Island (unnamed)
Boa, Virgin
Islands tree
Epicrates monensis granti
Wherever found
Wherever found
Wherever found
Wherever found
32 FR 4001,
3/11/1967;
40 FR 44412,
9/26/1975;
42 FR 2071,
1/10/1977;
44 FR 37130,
6/25/1979;
44 FR 59080,
10/12/1979;
T(S/A)
46 FR 40664,
8/10/1981;
48 FR 46332,
10/12/1983;
50 FR 25672,
6/20/1985;
52 FR 21059,
6/4/1987;
50 CFR
17.42(a).4d
41 FR 24062,
E
6/14/1976.
42 FR 37371,
7/21/1977;
E
50 CFR
17.95(c).CH
35 FR 8491,
E
6/2/1970.
43 FR 4618,
2/3/1978;
T
50 CFR
17.95(c).CH
35 FR 16047,
E
10/13/1970.
45 FR 18009,
E
3/20/1980.
45 FR 18009,
E
3/20/1980.
35 FR 16047,
10/13/1970;
E
44 FR 70677,
12/7/1979.
Caiman, Apaporis
Caiman crocodilus apaporiensis Wherever found
River
E
Caiman, black
Wherever found
E
Bolivia, Brazil,
Paraguay, Uruguay
E
Melanosuchus niger
Caiman, broadsnouted [Bolivia,
Caiman latirostris
Brazil, Paraguay,
Uruguay DPS]
Caiman, broadsnouted
Caiman latirostris
[Argentina DPS]
Caiman, brown
Caiman crocodilus
fuscus (includes Caiman
crocodilus chiapasius )
Argentina
Wherever found
Caiman, common Caiman crocodilus crocodilus
Wherever found
Caiman, yacare
Wherever found
Caiman yacare
Chuckwalla, San
Sauromalus varius
Wherever found
Esteban Island
Crocodile, African
Osteolaemus tetraspis tetraspis Wherever found
dwarf
Crocodile, African
Crocodylus cataphractus
Wherever found
slender-snouted
Crocodile,
American [Non- Crocodylus acutus
U.S. populations]
Wherever found,
except in U.S.A. (FL)
Crocodile,
American [FL
DPS]
U.S.A. (FL)
Crocodylus acutus
Crocodile, Ceylon
Crocodylus palustris kimbula
mugger
Crocodile, Congo
Osteolaemus tetraspis osborni
dwarf
Wherever found
Wherever found
Crocodile, Cuban Crocodylus rhombifer
Wherever found
Crocodile,
mugger
Wherever found
Crocodylus palustris palustris
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
78 FR 38162,
6/25/2013;
T
50 CFR
17.42(c).4d
65 FR 25867,
5/4/2000;
T(S/A)
50 CFR
17.42(c).4d
65 FR 25867,
5/4/2000;
T(S/A)
50 CFR
17.42(c).4d
35 FR 8491,
6/2/1970;
65 FR 25867,
T
5/4/2000;
50 CFR
17.42(c).4d
45 FR 18009,
E
3/20/1980.
41 FR 24062,
E
6/14/1976.
37 FR 6476,
E
3/30/1972.
40 FR 44149,
9/25/1975;
44 FR 75074,
E
12/18/1979;
72 FR 13027,
3/20/2007.
40 FR 44149,
9/25/1975;
72 FR 13027,
T
3/20/2007;
50 CFR
17.95(c).CH
41 FR 24062,
E
6/14/1976.
41 FR 24062,
E
6/14/1976.
35 FR 8491,
E
6/2/1970.
41 FR 24062,
E
6/14/1976.
Crocodile, Nile
Crocodile,
Orinoco
Crocodile,
Philippine
Crocodile,
saltwater [All
populations
except Papua
New Guinea and
Australia]
Crocodile,
saltwater
[Australia DPS]
Crocodylus niloticus
Wherever found
T
Crocodylus intermedius
Wherever found
E
Crocodylus novaeguineae
mindorensis
Wherever found
E
Crocodylus porosus
Wherever found,
except Papua New
Guinea and Australia
E
Crocodylus porosus
Australia
T
Crocodylus siamensis
Wherever found
E
Thamnophis rufipunctatus
Wherever found
T
Gartersnake,
Thamnophis eques megalops
northern Mexican
Wherever found
T
Gavial
Gavialis gangeticus
Wherever found
E
Gecko, day
Phelsuma edwardnewtoni
Wherever found
E
Phelsuma guentheri
Wherever found
E
Cyrtodactylus serpensinsula
Wherever found
T
Cyclura rileyi nuchalis
Wherever found
T
Cyclura cychlura inornata
Wherever found
T
Cyclura cychlura cychlura
Wherever found
T
Cyclura pinguis
Wherever found
E
Crocodile,
Siamese
Gartersnake,
narrow-headed
Gecko, Round
Island day
Gecko, Serpent
Island
Iguana, Acklins
ground
Iguana, Allen's
Cay
Iguana, Andros
Island ground
Iguana, Anegada
ground
35 FR 8491,
6/2/1970;
52 FR 23148,
6/17/1987;
53 FR 38451,
9/30/1988;
58 FR 49870,
9/23/1993;
61 FR 32356,
6/24/1996;
50 CFR
17.42(c).4d
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
44 FR 75074,
12/18/1979;
61 FR 32356,
6/24/1996.
44 FR 75074,
12/18/1979;
61 FR 32356,
6/24/1996;
50 CFR
17.42(c).4d
41 FR 24062,
6/4/1976.
79 FR 38677,
7/8/2014.
79 FR 38677,
7/8/2014;
50 CFR
17.42(g).4d
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
48 FR 28460,
6/22/1983.
48 FR 28460,
6/22/1983.
48 FR 28460,
6/22/1983.
48 FR 28460,
6/22/1983.
35 FR 8491,
6/2/1970.
Iguana,
Conolophus pallidus
Barrington land
Iguana, Cayman
Cyclura nubila caymanensis
Brac ground
Wherever found
E
Wherever found
T
Cyclura nubila nubila
Wherever found
(exluding population
introduced in Puerto
Rico)
T
Cyclura cychlura figginsi
Wherever found
T
Brachylophus fasciatus
Wherever found
E
Brachylophus vitiensis
Wherever found
E
Cyclura lewisi
Wherever found
E
Iguana, Jamaican Cyclura collei
Wherever found
E
Iguana,
Mayaguana
Cyclura carinata bartschi
Wherever found
T
Iguana, Mona
ground
Cyclura stejnegeri
Wherever found
T
Cyclura carinata carinata
Wherever found
T
Cyclura rileyi rileyi
Wherever found
E
Cyclura rileyi cristata
Wherever found
T
Gambelia silus
Wherever found
E
Lizard, Coachella
Uma inornata
Valley fringe-toed
Wherever found
T
Lizard, Hierro
giant
Wherever found
E
Lizard, Ibiza wall Podarcis pityusensis
Wherever found
T
Lizard, Maria
Island ground
Wherever found
E
Lizard, St. Croix
Ameiva polops
ground
Wherever found
E
Monitor, desert
Wherever found
E
Wherever found
E
Wherever found
E
Iguana, Cuban
ground
Iguana, Exuma
Island
Iguana, Fiji
banded
Iguana, Fiji
crested
Iguana, Grand
Cayman blue
Iguana, Turks
and Caicos
Iguana, Watling
Island ground
Iguana, White
Cay ground
Lizard, bluntnosed leopard
Gallotia simonyi simonyi
Cnemidophorus vanzoi
Varanus griseus
Monitor, Indian
Varanus bengalensis
(=Bengal)
Monitor, Komodo
Varanus komodoensis
Island
35 FR 8491,
6/2/1970.
48 FR 28460,
6/22/1983.
48 FR 28460,
6/22/1983.
48 FR 28460,
6/22/1983.
45 FR 18009,
3/20/1980.
45 FR 18009,
3/20/1980.
48 FR 28460,
6/22/1983.
48 FR 28460,
6/22/1983.
48 FR 28460,
6/22/1983.
43 FR 4618,
2/3/1978;
50 CFR
17.95(c).CH
48 FR 28460,
6/22/1983.
48 FR 28460,
6/22/1983.
48 FR 28460,
6/22/1983.
32 FR 4001,
3/11/1967.
45 FR 63812,
9/25/1980;
50 CFR
17.95(c).CH
49 FR 7394,
2/29/1984.
49 FR 7394,
2/29/1984.
56 FR 49469,
9/30/1991.
42 FR 28543,
6/3/1977;
50 CFR
17.95(c).CH
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
Monitor, yellow
Wherever found
E
Pinesnake, black Pituophis melanoleucus lodingi Wherever found
T
Pinesnake,
Louisiana
Pituophis ruthveni
Wherever found
T
Python, Indian
Python molurus molurus
Wherever found
E
Crotalus unicolor
Wherever found
T
Sistrurus catenatus
Wherever found
T
Rattlesnake,
Aruba Island
Rattlesnake,
eastern
massasauga
Varanus flavescens
Rattlesnake, New
Mexican ridgeCrotalus willardi obscurus
nosed
Wherever found
T
Sea snake, dusky Aipysurus fuscus
Wherever found
E
Sea turtle, green
[Central North
Chelonia mydas
Pacific DPS]
Sea turtle, green
[Central South
Chelonia mydas
Pacific DPS]
Green sea turtles
originating from the
Central North Pacific
Ocean, bounded by the
following coordinates:
41° N., 169° E. in the
northwest; 41° N., 143° T
W. in the northeast; 9°
N., 125° W. in the
southeast; and 9° N.,
175° W. in the
southwest Pacific coast
of Mexico
Green sea turtles
originating from the
Central South Pacific
Ocean, bounded by the
following coordinates:
9° N., 175° W. in the
northwest; 9° N., 125° E
W. in the northeast; 40°
S., 96° W. in the
southeast; 40° S., 176°
E. in the southwest;
and 13° S., 171° E. in
the west
41 FR 24062,
6/14/1976.
80 FR 60467,
10/6/2015;
50 CFR
17.42(h).4d
83 FR 14958,
April 6, 2018.
41 FR 24062,
6/14/1976.
48 FR 28460,
6/22/1983.
81 FR 67193,
9/30/2016.
43 FR 34476,
8/4/1978;
50 CFR
17.95(c).CH
80 FR 60560,
10/7/2015;N 81
FR 76311,
11/2/2016.
81 FR 20057,
4/6/2016;J
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207.
81 FR 20057,
4/6/2016;J
50 CFR 224.104.
Sea turtle, green
[Central West
Chelonia mydas
Pacific DPS]
Sea turtle, green
[East Indian—
Chelonia mydas
West Pacific
DPS]
Sea turtle, green
[East Pacific
Chelonia mydas
DPS]
Sea turtle, green
[Mediterranean Chelonia mydas
DPS]
Green sea turtles
originating from the
Central West Pacific
Ocean, bounded by the
following coordinates:
41° N., 146° E. in the
northwest; 41° N., 169°
E. in the northeast; 9° E
N., 175° W. in the east;
13° S., 171° E. in the
southeast; along the
northern coast of the
island of New Guinea;
and 4.5° N., 129° E. in
the west
Green sea turtles
originating from the
Eastern Indian and
Western Pacific
Oceans, bounded by
the following lines and
coordinates: 41° N.
Lat. in the north, 41°
N., 146° E. in the
northeast; 4.5° N., 129° T
E. in the southeast;
along the southern
coast of the island of
New Guinea; along the
western coast of
Australia (west of 142°
E. Long.); 40° S. Lat. in
the south; and 84° E.
Long. in the east
Green sea turtles
originating from the
East Pacific Ocean,
bounded by the
following lines and
coordinates: 41° N.,
143° W. in the
T
northwest; 41° N. Lat.
in the north; along the
western coasts of the
Americas; 40° S. Lat.
in the south; and 40°
S., 96° W. in the
southwest
Green sea turtles
originating from the
Mediterranean Sea,
E
bounded by 5.5° W.
Long. in the west
81 FR 20057,
4/6/2016;J
50 CFR 224.104.
81 FR 20057,
4/6/2016;J
50 CFR
17.42(b);4d
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207.
81 FR 20057,
4/6/2016;J
50 CFR
17.42(b);4d
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207.
81 FR 20057,
4/6/2016;J
50 CFR 224.104.
Sea turtle, green
[North Atlantic
Chelonia mydas
DPS]
Sea turtle, green
[North Indian
Chelonia mydas
DPS]
Sea turtle, green
[South Atlantic
Chelonia mydas
DPS]
Green sea turtles
originating from the
North Atlantic Ocean,
bounded by the
following lines and
coordinates: 48° N.
Lat. in the north, along
the western coasts of
Europe and Africa
(west of 5.5° W. Long.); T
north of 19° N. Lat. in
the east; bounded by
19° N., 65.1° W. to 14°
N., 65.1° W. then 14°
N., 77° W. in the south
and west; and along
the eastern coasts of
the Americas (north of
7.5° N., 77° W.)
Green sea turtles
originating from the
North Indian Ocean,
bounded by: Africa and
T
Asia in the west and
north; 84° E. Long. in
the east; and the
equator in the south
Green sea turtles
originating from the
South Atlantic Ocean,
bounded by the
following lines and
coordinates: along the
northern and eastern
coasts of South
America (east of 7.5° T
N., 77° W.); 14° N., 77°
W. to 14° N., 65.1° W.
to 19° N., 65.1° W. in
the north and west; 19°
N. Lat. in the northeast;
40° S., 19° E. in the
southeast; and 40° S.
Lat. in the south
81 FR 20057,
4/6/2016;J
50 CFR
17.42(b);4d
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207.
81 FR 20057,
4/6/2016;J
50 CFR
17.42(b);4d
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207.
81 FR 20057,
4/6/2016;J
50 CFR
17.42(b);4d
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207.
Sea turtle, green
[Southwest Indian Chelonia mydas
DPS]
Sea turtle, green
[Southwest
Chelonia mydas
Pacific DPS]
Green sea turtles
originating from the
Southwest Indian
Ocean, bounded by the
following lines: the
equator to the north;
T
84° E. Long. to the
east; 40° S. Lat. to the
south; and 19° E. Long
(and along the eastern
coast of Africa) in the
west
Green sea turtles
originating from the
Southwest Pacific
Ocean, bounded by the
following lines and
coordinates: along the
southern coast of the
island of New Guinea T
and the Torres Strait
(east of 142° E Long.);
13° S., 171° E. in the
northeast; 40° S., 176°
E. in the southeast;
and 40° S., 142° E. in
the southwest
Sea turtle,
hawksbill
Eretmochelys imbricata
Wherever found
E
Sea turtle,
Kemp's ridley
Lepidochelys kempii
Wherever found
E
Sea turtle,
leatherback
Dermochelys coriacea
Wherever found
E
Caretta caretta
Mediterranean Sea
DPS—Loggerhead sea
turtles originating from E
the Mediterranean Sea
east of 5°36′ W. Long
Sea turtle,
loggerhead
[Mediterranean
Sea DPS]
81 FR 20057,
4/6/2016;J
50 CFR
17.42(b);4d
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207.
81 FR 20057,
4/6/2016;J
50 CFR
17.42(b);4d
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207.
35 FR 8491,
6/2/1970;J
50 CFR
224.104;4d
50 CFR
17.95(c);CH
50 CFR
226.209.CH
35 FR 18319,
12/2/1970;J
50 CFR
224.104.4d
35 FR 8491,
6/2/1970;J
50 CFR
224.104;4d
50 CFR
17.95(c);CH
50 CFR
226.207.CH
76 FR 58868,
9/22/2011;J
50 CFR
224.104.4d
Sea turtle,
loggerhead
[North Indian
Ocean DPS]
Sea turtle,
loggerhead
[North Pacific
Ocean DPS]
Sea turtle,
loggerhead
[Northeast
Atlantic Ocean
DPS]
Sea turtle,
loggerhead
[Northwest
Atlantic Ocean
DPS]
Sea turtle,
loggerhead
[South Atlantic
Ocean DPS]
Sea turtle,
loggerhead
[South Pacific
Ocean DPS]
Caretta caretta
Caretta caretta
Caretta caretta
Caretta caretta
Caretta caretta
Caretta caretta
North Indian Ocean
DPS—Loggerhead sea
turtles originating from
E
the North Indian Ocean
north of the equator
and south of 30° N. Lat
North Pacific Ocean
DPS—Loggerhead sea
turtles originating from
E
the North Pacific north
of the equator and
south of 60° N. Lat
Northeast Atlantic
Ocean DPS—
Loggerhead sea turtles
originating from the
Northeast Atlantic
Ocean north of the
equator, south of 60° E
N. Lat., and east of 40°
W. Long., except in the
vicinity of the Strait of
Gibraltar where the
eastern boundary is
5°36′ W. Long
Northwest Atlantic
Ocean DPS—
Loggerhead sea turtles
originating from the
Northwest Atlantic
T
Ocean north of the
equator, south of 60°
N. Lat., and west of 40°
W. Long.
South Atlantic Ocean
DPS—Loggerhead sea
turtles originating from
the South Atlantic
Ocean south of the
T
equator, north of 60° S.
Lat., west of 20° E.
Long., and east of 67°
W. Long
South Pacific Ocean
DPS—Loggerhead sea
turtles originating from
the South Pacific south
E
of the equator, north of
60° S. Lat., west of 67°
W. Long., and east of
141° E. Long
76 FR 58868,
9/22/2011;J
50 CFR
224.104.4d
76 FR 58868,
9/22/2011;J
50 CFR
224.104.4d
76 FR 58868,
9/22/2011;J
50 CFR
224.104.4d
76 FR 58868,
9/22/2011;J
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207;
50 CFR
17.95(c);CH
50 CFR
226.223.CH
76 FR 58868,
9/22/2011;J
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207.
76 FR 58868,
9/22/2011;J
50 CFR
224.104.4d
Sea turtle,
loggerhead
[Southeast Indo- Caretta caretta
Pacific Ocean
DPS]
Sea turtle,
loggerhead
Caretta caretta
[Southwest Indian
Ocean DPS]
Sea turtle, olive
ridley [Pacific
coast of Mexico
breeding DPS]
Southeast Indo-Pacific
Ocean DPS—
Loggerhead sea turtles
originating from the
Southeast Indian
Ocean south of the
equator, north of 60° S. T
Lat., and east of 80° E.
Long.; South Pacific
Ocean south of the
equator, north of 60° S.
Lat., and west of 141°
E. Long
Southwest Indian
Ocean DPS—
Loggerhead sea turtles
originating from the
Southwest Indian
T
Ocean north of the
equator, south of 30°
N. Lat., east of 20° E.
Long., and west of 80°
E. Long
76 FR 58868,
9/22/2011;J
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207.
76 FR 58868,
9/22/2011;J
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207.
43 FR 32800,
7/28/1978;J
50 CFR
224.104.4d
43 FR 32800,
7/28/1978;J
50 CFR
17.42(b);4d
50 CFR 223.205;
50 CFR 223.206;
50 CFR 223.207.
52 FR 42658,
11/6/1987;
50 CFR
17.42(b).4d
48 FR 28460,
6/22/1983.
52 FR 42658,
11/6/1987;
50 CFR
17.42(b).4d
Lepidochelys olivacea
Breeding colony
populations on Pacific E
coast of Mexico
Sea turtle, olive
ridley
Lepidochelys olivacea
Wherever found except
when listed as
T
endangered under 50
CFR 224.101
Skink, blue-tail
mole
Eumeces egregius lividus
Wherever found
T
Skink, Round
Island
Leiolopisma telfairi
Wherever found
T
Skink, sand
Neoseps reynoldsi
Wherever found
T
Wherever found
E
80 FR 59423,
10/1/2015.
Wherever found
T
42 FR 60743,
11/29/1977.
Skink, Slevin's
(Gualiik
Emoia slevini
halumtanu,
Gholuuf)
Snake, Atlantic
Nerodia clarkii taeniata
salt marsh
Snake,
copperbelly water Nerodia erythrogaster neglecta
[Northern DPS]
U.S.A. (IN north of 40°
T
N. Lat., MI, OH)
62 FR 4183,
1/29/1997.
Snake, eastern
indigo
Snake, giant
garter
Snake, Maria
Island
Snake, San
Francisco garter
43 FR 4026,
1/31/1978.
58 FR 54053,
10/20/1993.
56 FR 49469,
9/30/1991.
32 FR 4001,
3/11/1967.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
44 FR 23062,
4/17/1979.
45 FR 55654,
8/20/1980;
54 FR 32326,
8/4/1989;
55 FR 12178,
4/2/1990;
50 CFR
17.95(c).CH
Drymarchon corais couperi
Wherever found
T
Thamnophis gigas
Wherever found
T
Liophus ornatus
Wherever found
E
Thamnophis sirtalis tetrataenia Wherever found
E
Tartaruga
Podocnemis expansa
Wherever found
E
Terrapin, river
Batagur baska
Wherever found
E
Tomistoma
Tomistoma schlegelii
Wherever found
E
Tortoise,
angulated
Geochelone yniphora
Wherever found
E
Tortoise, Bolson Gopherus flavomarginatus
Wherever found
E
Tortoise, desert
[Mojave DPS]
Gopherus agassizii
Wherever found,
except AZ south and
east of Colorado R.,
and Mexico
T
Tortoise, desert
Gopherus agassizii
AZ south and east of
Colorado R., and
Mexico, when found
outside of Mexico or
said range in AZ
55 FR 12178,
4/2/1990;
T(S/A)
50 CFR
17.42(e).4d
Tortoise,
Galapagos
Tortoise, gopher
[West of Mobile
and Tombigbee
Rivers DPS]
Tortoise,
Madagascar
radiated
Geochelone nigra
(=elephantopus)
Wherever found
E
35 FR 8491,
6/2/1970.
Gopherus polyphemus
Wherever found west
of Mobile and
Tombigbee Rivers in
AL, MS, and LA
T
52 FR 25376,
7/7/1987.
Geochelone radiata
Wherever found
E
35 FR 8491,
6/2/1970.
Tracaja
Podocnemis unifilis
Wherever found
E
Tuatara
Sphenodon punctatus
Wherever found
E
Tuatara, Brother's
Sphenodon guntheri
Island
Wherever found
E
Turtle, Alabama
redbellied
Wherever found
E
Pseudemys alabamensis
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970;
65 FR 16053,
3/24/2000.
35 FR 8491,
6/2/1970;
65 FR 16053,
3/24/2000.
52 FR 22939,
6/16/1987.
Turtle, aquatic
box
Turtle, black
softshell
Turtle, bog
(=Muhlenberg)
[Northen DPS]
Turtle, bog
(=Muhlenberg)
Terrapene coahuila
Wherever found
E
Trionyx nigricans
Wherever found
E
Clemmys muhlenbergii
Wherever found,
except GA, NC, SC,
TN, VA
T
Clemmys muhlenbergii
U.S.A. (GA, NC, SC,
TN, VA)
Turtle, Brazilian
Phrynops hogei
sideneck
Turtle, Burmese
Morenia ocellata
peacock
Turtle, Cat Island Trachemys terrapen
Turtle, Central
American river
Turtle, Cuatro
Cienegas
softshell
Turtle, flattened
musk [Black
Warrior River
DPS]
Wherever found
Wherever found
Cat Island in the
Bahamas
62 FR 59605,
11/4/1997;
T(S/A)
50 CFR
17.42(f).4d
56 FR 49469,
E
9/30/1991.
41 FR 24062,
E
6/14/1976.
56 FR 49469,
E
9/30/1991.
48 FR 28460,
E
6/22/1983.
Wherever found
Trionyx ater
Wherever found
E
41 FR 24062,
6/14/1976.
Sternotherus depressus
Black Warrior R.
system upstream from T
Bankhead Dam
52 FR 22418,
6/11/1987.
Wherever found
E
Trachemys stejnegeri malonei
Wherever found
E
Kachuga tecta tecta
Wherever found
E
Trionyx gangeticus
Wherever found
E
Trionyx hurum
Wherever found
E
Turtle, Plymouth
Pseudemys rubriventris bangsi Wherever found
redbelly
E
Turtle, ringed
map
Turtle, shortnecked or
western swamp
Turtle, Sonoyta
mud
Turtle, South
American redlined
Turtle, spotted
pond
62 FR 59605,
11/4/1997.
Dermatemys mawii
Turtle, geometric Psammobates geometricus
Turtle, Inagua
Island
Turtle, Indian
sawback
Turtle, Indian
softshell
Turtle, peacock
softshell
38 FR 14678,
6/4/1973.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
56 FR 49469,
9/30/1991.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
41 FR 24062,
6/14/1976.
45 FR 21828,
4/2/1980;
50 CFR
17.95(c).CH
51 FR 45907,
12/23/1986.
Graptemys oculifera
Wherever found
T
Pseudemydura umbrina
Wherever found
E
35 FR 8491,
6/2/1970.
Kinosternon
sonoriense longifemorale
Wherever found
E
82 FR 43897,
9/20/2017.
Trachemys scripta callirostris
Wherever found
E
56 FR 49469,
9/30/1991.
Geoclemys hamiltonii
Wherever found
E
41 FR 24062,
6/14/1976.
Turtle, threekeeled Asian
Turtle, yellowblotched map
Melanochelys tricarinata
Wherever found
E
Graptemys flavimaculata
Wherever found
T
Viper, Lar Valley Vipera latifii
Wherever found
E
Whipsnake,
Alameda
(=striped racer)
Wherever found
T
Masticophis lateralis
euryxanthus
41 FR 24062,
6/14/1976.
56 FR 1459,
1/14/1991.
48 FR 28460,
6/22/1983.
62 FR 64306,
12/5/1997;
50 CFR
17.95(c).CH
Amphibians
Coqui, golden
Eleutherodactylus jasperi
Wherever found
T
Coqui, llanero
Eleutherodactylus juanariveroi
Wherever found
E
Frog, California
red-legged
Rana draytonii
Wherever found
T
Frog, Chiricahua
Rana chiricahuensis
leopard
Wherever found
T
Frog, dusky
gopher
Rana sevosa (= Lithobates
sevosus)
Wherever found
E
Frog, Goliath
Conraua goliath
Wherever found
T
Discoglossus nigriventer
Wherever found
E
Rana muscosa
Northern California
DPS—U.S.A., northern E
California
Rana muscosa
Southern California
DPS—U.S.A., southern E
California
Frog, Oregon
spotted
Rana pretiosa
Wherever found
T
Frog,
Panamanian
golden
Atelopus varius zeteki
Wherever found
E
Frog, Israel
painted
Frog, mountain
yellow-legged
[Northern
California DPS]
Frog, mountain
yellow-legged
[Southern
California DPS]
42 FR 58756,
11/11/1977;
50 CFR
17.95(d).CH
77 FR 60777,
10/4/2012;
50 CFR
17.95(d).CH
61 FR 25813,
5/23/1996;
50 CFR
17.43(b);4d
50 CFR
17.95(d).CH
67 FR 40790,
6/13/2002;
50 CFR
17.43(b).4d
66 FR 63002,
12/4/2001;
50 CFR
17.95(d).CH
59 FR 63261,
12/8/1994.
35 FR 8491,
6/2/1970.
79 FR 24255,
4/29/2014;
50 CFR
17.95(d).CH
67 FR 44382,
7/2/2002;
50 CFR
17.95(d).CH
79 FR 51657,
8/29/2014;
50 CFR
17.95(d).CH
41 FR 24062,
6/14/1976.
Frog, Sierra
Nevada yellowlegged
Rana sierrae
Wherever found
E
Frog, Stephen
Island
Leiopelma hamiltoni
Wherever found
E
Guajón
Eleutherodactylus cooki
Wherever found
T
Hellbender,
Ozark
Cryptobranchus alleganiensis
bishopi
Wherever found
E
Salamander,
Austin blind
Eurycea waterlooensis
Wherever found
E
Salamander,
Barton Springs
Eurycea sosorum
Wherever found
E
Salamander,
California tiger
[Santa Barbara
County DPS]
Ambystoma californiense
Santa Barbara County
DPS—U.S.A. (CAE
Santa Barbara County)
Salamander,
California tiger
[Central
California DPS]
Ambystoma californiense
Central California DPS
—U.S.A. (CA-Central T
California)
Salamander,
California tiger
Ambystoma californiense
[Sonoma County
DPS]
Sonoma County DPS
—U.S.A. (CA-Sonoma E
County)
Salamander,
Cheat Mountain
Salamander,
Chinese giant
Salamander,
desert slender
Plethodon nettingi
Wherever found
T
Andrias davidianus (=davidianus
Wherever found
d.)
E
Batrachoseps aridus
Wherever found
E
Salamander,
Ambystoma cingulatum
frosted flatwoods
Wherever found
T
Salamander,
Georgetown
Eurycea naufragia
Wherever found
T
Salamander,
Japanese giant
Andrias japonicus (=davidianus
Wherever found
j.)
E
79 FR 24255,
4/29/2014;
50 CFR
17.95(d).CH
35 FR 8491,
6/2/1970.
62 FR 31757,
6/11/1997;
50 CFR
17.95(d).CH
76 FR 61956,
10/6/2011.
78 FR 51277,
8/20/2013;
50 CFR
17.95(d).CH
62 FR 23377,
4/30/1997.
65 FR 3109,
1/19/2000;
65 FR 57242,
9/21/2000;
50 CFR
17.95(d).CH
69 FR 47248,
8/4/2004;
50 CFR
17.43(c);4d
50 CFR
17.95(d).CH
67 FR 47739,
7/22/2002;
68 FR 13520,
3/19/2003;
50 CFR
17.95(d).CH
54 FR 34464,
8/18/1989.
41 FR 24062,
6/14/1976.
38 FR 14678,
6/4/1973.
64 FR 15691,
4/1/1999;
50 CFR
17.95(d).CH
79 FR 20107,
4/11/2014;
50 CFR
17.43(e).4d
41 FR 24062,
6/14/1976.
Salamander,
Plethodon neomexicanus
Jemez Mountains
Wherever found
E
Salamander,
Eurycea tonkawae
Jollyville Plateau
Wherever found
T
Salamander, Red
Phaeognathus hubrichti
Hills
Wherever found
T
Salamander,
reticulated
flatwoods
Ambystoma bishopi
Wherever found
E
Salamander,
Salado
Eurycea chisholmensis
Wherever found
T
Wherever found
T
Ambystoma macrodactylum
croceum
Wherever found
E
Plethodon shenandoah
Wherever found
E
Ambystoma tigrinum stebbinsi
Wherever found
E
Typhlomolge rathbuni
Wherever found
E
Anaxyrus californicus
Wherever found
E
Toad, Cameroon Bufo superciliaris
Wherever found
E
Toad, Houston
Bufo houstonensis
Wherever found
E
Bufo periglenes
Wherever found
E
Peltophryne lemur
Wherever found
T
Toad, Wyoming
Bufo hemiophrys baxteri
Wherever found
E
Toad, Yosemite
Anaxyrus canorus
Wherever found
T
Toads, African
viviparous
Nectophrynoidesspp.
Wherever found
E
Salamander, San
Eurycea nana
Marcos
Salamander,
Santa Cruz longtoed
Salamander,
Shenandoah
Salamander,
Sonoran tiger
Salamander,
Texas blind
Toad, arroyo
(=arroyo
southwestern)
Toad, Monte
Verde golden
Toad, Puerto
Rican crested
78 FR 55599,
9/10/2013;
50 CFR
17.95(d).CH
78 FR 51277,
8/20/2013;
50 CFR
17.95(d).CH
41 FR 53032,
12/3/1976.
74 FR 6700,
2/10/2009;
50 CFR
17.95(d).CH
79 FR 20107,
4/11/2014.
45 FR 47355,
7/14/1980;
50 CFR
17.43(a);4d
50 CFR
17.95(d).CH
32 FR 4001,
3/11/1967.
54 FR 34464,
8/18/1989.
62 FR 665,
1/6/1997.
32 FR 4001,
3/11/1967.
59 FR 64859,
12/16/1994;
50 CFR
17.95(d).CH
41 FR 24062,
6/14/1976.
35 FR 16047,
10/13/1970;
50 CFR
17.95(d).CH
41 FR 24062,
6/14/1976.
52 FR 28828,
8/4/1987.
49 FR 1992,
1/17/1984.
79 FR 24255,
4/29/2014;
50 CFR
17.95(d).CH
41 FR 24062,
6/14/1976.
Waterdog, Black
Necturus alabamensis
Warrior
Wherever found
E
83 FR 257,
1/3/2018.
Fishes
Ala Balik (trout)
Salmo platycephalus
Wherever found
E
Angelshark,
Argentine
Squatina argentina
Wherever found
E
Angelshark,
common
Squatina squatina
Wherever found
E
Angelshark,
sawback
Squatina aculeata
Wherever found
E
Angelshark,
smoothback
Squatina oculata
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Angelshark, spiny Squatina guggenheim
Ayumodoki
Hymenophysa curta
(loach)
Blindcat, Mexican
Prietella phreatophila
(catfish)
Bocaccio [Puget
Sound-Georgia Sebastes paucispinis
Basin DPS]
Puget Sound-Georgia
Basin DPS—see 50
E
CFR 224.101
Bonytongue,
Asian
Scleropages formosus
Wherever found
E
Cardinalfish,
Banggai
Pterapogon kauderni
Wherever found
T
Catfish (Thailand) Pangasius sanitwongsei
Wherever found
E
Catfish, Thailand
Pangasianodon gigas
giant
Wherever found
E
Catfish, Yaqui
Wherever found
T
Ictalurus pricei
35 FR 8491,
6/2/1970.
82 FR 21722,
5/10/2017;N 84
FR 13809,
4/8/2019.
81 FR 50394,
8/1/2016;N 81 FR
76311, 11/2/2016.
81 FR 50394,
8/1/2016;N 81 FR
76311, 11/2/2016.
81 FR 50394,
8/1/2016;N 81 FR
76311, 11/2/2016.
82 FR 21722,
5/10/2017;N 84
FR 13809,
4/8/2019.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
75 FR 22276,
4/28/2010;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.224.CH
41 FR 24062,
6/14/1976.
81 FR 3023,
1/20/2016;N 81
FR 76311,
11/2/2016.
35 FR 8491,
6/2/1970.
35 FR 8491,
6/2/1970.
49 FR 34490,
8/31/1984;
50 CFR
17.44(h);4d
50 CFR
17.95(e).CH
Cavefish,
Alabama
Wherever found
E
Cavefish, Ozark Amblyopsis rosae
Wherever found
T
Chub, bonytail
Gila elegans
Wherever found
E
Chub, Borax
Lake
Gila boraxobius
Wherever found
E
Chub, Chihuahua Gila nigrescens
Wherever found
T
Chub, Gila
Wherever found
E
Chub, humpback Gila cypha
Wherever found
E
Chub, Hutton tui Gila bicolor ssp.
Wherever found
T
Chub, Mohave tui Gila bicolor mohavensis
Wherever found
E
Chub, Owens tui Gila bicolor snyderi
Wherever found
E
Chub,
Pahranagat
roundtail
Wherever found
E
35 FR 16047,
10/13/1970.
Erimystax cahni
Wherever found,
except where listed as
T
an experimental
population
42 FR 45526,
9/9/1977;
50 CFR
17.44(c);4d
50 CFR
17.95(e).CH
Erimystax cahni
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.84(s)
(1)(i))
72 FR 52434,
9/13/2007;
50 CFR
17.84(sr).10j
Chub, slender
Chub, slender
Speoplatyrhinus poulsoni
42 FR 45526,
9/9/1977;
53 FR 37968,
9/28/1988;
50 CFR
17.95(e).CH
49 FR 43965,
11/1/1984.
45 FR 27710,
4/23/1980;
50 CFR
17.95(e).CH
45 FR 35821,
5/28/1980;
47 FR 43957,
10/5/1982;
50 CFR
17.95(e).CH
48 FR 46053,
10/11/1983;
50 CFR
17.44(g).4d
70 FR 66664,
11/2/2005;
50 CFR
17.95(e).CH
32 FR 4001,
3/11/1967;
50 CFR
17.95(e).CH
50 FR 12302,
3/28/1985;
50 CFR 17.44(j).4d
35 FR 16047,
10/13/1970.
50 FR 31592,
8/5/1985;
50 CFR
17.95(e).CH
Gila intermedia
Gila robusta jordani
Chub, Sonora
Chub, spotfin
Gila ditaenia
Wherever found
Erimonax monachus
Wherever found,
except where listed as
T
an experimental
population
Chub, spotfin
Erimonax monachus
Chub, spotfin
Erimonax monachus
Chub, spotfin
Erimonax monachus
T
U.S.A. (TN—specified
portions of the Tellico
XN
River; see
§17.84(m) (1)(i))
U.S.A. (AL, TN—
specified portions of
XN
Shoal Creek; see
§17.84(m)(1)(ii))
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.84(m)
(1)(iii))
Chub, Virgin
River
Gila robusta semidnuda
Wherever found
E
Chub, Yaqui
Gila purpurea
Wherever found
E
Cicek (minnow)
Acanthorutilus handlirschi
Wherever found
E
Coelacanth,
African
Latimeria chalumnae
[Tanzanian DPS]
Tanzanian DPS—see
T
50 CFR 223.102
Cui-ui
Chasmistes cujus
Wherever found
E
Dace, Ash
Meadows
speckled
Rhinichthys osculus nevadensis Wherever found
E
Dace, blackside
Phoxinus
Wherever found
(=Chrosomus), cumberlandensis
T
Dace, Clover
Valley speckled
Rhinichthys osculus oligoporus Wherever found
E
51 FR 16042,
4/30/1986;
50 CFR
17.44(o);4d
50 CFR
17.95(e).CH
42 FR 45526,
9/9/1977;
50 CFR
17.44(c);4d
50 CFR
17.95(e).CH
67 FR 52420,
8/12/2002;
50 CFR
17.84(m).10j
70 FR 1286,
1/6/2005;
50 CFR
17.84(m).10j
72 FR 52434,
9/13/2007;
50 CFR
17.84(m).10j
54 FR 35305,
8/24/1989;
50 CFR
17.95(e).CH
49 FR 34490,
8/31/1984;
50 CFR
17.95(e).CH
35 FR 8491,
6/2/1970.
81 FR 17398,
3/29/2016;N 81
FR 76311,
11/2/2016.
32 FR 4001,
3/11/1967.
47 FR 19995,
5/10/1982;
48 FR 608,
1/5/1983;
48 FR 40178,
9/2/1983;
50 CFR
17.95(e).CH
52 FR 22580,
6/12/1987.
54 FR 41448,
10/10/1989.
Dace, desert
Eremichthys acros
Wherever found
T
Dace,
Independence
Valley speckled
Rhinichthys osculus lethoporus Wherever found
E
Dace, Kendall
Warm Springs
Rhinichthys osculus thermalis
Wherever found
E
Dace, laurel
Chrosomus saylori
Wherever found
E
Dace, Moapa
Moapa coriacea
Wherever found
E
Darter, amber
Percina antesella
Wherever found
E
Darter, bayou
Etheostoma rubrum
Wherever found
T
Darter, bluemask Etheostoma akatulo
Wherever found
E
Darter, boulder
Etheostoma wapiti
Darter, boulder
Etheostoma wapiti
Darter, candy
Etheostoma osburni
Wherever found,
except where listed as
E
an experimental
population
Shoal Creek (from
Shoal Creek mile 41.7
(66.7 km)) at the mouth
of Long Branch,
Lawrence County, TN,
downstream to the
backwaters of Wilson
Reservoir (Shoal Creek XN
mile 14 (22 km)) at
Goose Shoals,
Lauderdale County, AL,
including the lower 5
miles (8 km) of all
tributaries that enter
this reach
Wherever found
E
32 FR 4001,
3/11/1967;
35 FR 16047,
10/13/1970;
50 FR 50304,
12/10/1985;
50 CFR
17.44(m);4d
50 CFR
17.95(e);CH
54 FR 41448,
10/10//1989;
54 FR 47861,
11/17/1989.
35 FR 16047,
10/13/1970.
76 FR 48722,
8/9/2011;
50 CFR
17.95(e).CH
32 FR 4001,
3/11/1967.
50 FR 31597,
8/5/1985;
50 CFR
17.95(e).CH
40 FR 44149,
9/25/1975;
50 CFR
17.44(b).4d
58 FR 68480,
12/27/1993.
53 FR 33996,
9/1/1988.
70 FR 1286,
1/6/2005;
50 CFR
17.84(o).10j
83 FR 58747,
11/21/2018.
Darter, Cherokee Etheostoma scotti
Wherever found
T
Darter,
Cumberland
Wherever found
E
Wherever found
E
Etheostoma susanae
Darter, diamond Crystallaria cincotta
Darter, duskytail Etheostoma percnurum
Darter, duskytail Etheostoma percnurum
Darter, duskytail Etheostoma percnurum
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (TN—specified
portions of the Tellico
XN
River; see §17.84(p)(1)
(i))
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.84(q)
(1)(ii))
Darter, Etowah
Etheostoma etowahae
Wherever found
E
Darter, fountain
Etheostoma fonticola
Wherever found
E
Darter, goldline
Percina aurolineata
Wherever found
T
Darter, Kentucky
Etheostoma spilotum
arrow
Wherever found
T
Darter, leopard
Percina pantherina
Wherever found
T
Darter, Maryland Etheostoma sellare
Wherever found
E
Darter, Niangua
Wherever found
T
Etheostoma nianguae
59 FR 65505,
12/20/1994.
76 FR 48722,
8/9/2011;
50 CFR
17.95(e).CH
78 FR 45074,
7/26/2013;
50 CFR
17.95(e).CH
58 FR 25758,
4/27/1993.
67 FR 52420,
8/12/2002;
50 CFR
17.84(q).10j
72 FR 52434,
9/13/2007;
50 CFR
17.84(q).10j
59 FR 65505,
12/20/1994.
35 FR 16047,
10/13/1970;
50 CFR
17.95(e).CH
57 FR 14786,
4/22/1992.
81 FR 68963,
10/5/2016;
50 CFR
17.44(p);4d
50 CFR
17.95(e).CH
43 FR 3711,
1/27/1978;
50 CFR
17.44(d);4d
50 CFR
17.95(e).CH
32 FR 4001,
3/11/1967;
50 CFR
17.95(e).CH
50 FR 24649,
6/12/1985;
50 CFR
17.44(k);4d
50 CFR
17.95(e).CH
Darter, Okaloosa Etheostoma okaloosae
Wherever found
T
Darter, Pearl
Percina aurora
Wherever found
T
Darter, relict
Etheostoma chienense
Wherever found
E
Darter, rush
Etheostoma phytophilum
Wherever found
E
Darter,
slackwater
Etheostoma boschungi
Wherever found
T
Darter, snail
Percina tanasi
Wherever found
T
Darter, trispot
Etheostoma trisella
Wherever found
T
Darter, vermilion Etheostoma chermocki
Wherever found
E
Darter,
watercress
Etheostoma nuchale
Wherever found
E
Darter,
yellowcheek
Etheostoma moorei
Wherever found
E
Eulachon
[Southern DPS]
Thaleichthys pacificus
Southern DPS—see 50
T
CFR 223.102
Gambusia, Big
Gambusia gaigei
Bend
Gambusia, Clear
Gambusia heterochir
Creek
Gambusia, Pecos Gambusia nobilis
Wherever found
E
Wherever found
E
Wherever found
E
38 FR 14678,
6/4/1973;
76 FR 18087,
4/1/2011;
50 CFR
17.44(bb).4d
82 FR 43885,
9/20/2017.
58 FR 68480,
12/27/1993.
76 FR 48722,
8/9/2011;
50 CFR
17.95(e).CH
42 FR 45526,
9/9/1977;
50 CFR
17.44(c);4d
50 CFR
17.95(e).CH
40 FR 47505,
10/9/1975;
49 FR 27510,
7/5/1984.
83 FR 67131,
12/28/2018.
66 FR 59367,
11/28/2001;
50 CFR
17.95(e).CH
35 FR 16047,
10/13/1970.
76 FR 48722,
8/9/2011;
50 CFR
17.95(e).CH
75 FR 13012,
3/18/2010;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.222.CH
32 FR 4001,
3/11/1967.
32 FR 4001,
3/11/1967.
35 FR 16047,
10/13/1970.
Gambusia, San
Marcos
Gambusia georgei
Wherever found
E
Goby, tidewater
Eucyclogobius newberryi
Wherever found
E
Grouper, gulf
Mycteroperca jordani
Wherever found
E
Grouper, island
Mycteroperca fusca
Wherever found
T
Grouper, Nassau Epinephelus striatus
Wherever found
T
Guitarfish,
blackchin
Rhinobatos cemciculus
Wherever found
T
Guitarfish,
Brazilian
Rhinobatos horkelii
Wherever found
E
Guitarfish,
common
Rhinobatos rhinobatos
Wherever found
T
Logperch,
Conasauga
Percina jenkinsi
Wherever found
E
Logperch,
Roanoke
Percina rex
Wherever found
E
Madtom, Chucky Noturus crypticus
Wherever found
E
Madtom, Neosho Noturus placidus
Wherever found
T
Madtom, pygmy Noturus stanauli
Madtom, pygmy Noturus stanauli
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.84(t)
(1)(i))
45 FR 47355,
7/14/1980;
50 CFR
17.95(e).CH
59 FR 5494,
2/4/1994;
50 CFR
17.95(e).CH
81 FR 72545,
10/20/2016;N 84
FR 13809,
4/8/2019.
81 FR 72545,
10/20/2016;N 84
FR 13809,
4/8/2019.
81 FR 42268,
6/29/2016;N 81
FR 76311,
11/2/2016.
82 FR 6309,
1/19/2017;N 84
FR 13809,
4/8/2019.
82 FR 21722,
5/10/2017;N 84
FR 13809,
4/8/2019.
82 FR 6309,
1/19/2017;N 84
FR 13809,
4/8/2019.
50 FR 31597,
8/5/1985;
50 CFR
17.95(e).CH
54 FR 34468,
8/18/1989.
76 FR 48722,
8/9/2011;
50 CFR
17.95(e).CH
55 FR 21148,
5/22/1990.
58 FR 25758,
4/27/1993.
72 FR 52434,
9/13/2007;
50 CFR
17.84(t).10j
Madtom, Scioto
Noturus trautmani
Madtom, smoky
Noturus baileyi
Madtom, smoky
Noturus baileyi
Madtom,
yellowfin
Madtom,
yellowfin
Madtom,
yellowfin
Madtom,
yellowfin
Noturus flavipinnis
Noturus flavipinnis
Noturus flavipinnis
Noturus flavipinnis
Wherever found
E
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (TN—specified
portions of the Tellico
XN
River; see §17.84(r)(1)
(i))
Wherever found,
except where listed as
T
an experimental
population
U.S.A. (TN, VA—
specified portions of
the Holston River and XN
watershed; see
§17.84(e)(1)(i))
U.S.A. (TN—specified
portions of the Tellico
XN
River; see §17.84(e)(1)
(ii))
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.84(e)
(1)(iii))
Minnow, Devils
River
Dionda diaboli
Wherever found
T
Minnow, loach
Rhinichthys cobitis
Wherever found
E
Hybognathus amarus
Wherever found,
except where listed as
E
an experimental
population
Minnow, Rio
Grande silvery
40 FR 44149,
9/25/1975.
49 FR 43065,
10/26/1984;
50 CFR
17.95(e).CH
67 FR 52420,
8/12/2002;
50 CFR
17.84(r).10j
42 FR 45526,
9/9/1977;
50 CFR
17.44(c);4d
50 CFR
17.95(e).CH
53 FR 29335,
8/4/1988;
50 CFR
17.84(e).10j
67 FR 52420,
8/12/2002;
50 CFR
17.84(e).10j
72 FR 52434,
9/13/2007;
50 CFR
17.84(e).10j
64 FR 56596,
10/20/1999;
50 CFR
17.95(e).CH
51 FR 39468,
10/28/1986;
77 FR 10810,
2/23/2012;
50 CFR
17.95(e).CH
59 FR 36988,
7/20/1994;
50 CFR
17.95(e).CH
Minnow, Rio
Grande silvery
Hybognathus amarus
Rio Grande, from Little
Box Canyon
(approximately 10.4
river miles downstream
of Fort Quitman, TX) to
Amistad Dam; and on XN
the Pecos River, from
its confluence with
Independence Creek to
its confluence with the
Rio Grande
Nekogigi (catfish) Coreobagrus ichikawai
Wherever found
E
Pikeminnow,
Colorado
Ptychocheilus lucius
Wherever found,
except where listed as
E
an experimental
population
Pikeminnow,
Colorado
Ptychocheilus lucius
Salt and Verde R.
drainages, AZ
XN
Poolfish,
Pahrump
Empetrichthys latos
Wherever found
E
Pupfish, Ash
Meadows
Amargosa
Cyprinodon nevadensis
mionectes
Wherever found
E
Pupfish,
Comanche
Springs
Cyprinodon elegans
Wherever found
E
Pupfish, desert
Cyprinodon macularius
Wherever found
E
Pupfish, Devils
Hole
Cyprinodon diabolis
Wherever found
E
Pupfish, Leon
Springs
Cyprinodon bovinus
Wherever found
E
Pupfish, Owens
Cyprinodon radiosus
Wherever found
E
Pupfish, Warm
Springs
Cyprinodon nevadensis
pectoralis
Wherever found
E
73 FR 74357,
12/8/2008;
50 CFR
17.84(u).10j
35 FR 8491,
6/2/1970.
32 FR 4001,
3/11/1967;
50 FR 30188,
7/24/1985;
50 CFR
17.95(e).CH
50 FR 30188,
7/24/1985;
50 CFR
17.84(b).10j
32 FR 4001,
3/11/1967.
47 FR 19995,
5/10/1982;
48 FR 608,
1/5/1983;
48 FR 40178,
9/2/1983;
50 CFR
17.95(e).CH
32 FR 4001,
3/11/1967.
51 FR 10842,
3/31/1986;
50 CFR
17.95(e).CH
32 FR 4001,
3/11/1967.
45 FR 54678,
8/15/1980;
50 CFR
17.95(e).CH
32 FR 4001,
3/11/1967.
35 FR 16047,
10/13/1970.
Ray, giant manta Manta birostris
Wherever found
T
Rockfish,
yelloweye [Puget
Sebastes ruberrimus
Sound-Georgia
Basin DPS]
Puget Sound-Georgia
Basin DPS—see 50
T
CFR 223.102
Salmon, Atlantic
[Gulf of Maine
Salmo salar
DPS]
Gulf of Maine DPS—
see 50 CFR 224.101
Salmon, Chinook
[California
Oncorhynchus tshawytscha
Coastal ESU]
California Coastal ESU
T
—see 50 CFR 223.102
Salmon, Chinook
[Central Valley
Oncorhynchus tshawytscha
spring-run ESU]
Central Valley springrun ESU—see 50 CFR T
223.102
E
83 FR 2916,
1/22/2018;N 84
FR 13809,
4/8/2019.
75 FR 22276,
4/28/2010;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.224.CH
65 FR 69459,
11/17/2000;J
74 FR 29344,
6/19/2009;J
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.217.CH
64 FR 50394,
9/16/1999;N
64 FR 72960,
12/29/1999;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.211.CH
64 FR 50394,
9/16/1999;N
64 FR 72960,
12/29/1999;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.211.CH
Salmon, Chinook
[Central Valley
Oncorhynchus tshawytscha
spring-run ESU—
XN]
Central Valley springrun ESU-XN—see 50 XN
CFR 223.102
Salmon, Chinook
[Lower Columbia Oncorhynchus tshawytscha
River ESU]
Lower Columbia River
ESU—see 50 CFR
T
223.102
Salmon, Chinook
[Puget Sound
Oncorhynchus tshawytscha
ESU]
Puget Sound ESU—
see 50 CFR 223.102
T
Salmon, Chinook
[Sacramento
Oncorhynchus tshawytscha
River winter-run
ESU]
Sacramento River
winter-run ESU—see
50 CFR 224.101
E
78 FR 79622,
12/31/2013;N
79 FR 42687,
7/23/2014;
50 CFR
223.301.10j
64 FR 14308,
3/24/1999;N
64 FR 41835,
8/2/1999;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
64 FR 14308,
3/24/1999;N
64 FR 41835,
8/2/1999;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
55 FR 12191,
4/2/1990;N
55 FR 12831,
4/6/1990;
55 FR 46515,
11/4/1990;N
55 FR 49623,
11/30/1990;
59 FR 440,
1/4/1994;N
59 FR 13836,
3/23/1994;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.204.CH
Salmon, Chinook
[Snake River fall- Oncorhynchus tshawytscha
run ESU]
Snake River fall-run
ESU—see 50 CFR
223.102
T
Salmon, Chinook
[Snake River
Oncorhynchus tshawytscha
spring/summerrun ESU]
Snake River
spring/summer-run
ESU—see 50 CFR
223.102
T
Salmon, Chinook
[Upper Columbia
Oncorhynchus tshawytscha
River spring-run
ESU]
Upper Columbia River
spring-run ESU—see E
50 CFR 224.101
Salmon, Chinook
[Upper Columbia
Oncorhynchus tshawytscha
River spring-run
ESU-XN]
Upper Columbia River
spring-run ESU-XN— XN
see 50 CFR 223.102
57 FR 14653,
4/22/1992;N
58 FR 49880,
9/23/1993;
59 FR 42529,
8/18/1994;N
59 FR 54840,
11/2/1994;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.205.CH
57 FR 14653,
4/22/1992;N
58 FR 49880,
9/23/1993;
59 FR 42529,
8/18/1994;N
59 FR 54840,
11/2/1994;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.205.CH
64 FR 14308,
3/24/1999;N
64 FR 41835,
8/2/1999;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.212.CH
79 FR 40004,
7/11/2014;N
79 FR 52576,
9/4/2014;
50 CFR
223.301.10j
Salmon, Chinook
[Upper Willamette Oncorhynchus tshawytscha
River ESU]
Upper Willamette River
ESU—see 50 CFR
T
223.102
Salmon, chum
[Columbia River Oncorhynchus keta
ESU]
Columbia River ESU—
T
see 50 CFR 223.102
Salmon, chum
[Hood Canal
summer-run
ESU]
Hood Canal summerrun ESU—see 50 CFR T
223.102
Oncorhynchus keta
Salmon, coho
[Central
Oncorhynchus kisutch
California Coast
ESU]
Central California
Coast ESU—see 50
CFR 224.101
E
64 FR 14308,
3/24/1999;N
64 FR 41835,
8/2/1999;
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
64 FR 14508,
3/25/1999;N
64 FR 41835,
8/2/1999;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
64 FR 14508,
3/25/1999;N
64 FR 41835,
8/2/1999;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
61 FR 56138,
10/31/1996;N
61 FR 59028,
11/20/1996;
70 FR 37160,
6/28/2005;N
77 FR 19552,
4/2/2012;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.210.CH
Salmon, coho
[Lower Columbia Oncorhynchus kisutch
River ESU]
Lower Columbia River
ESU—see 50 CFR
T
223.102
Salmon, coho
[Oregon Coast
ESU]
Oregon Coast ESU—
T
see 50 CFR 223.102
Oncorhynchus kisutch
Salmon, coho
[Southern
Oregon-Northern Oncorhynchus kisutch
California Coast
ESU]
Southern Oregon—
Northern California
Coast ESU—see 50
CFR 223.102
Salmon, sockeye
[Ozette Lake
Oncorhynchus nerka
ESU]
Ozette Lake ESU—see
T
50 CFR 223.102
T
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
75 FR 29489,
5/26/2010;N
76 FR 20558,
4/13/2011;
76 FR 35755,
6/20/2011;N
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
62 FR 24588,
5/6/1997;N
62 FR 33038,
6/18/1997;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.210.CH
64 FR 14528,
3/25/1999;N
64 FR 41835,
8/2/1999;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
Salmon, sockeye
[Snake River
Oncorhynchus nerka
ESU]
Snake River ESU—see
E
50 CFR 224.101
Sawfish, dwarf
Pristis clavata
Wherever found
E
Sawfish, green
Pristis zijsron
Wherever found
E
Sawfish,
largetooth
Pristis pristis(formerly Pristis
perotteti, Pristis
pristis, and Pristis microdon)
Wherever found
E
Sawfish, narrow Anoxypristis cuspidata
Wherever found
E
Sawfish,
smalltooth [Non- Pristis pectinata
U.S. DPS]
Non-U.S. DPS—
Smalltooth sawfish
originating from nonU.S. waters
E
Sawfish,
smalltooth [U.S.
DPS]
Pristis pectinata
U.S. DPS—Smalltooth
sawfish originating
E
from U.S. waters
Sculpin, grotto
Cottus specus
Wherever found
E
56 FR 58619,
11/20/1991;N
57 FR 212,
1/3/1992;
70 FR 37160,
6/28/2005;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.205.CH
79 FR 73978,
12/12/2014;N
79 FR 3914,
1/26/2015.
79 FR 73978,
12/12/2014;N
79 FR 3914,
1/26/2015.
76 FR 40822,
9/12/2011;N
79 FR 42687,
7/23/2014;
79 FR 73978,
12/12/2014;N
79 FR 3914,
1/26/2015.
79 FR 73978,
12/12/2014;N
79 FR 3914,
1/26/2015.
79 FR 73978,
12/12/2014;N
79 FR 3914,
1/26/2015.
68 FR 15674,
4/1/2003;N
70 FR 69464,
11/16/2005;
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.218.CH
78 FR 58938,
9/25/2013;
50 CFR
17.95(e).CH
Sculpin, pygmy
Cottus pygmaeus
Wherever found
T
Shark,
daggernose
Isogomphodon oxyrhynchus
Wherever found
E
Shark,
narrownose
smoothhound
Mustelus schmitti
Wherever found
T
Shark, oceanic
whitetip
Carcharhinus longimanus
Wherever found
T
Sphyrna lewini
Central & SW Atlantic
DPS—see 50 CFR
T
223.102
Sphyrna lewini
Eastern Atlantic DPS—
E
see 50 CFR 224.101
Sphyrna lewini
Eastern Pacific DPS—
E
see 50 CFR 224.101
Sphyrna lewini
Indo-West Pacific DPS
T
—see 50 CFR 223.102
Mustelus fasciatus
Wherever found
Shark, scalloped
hammerhead
[Central & SW
Atlantic DPS]
Shark, scalloped
hammerhead
[Eastern Atlantic
DPS]
Shark, scalloped
hammerhead
[Eastern Pacific
DPS]
Shark, scalloped
hammerhead
[Indo-West
Pacific DPS]
Shark, striped
smoothhound
E
Shiner, Arkansas
River [Arkansas Notropis girardi
River Basin DPS]
Arkansas River Basin
T
(AR, KS, NM, OK, TX)
Shiner, beautiful Cyprinella formosa
Wherever found
T
Shiner, blue
Cyprinella caerulea
Wherever found
T
Shiner, Cahaba
Notropis cahabae
Wherever found
E
54 FR 39846,
9/28/1989;
50 CFR
17.44(u).4d
82 FR 21722,
5/10/2017;N 84
FR 13809,
4/8/2019.
82 FR 21722,
5/10/2017;N 84
FR 13809,
4/8/2019.
83 FR 4153,
1/30/2018;N 84
FR 13809,
4/8/2019.
79 FR 38214,
7/3/2014;N
79 FR 52576,
9/4/2014.
79 FR 38214,
7/3/2014;N
79 FR 52576,
9/4/2014.
79 FR 38214,
7/3/2014;N
79 FR 52576,
9/4/2014.
79 FR 38214,
7/3/2014;N
79 FR 52576,
9/4/2014.
82 FR 21722,
5/10/2017;N 84
FR 13809,
4/8/2019.
63 FR 64772,
11/23/1998;
50 CFR
17.95(e).CH
49 FR 34490,
8/31/1984;
50 CFR
17.44(h);4d
50 CFR
17.95(e).CH
57 FR 14786,
4/22/1992.
55 FR 42961,
10/25/1990.
Shiner, Cape
Fear
Notropis mekistocholas
Wherever found
E
Shiner, palezone Notropis albizonatus.
Wherever found
E
Shiner, Pecos
bluntnose
Notropis simus pecosensis
Wherever found
T
Shiner,
sharpnose
Notropis oxyrhynchus
Wherever found
E
Wherever found
E
Shiner, smalleye Notropis buccula
Shiner, Topeka
Shiner, Topeka
Notropis topeka
Notropis topeka
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (MO—specified
portions of Little Creek,
Big Muddy Creek, and
Spring Creek
watersheds in Adair, XN
Gentry, Harrison,
Putnam, Sullivan, and
Worth Counties; see
§17.84(d)(1)(i))
Silverside,
Waccamaw
Menidia extensa
Wherever found
T
Smelt, delta
Hypomesus transpacificus
Wherever found
T
Spikedace
Meda fulgida
Wherever found
E
52 FR 36034,
9/25/1987;
50 CFR
17.95(e).CH
58 FR 25758,
4/27/1993.
52 FR 5295,
2/20/1987;
50 CFR
17.44(r);4d
50 CFR
17.95(e).CH
79 FR 45273,
8/4/2014;
50 CFR
17.95(e).CH
79 FR 45273,
8/4/2014;
50 CFR
17.95(e).CH
63 FR 69008,
12/15/1998;
50 CFR
17.95(e).CH
78 FR 42702,
7/17/2013;
50 CFR
17.84(d).10j
52 FR 11277,
4/8/1987;
50 CFR
17.44(s);4d
50 CFR
17.95(e).CH
58 FR 12854,
3/5/1993;
50 CFR
17.95(e).CH
51 FR 23769,
7/1/1986;
77 FR 10810,
2/23/2012;
50 CFR
17.95(e).CH
Spinedace, Big
Spring
Lepidomeda mollispinis
pratensis
Wherever found
T
Spinedace, Little
Lepidomeda vittata
Colorado
Wherever found
T
Spinedace, White
Lepidomeda albivallis
River
Wherever found
E
Springfish, Hiko
White River
Crenichthys baileyi grandis
Wherever found
E
Springfish,
Railroad Valley
Crenichthys nevadae
Wherever found
T
Springfish, White
Crenichthys baileyi baileyi
River
Wherever found
E
Steelhead
[California
Central Valley
DPS]
California Central
Valley DPS—see 50
CFR 223.102
T
Oncorhynchus mykiss
50 FR 12298,
3/28/1985;
50 CFR
17.44(i);4d
50 CFR
17.95(e).CH
32 FR 4001,
3/11/1967;
35 FR 16047,
10/13/1970;
52 FR 35034,
9/16/1987;
50 CFR
17.44(t);4d
50 CFR
17.95(e).CH
50 FR 37194,
9/12/1985;
50 CFR
17.95(e).CH
50 FR 39123,
9/27/1985;
50 CFR
17.95(e).CH
51 FR 10857,
3/31/1986;
50 CFR
17.44(n);4d
50 CFR
17.95(e).CH
50 FR 39123,
9/27/1985;
50 CFR
17.95(e).CH
63 FR 13347,
3/19/1998;N
63 FR 32996,
6/17/1998;
71 FR 834,
1/5/2006;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.211.CH
Steelhead
[Central
Oncorhynchus mykiss
California Coast
DPS]
Central California
Coast DPS—see 50
CFR 223.102
Steelhead [Lower
Columbia River Oncorhynchus mykiss
DPS]
Lower Columbia River
DPS—see 50 CFR
T
223.102
Steelhead
[Middle Columbia Oncorhynchus mykiss
River DPS]
Middle Columbia River
DPS—see 50 CFR
T
223.102
Steelhead
[Middle Columbia Oncorhynchus mykiss
River DPS—XN]
Middle Columbia River
DPS—XN—see 50
XN
CFR 223.102
T
62 FR 43937,
8/18/1997;N
63 FR 32996,
6/17/1998;
71 FR 834,
1/5/2006;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.211.CH
63 FR 13347,
3/19/1998;N
63 FR 32996,
6/17/1998;
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
64 FR 14517,
3/25/1999;N
64 FR 41835,
8/2/1999;
71 FR 834,
1/5/2006;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
78 FR 2893,
1/15/2013;N
79 FR 42687,
7/23/2014;
50 CFR
223.301.10j
Steelhead
[Northern
California DPS]
Northern California
DPS—see 50 CFR
223.102
T
Steelhead [Puget
Oncorhynchus mykiss
Sound DPS]
Puget Sound DPS—
see 50 CFR 223.102
T
Steelhead [Snake
Oncorhynchus mykiss
River Basin DPS]
Snake River Basin
DPS—see 50 CFR
223.102
T
Steelhead [South
Central California Oncorhynchus mykiss
Coast DPS]
South-Central
California Coast DPS T
—see 50 CFR 223.102
Oncorhynchus mykiss
65 FR 36075,
6/7/2000;N
65 FR 54177,
9/7/2000;
71 FR 834,
1/5/2006;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.211.CH
72 FR 26722,
5/11/2007;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
62 FR 43937,
8/18/1997;N
63 FR 32996,
6/17/1998;
71 FR 834,
1/5/2006;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
62 FR 43937,
8/18/1997;N
63 FR 32996,
6/17/1998;
71 FR 834,
1/5/2006;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.211.CH
Steelhead
[Southern
California DPS]
Oncorhynchus mykiss
Southern California
DPS—see 50 CFR
224.101
E
Steelhead [Upper
Columbia River Oncorhynchus mykiss
DPS]
Upper Columbia River
DPS—see 50 CFR
T
223.102
Steelhead [Upper
Willamette River Oncorhynchus mykiss
DPS]
Upper Willamette River
DPS—see 50 CFR
T
223.102
Stickleback,
unarmored
threespine
Wherever found
Gasterosteus aculeatus
williamsoni
E
Sturgeon, Adriatic Acipenser naccarii
Wherever found
E
Sturgeon,
Alabama
Wherever found
E
Scaphirhynchus suttkusi
62 FR 43937,
8/18/1997;N
63 FR 32996,
6/17/1998;
71 FR 834,
1/5/2006;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.211.CH
62 FR 43937,
8/18/1997;N
63 FR 32996,
6/17/1998;
71 FR 834,
1/5/2006;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
64 FR 14517,
3/25/1999;N
64 FR 41835,
8/2/1999;
71 FR 834,
1/5/2006;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
223.203;4d
50 CFR
226.212.CH
35 FR 16047,
10/13/1970.
79 FR 31222,
6/2/2014;N
79 FR 52576,
9/4/2014.
65 FR 26438,
5/5/2000;
50 CFR
17.95(e).CH
Sturgeon, Atlantic
(Atlantic
Acipenser oxyrinchus
subspecies)
oxyrinchus
[Carolina DPS]
Carolina DPS—see 50
E
CFR 224.101
Sturgeon, Atlantic
(Atlantic
Acipenser oxyrinchus
subspecies)
oxyrinchus
[Chesapeake Bay
DPS]
Chesapeake Bay DPS
E
—see 50 CFR 224.101
Sturgeon, Atlantic
(Atlantic
Acipenser oxyrinchus
subspecies)[Gulf oxyrinchus
of Maine DPS]
Gulf of Maine DPS—
see 50 CFR 223.102
Sturgeon, Atlantic
(Atlantic
Acipenser oxyrinchus
subspecies)[New oxyrinchus
York Bight DPS]
New York Bight DPS—
E
see 50 CFR 224.101
Sturgeon, Atlantic
(Atlantic
Acipenser oxyrinchus
subspecies)
oxyrinchus
[South Atlantic
DPS]
South Atlantic DPS—
E
see 50 CFR 224.101
Sturgeon, Atlantic
Acipenser oxyrinchus desotoi
(Gulf subspecies)
Wherever found
T
Sturgeon, beluga Huso huso
Wherever found
T
Sturgeon,
Chinese
Acipenser sinensis
Wherever found
E
Sturgeon,
European
Acipenser sturio
Wherever found
E
T
77 FR 5914,
2/6/2012;N 79 FR
42687, 7/23/2014;
50 CFR
226.225.CH
77 FR 5880,
2/6/2012;N 79 FR
42687, 7/23/2014;
50 CFR
226.225.CH
77 FR 5880,
2/6/2012;N 79 FR
42687, 7/23/2014;
50 CFR
223.211; 4d 50
CFR 226.225.CH
77 FR 5880,
2/6/2012;N 79 FR
42687, 7/23/2014;
50 CFR
226.225.CH
77 FR 5914,
2/6/2012;N 79 FR
42687, 7/23/2014;
50 CFR
226.225.CH
56 FR 49653,
9/30/1991;N
56 FR 49658,
9/30/1991;
50 CFR 17.44;4d
50 CFR
17.95(e);CH
50 CFR
226.214.CH
69 FR 18499,
4/8/2004;
50 CFR
17.44(y).4d
79 FR 31222,
6/2/2014;N
79 FR 52576,
9/4/2014.
79 FR 31222,
6/2/2014;N
79 FR 52576,
9/4/2014.
Sturgeon, green
Acipenser medirostris
[Southern DPS]
Sturgeon, Kaluga Huso dauricus
Sturgeon, pallid
Scaphirhynchus albus
Sturgeon,
Sakhalin
Acipenser mikadoi
Sturgeon,
shortnose
Acipenser brevirostrum
Sturgeon,
shovelnose
Scaphirhynchus platorynchus
Sturgeon, white
[Kootenai River
DPS]
Acipenser transmontanus
Sucker, June
Chasmistes liorus
Sucker, Lost
River
Deltistes luxatus
Sucker,
razorback
Xyrauchen texanus
Sucker, Santa
Ana [Three CA Catostomus santaanae
river basins DPS]
Sucker,
shortnose
Chasmistes brevirostris
71 FR 26835,
5/9/2006;
76 FR 20558,
4/13/2011;
Southern DPS—see 50
79 FR 42687,
T
CFR 223.102
7/23/2014;
50 CFR
223.210;4d
50 CFR
226.219.CH
79 FR 31222,
6/2/2014;N
Wherever found
E
79 FR 52576,
9/4/2014.
55 FR 36641,
Wherever found
E
9/6/1990.
79 FR 31222,
6/2/2014;N
Wherever found
E
79 FR 52576,
9/4/2014.
32 FR 4001,
Wherever found
E
3/11/1967.
75 FR 53598,
T
9/1/2010;
Wherever found
(S/A) 50 CFR
17.44(aa).4d
Kootenai River DPS—
59 FR 45989,
U.S.A. (ID, MT),
9/6/1994;
E
Canada (BC),
50 CFR
(Kootenai R. system)
17.95(e).CH
51 FR 10851,
3/31/1986;
Wherever found
E
50 CFR
17.95(e).CH
53 FR 27130,
7/18/1988;
Wherever found
E
50 CFR
17.95(e).CH
56 FR 54957,
10/23/1991;
Wherever found
E
50 CFR
17.95(e).CH
Los Angeles River
65 FR 19686,
basin, San Gabriel
4/12/2000;
T
River basin, Santa Ana
50 CFR
River basin
17.95(e).CH
53 FR 27130,
7/18/1988;
Wherever found
E
50 CFR
17.95(e).CH
Sucker, Warner
Catostomus warnerensis
Wherever found
T
Sucker, Zuni
bluehead
Catostomus discobolus yarrowi Wherever found
E
Sunfish, spring
pygmy
Elassoma alabamae
Wherever found
T
Wherever found
E
Wherever found
E
Wherever found
E
U.S.A. only
E
Wherever found
E
Wherever found
T
Tango, Miyako
Tanakia tanago
(Tokyo bitterling)
Temoleh, Ikan
Probarbus jullieni
(minnow)
Topminnow,
Fundulus julisia
Barrens
Topminnow, Gila
Poeciliopsis occidentalis
(incl. Yaqui)
Totoaba (seatrout
Cynoscion macdonaldi
or weakfish)
Trout, Apache
Oncorhynchus apache
Trout, bull [Lower
Salvelinus confluentus
48 States DPS]
U.S.A., coterminous
(lower 48 states),
except where listed as T
an experimental
population
Trout, bull
Clackamas River
subbasin and the
mainstem Willamette
River, from Willamette
Falls to its points of
XN
confluence with the
Columbia River,
including Multnomah
Channel
Salvelinus confluentus
50 FR 39117,
9/27/1985;
50 CFR
17.44(l);4d
50 CFR
17.95(e).CH
79 FR 43131,
7/24/2014;
50 CFR
17.95(e).CH
78 FR 60766,
10/2/2013; 50
CFR 17.95(e).CH
35 FR 8491,
6/2/1970.
41 FR 24062,
6/14/1976.
83 FR 56131,
10/21/2019.
32 FR 4001,
3/11/1967.
44 FR 29478,
5/21/1979.
32 FR 4001,
3/11/1967;
40 FR 29863,
7/16/1975;
50 CFR
17.44(a).4d
63 FR 31647,
6/10/1998;
63 FR 42757,
8/11/1998;
64 FR 17110,
4/8/1999;
64 FR 58910,
11/1/1999;
50 CFR
17.44(w);4d
50 CFR
17.44(x);4d
50 CFR
17.95(e).CH
76 FR 35979,
6/21/2011;
50 CFR
17.84(v).10j
Trout, Gila
Oncorhynchus gilae
Wherever found
T
Wherever found
T
Oncorhynchus clarkii henshawi Wherever found
T
Trout, greenback
Oncorhynchus clarkii stomias
cutthroat
Trout, Lahontan
cutthroat
Trout, Little Kern Oncorhynchus aguabonita
golden
whitei
Wherever found
T
Trout, Paiute
cutthroat
Oncorhynchus clarkii seleniris
Wherever found
T
Woundfin
Plagopterus argentissimus
Wherever found,
except where listed as
E
an experimental
population
Woundfin
Plagopterus argentissimus
Gila R. drainage, AZ,
NM
XN
32 FR 4001,
3/11/1967;
71 FR 40657,
7/18/2006;
50 CFR
17.44(z).4d
32 FR 4001,
3/11/1967;
43 FR 16343,
4/18/1978;
50 CFR
17.44(f).4d
35 FR 16047,
10/13/1970;
40 FR 29863,
7/16/1975;
50 CFR
17.44(a).4d
43 FR 15427,
4/13/1978;
50 CFR
17.44(e);4d
50 CFR
17.95(e).CH
32 FR 4001,
3/11/1967;
40 FR 29863,
7/16/1975;
50 CFR
17.44(a).4d
35 FR 16047,
10/13/1970;
50 FR 30188,
7/24/1985;
50 CFR
17.95(e).CH
50 FR 30188,
7/24/1985;
50 CFR
17.84(b).10j
Clams
Acornshell,
southern
Epioblasma othcaloogensis
Wherever found
E
Bankclimber,
purple
Elliptoideus sloatianus
Wherever found
T
Bean, Choctaw
Villosa choctawensis
Wherever found
E
58 FR 14330,
3/17/1993;
50 CFR
17.95(f).CH
63 FR 12664,
3/16/1998;
50 CFR
17.95(f).CH
77 FR 61663,
10/10/2012;
50 CFR
17.95(f).CH
Bean,
Cumberland
Bean,
Cumberland
Bean,
Cumberland
Villosa trabalis
Villosa trabalis
Villosa trabalis
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (AL—specified
portions of the
XN
Tennessee River; see
§17.85(a)(1))
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.85(b)
(1))
Bean, Purple
Villosa perpurpurea
Wherever found
E
Blossom, green
Epioblasma torulosa
gubernaculum
Wherever found
E
Blossom,
tubercled
Epioblasma torulosa torulosa
Blossom,
tubercled
Epioblasma torulosa torulosa
Blossom, turgid
Epioblasma turgidula
Blossom, turgid
Epioblasma turgidula
Blossom, yellow Epioblasma florentina florentina
Blossom, yellow Epioblasma florentina florentina
Purple cat's paw
Epioblasma obliquata obliquata
(pearlymussel)
Purple cat's paw
Epioblasma obliquata obliquata
(pearlymussel)
Catspaw, white
(pearlymussel)
Epioblasma obliquata
perobliqua
Wherever found,
except where listed as
an experimental
population
U.S.A. (AL—specified
portions of the
Tennessee River; see
§17.85(a)(1))
Wherever found,
except where listed as
an experimental
population
U.S.A. (AL—specified
portions of the
Tennessee River; see
§17.85(a)(1))
Wherever found,
except where listed as
an experimental
population
U.S.A. (AL—specified
portions of the
Tennessee River; see
§17.85(a)(1))
Wherever found,
except where listed as
an experimental
population
U.S.A. (AL—specified
portions of the
Tennessee River; see
§17.85(a)(1))
Wherever found
41 FR 24062,
6/14/1976.
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
62 FR 1647,
1/10/1997;
50 CFR
17.95(f).CH
41 FR 24062,
6/14/1976.
E
41 FR 24062,
6/14/1976.
XN
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
E
41 FR 24062,
6/14/1976.
XN
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
E
41 FR 24062,
6/14/1976.
XN
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
E
55 FR 28209,
7/10/1990.
XN
E
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
41 FR 24062,
6/14/1976.
Clubshell
Pleurobema clava
Clubshell
Pleurobema clava
Clubshell, black
Pleurobema curtum
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (AL—specified
portions of the
XN
Tennessee River; see
§17.85(a)(1))
Wherever found
E
Clubshell, ovate Pleurobema perovatum
Wherever found
E
Clubshell,
southern
Wherever found
E
Pleurobema decisum
Combshell,
Cumberlandian
Epioblasma brevidens
Combshell,
Cumberlandian
Epioblasma brevidens
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (AL—specified
portions of the
XN
Tennessee River; see
§17.85(a)(1))
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.85(b)
(1)
Combshell,
Cumberlandian
Epioblasma brevidens
Combshell,
southern
Epioblasma (=Dysnomia) penita Wherever found
E
Combshell,
upland
Epioblasma metastriata
Wherever found
E
Ebonyshell,
round
Fusconaia rotulata
Wherever found
E
Elktoe,
Appalachian
Alasmidonta raveneliana
Wherever found
E
Elktoe,
Cumberland
Alasmidonta atropurpurea
Wherever found
E
Cyprogenia stegaria
Wherever found,
except where listed as
E
an experimental
population
Fanshell
58 FR 5638,
1/22/1993.
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
52 FR 11162,
4/7/1987.
58 FR 14330,
3/17/1993;
50 CFR
17.95(f).CH
58 FR 14330,
3/17/1993;
50 CFR
17.95(f).CH
62 FR 1647,
1/10/1997;
50 CFR
17.95(f).CH
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
52 FR 11162,
4/7/1987.
77 FR 61663,
10/10/2012;
50 CFR
17.95(f).CH
58 FR 14330,
3/17/1993;
50 CFR
17.95(f).CH
59 FR 60324,
11/23/1994;
50 CFR
17.95(f).CH
62 FR 1647,
1/10/1997;
50 CFR
17.95(f).CH
55 FR 25591,
6/21/1990.
Cyprogenia stegaria
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.85(b)
(1))
Lampsilis powelli
Wherever found
T
Potamilus inflatus
Wherever found
T
Heelsplitter,
Carolina
Lasmigona decorata
Wherever found
E
Higgins eye
(pearlymussel)
Lampsilis higginsii
Wherever found
E
Hornshell, Texas Popenaias popeii
Wherever found
E
Kidneyshell,
fluted
Ptychobranchus subtentus
Wherever found
E
Kidneyshell,
southern
Ptychobranchus jonesi
Wherever found
E
Kidneyshell,
triangular
Ptychobranchus greenii
Wherever found
E
Fanshell
Fatmucket,
Arkansas
Heelsplitter,
inflated
Lampmussel,
Alabama
Lampsilis virescens
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (AL—specified
portions of the
XN
Tennessee River; see
§17.85(a)(1))
Lampmussel,
Alabama
Lampsilis virescens
Lance, yellow
Elliptio lanceolata
Wherever found
T
Lilliput, pale
Toxolasma cylindrellus
Wherever found
E
Mapleleaf,
Quadrula fragosa
winged (mussel)
Mapleleaf,
Quadrula fragosa
winged (mussel)
Moccasinshell,
Alabama
Medionidus acutissimus
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (AL—specified
portions of the
XN
Tennessee River; see
§17.85(a)(1))
Wherever found
T
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
55 FR 12797,
4/5/1990.
55 FR 39868,
9/28/1990.
58 FR 34926,
6/30/1993;
50 CFR
17.95(f).CH
41 FR 24062,
6/14/1976.
83 FR 5720,
2/9/2018.
78 FR 59269,
9/26/2013;
50 CFR
17.95(f).CH
77 FR 61663,
10/10/2012;
50 CFR
17.95(f).CH
58 FR 14330,
3/17/1993;
50 CFR
17.95(f).CH
41 FR 24062,
6/14/1976.
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
83 FR 14189,
4/3/2018.
41 FR 24062,
6/14/1976.
56 FR 28345,
6/20/1991.
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
58 FR 14330,
3/17/1993;
50 CFR
17.95(f).CH
Moccasinshell,
Coosa
Medionidus parvulus
Wherever found
E
Moccasinshell,
Gulf
Medionidus penicillatus
Wherever found
E
Moccasinshell,
Ochlockonee
Medionidus simpsonianus
Wherever found
E
Moccasinshell,
Suwannee
Medionidus walkeri
Wherever found
T
Monkeyface,
Appalachian
(pearlymussel)
Quadrula sparsa
Monkeyface,
Appalachian
(pearlymussel)
Quadrula sparsa
Monkeyface,
Cumberland
Quadrula intermedia
Monkeyface,
Cumberland
Monkeyface,
Cumberland
Quadrula intermedia
Quadrula intermedia
Wherever found,
except where listed as
an experimental
population
U.S.A. (TN—specified
portions of the French
Broad and Holston
Rivers; see §17.85(b)
(1))
Wherever found,
except where listed as
an experimental
population
U.S.A. (AL—specified
portions of the
Tennessee River; see
§17.85(a)(1))
U.S.A. (TN—specified
portions of the French
Broad and Holston
Rivers; see §17.85(b)
(1))
E
41 FR 24062,
6/14/1976.
XN
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
E
41 FR 24062,
6/14/1976.
XN
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
XN
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
Mucket, Neosho Lampsilis rafinesqueana
Wherever found
E
Mucket,
orangenacre
Lampsilis perovalis
Wherever found
T
Mucket, pink
(pearlymussel)
Lampsilis abrupta
Wherever found
E
Epioblasma capsaeformis
Wherever found,
except where listed as
E
an experimental
population
Mussel, oyster
58 FR 14330,
3/17/1993;
50 CFR
17.95(f).CH
63 FR 12664,
3/16/1998;
50 CFR
17.95(f).CH
63 FR 12664,
3/16/1998;
50 CFR
17.95(f).CH
81 FR 69417,
10/6/2016.
78 FR 57076,
9/17/2013;
50 CFR
17.95(f).CH
58 FR 14330,
3/17/1993;
50 CFR
17.95(f).CH
41 FR 24062,
6/14/1976.
62 FR 1647,
1/10/1997;
50 CFR
17.95(f).CH
Mussel, oyster
Mussel, oyster
Mussel, rayed
bean
Mussel,
scaleshell
Epioblasma capsaeformis
Epioblasma capsaeformis
U.S.A. (AL—specified
portions of the
XN
Tennessee River; see
§17.85(a)(1))
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.85(b)
(1))
Villosa fabalis
Wherever found
E
Leptodea leptodon
Wherever found
E
Pearlshell,
Alabama
Margaritifera marrianae
Wherever found
E
Pearlshell,
Louisiana
Margaritifera hembeli
Wherever found
T
Pearlymussel,
birdwing
Pearlymussel,
birdwing
Lemiox rimosus
Lemiox rimosus
Pearlymussel,
birdwing
Lemiox rimosus
Pearlymussel,
cracking
Hemistena lata
Pearlymussel,
cracking
Hemistena lata
Wherever found,
except where listed as
an experimental
population
U.S.A. (AL—specified
portions of the
Tennessee River; see
§17.85(a)(1))
U.S.A. (TN—specified
portions of the French
Broad and Holston
Rivers; see §17.85(b)
(1))
Wherever found,
except where listed as
an experimental
population
U.S.A. (AL—specified
portions of the
Tennessee River; see
§17.85(a)(1))
U.S.A. (TN—specified
portions of the French
Broad and Holston
Rivers; see §17.85(b)
(1))
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
77 FR 8632,
2/14/2012.
66 FR 51322,
10/9/2001.
77 FR 61663,
10/10/2012;
50 CFR
17.95(f).CH
53 FR 3567,
2/5/1988;
58 FR 49935,
9/24/1993.
E
41 FR 24062,
6/14/1976.
XN
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
XN
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
E
54 FR 39850,
9/28/1989.
XN
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
XN
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
Pearlymussel,
cracking
Hemistena lata
Pearlymussel,
Curtis
Epioblasma florentina curtisii
Wherever found
E
41 FR 24062,
6/14/1976.
Dromus dromas
Wherever found,
except where listed as
E
an experimental
population
41 FR 24062,
6/14/1976.
Pearlymussel,
dromedary
Pearlymussel,
dromedary
Pearlymussel,
dromedary
Pearlymussel,
littlewing
Pearlymussel,
Nicklin's
Dromus dromas
Dromus dromas
U.S.A. (AL—specified
portions of the
XN
Tennessee River; see
§17.85(a)(1))
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.85(b)
(1))
Pegias fabula
Wherever found
E
Megalonaias nicklineana
Wherever found
E
Pleuronaia dolabelloides
Wherever found
E
Pearlymussel,
Tampico
Pigtoe,
Cumberland
Cyrtonaias tampicoensis
tecomatensis
Wherever found
E
Pleurobema gibberum
Wherever found
E
Pigtoe, dark
Pleurobema furvum
Wherever found
E
Pearlymussel,
slabside
Pigtoe, finerayed Fusconaia cuneolus
Pigtoe, finerayed Fusconaia cuneolus
Pigtoe, finerayed Fusconaia cuneolus
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (AL—specified
portions of the
XN
Tennessee River; see
§17.85(a)(1))
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.85(b)
(1))
Pigtoe, flat
Pleurobema marshalli
Wherever found
E
Pigtoe, fuzzy
Pleurobema strodeanum
Wherever found
T
Pigtoe, Georgia
Pleurobema hanleyianum
Wherever found
E
Pigtoe, heavy
Pleurobema taitianum
Wherever found
E
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
53 FR 45861,
11/14/1988.
41 FR 24062,
6/14/1976.
78 FR 59269,
9/26/2013;
50 CFR
17.95(f).CH
41 FR 24062,
6/14/1976.
56 FR 21084,
5/7/1991.
58 FR 14330,
3/17/1993;
50 CFR
17.95(f).CH
41 FR 24062,
6/14/1976.
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
52 FR 11162,
4/7/1987.
77 FR 61663,
10/10/2012;
50 CFR
17.95(f).CH
75 FR 67512,
11/2/2010;
50 CFR
17.95(f).CH
52 FR 11162,
4/7/1987.
Pigtoe, narrow
Fusconaia escambia
Wherever found
T
Pigtoe, oval
Pleurobema pyriforme
Wherever found
E
Pigtoe, rough
Pleurobema plenum
Pigtoe, rough
Pleurobema plenum
Pigtoe, shiny
Fusconaia cor
Pigtoe, shiny
Pigtoe, shiny
Fusconaia cor
Fusconaia cor
Wherever found,
except where listed as
an experimental
population
U.S.A. (TN—specified
portions of the French
Broad and Holston
Rivers; see §17.85(b)
(1))
Wherever found,
except where listed as
an experimental
population
U.S.A. (AL—specified
portions of the
Tennessee River; see
§17.85(a)(1))
U.S.A. (TN—specified
portions of the French
Broad and Holston
Rivers; see §17.85(b)
(1))
E
41 FR 24062,
6/14/1976.
XN
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
E
41 FR 24062,
6/14/1976.
XN
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
XN
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
Pigtoe, southern Pleurobema georgianum
Wherever found
E
Pigtoe, tapered
Wherever found
T
Pimpleback,
orangefoot
Fusconaia burkei
Plethobasus cooperianus
Pimpleback,
orangefoot
Plethobasus cooperianus
Pink, ring
Obovaria retusa
77 FR 61663,
10/10/2012;
50 CFR
17.95(f).CH
63 FR 12664,
3/16/1998;
50 CFR
17.95(f).CH
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.85(b)
(1))
Wherever found,
except where listed as
E
an experimental
population
58 FR 14330,
3/17/1993;
50 CFR
17.95(f).CH
77 FR 61663,
10/10/2012;
50 CFR
17.95(f).CH
41 FR 24062,
6/14/1976.
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
54 FR 40109,
9/29/1989.
Pink, ring
Obovaria retusa
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.85(b)
(1))
Pocketbook, fat
Potamilus capax
Wherever found
E
Pocketbook,
finelined
Lampsilis altilis
Wherever found
T
Rockpocketbook,
Ouachita
Arkansia wheeleri
Wherever found
E
Pocketbook,
shinyrayed
Lampsilis subangulata
Wherever found
E
Pocketbook,
speckled
Lampsilis streckeri
Wherever found
E
Rabbitsfoot
Quadrula cylindrica cylindrica
Wherever found
T
Rabbitsfoot,
rough
Quadrula cylindrica strigillata
Wherever found
E
Riffleshell,
northern
Epioblasma torulosa rangiana
Wherever found
E
Riffleshell, tan
Epioblasma florentina walkeri
(=E. walkeri)
Wherever found
E
Sandshell,
southern
Hamiota australis
Wherever found
T
Sheepnose
Plethobasus cyphyus
Wherever found
E
Slabshell,
Chipola
Elliptio chipolaensis
Wherever found
T
Snuffbox
(mussel)
Epioblasma triquetra
Wherever found
E
Spectaclecase
Cumberlandia monodonta
Wherever found
E
Spinymussel,
Altamaha
Elliptio spinosa
Wherever found
E
Spinymussel,
James
Pleurobema collina
Wherever found
E
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
41 FR 24062,
6/14/1976.
58 FR 14330,
3/17/1993;
50 CFR
17.95(f).CH
56 FR 54950,
10/23/1991.
63 FR 12664,
3/16/1998;
50 CFR
17.95(f).CH
54 FR 8339,
2/28/1989.
78 FR 57076,
9/17/2013;
50 CFR
17.95(f).CH
62 FR 1647,
1/10/1997;
50 CFR
17.95(f).CH
58 FR 5638,
1/22/1993.
42 FR 42351,
8/23/1977.
77 FR 61663,
10/10/2012;
50 CFR
17.95(f).CH
77 FR 14914,
3/13/2012.
63 FR 12664,
3/16/1998;
50 CFR
17.95(f).CH
77 FR 8632,
2/14/2012.
77 FR 14914,
3/13/2012.
76 FR 62928,
10/11/2011;
50 CFR
17.95(f).CH
53 FR 27689,
7/22/1988.
Spinymussel, Tar
Elliptio steinstansana
River
Wherever found
E
Stirrupshell
Quadrula stapes
Wherever found
E
Threeridge, fat
Amblema neislerii
Wherever found
E
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.85(b)
(1))
Wartyback, white Plethobasus cicatricosus
Wartyback, white Plethobasus cicatricosus
Wedgemussel,
dwarf
Alasmidonta heterodon
Wherever found
E
50 FR 26572,
6/27/1985.
52 FR 11162,
4/7/1987.
63 FR 12664,
3/16/1998;
50 CFR
17.95(f).CH
41 FR 24062,
6/14/1976.
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
55 FR 9447,
3/14/1990.
Snails
Abalone, Black
Haliotis cracherodii
Wherever found
E
Abalone, white
Haliotis sorenseni
Wherever found
E
Ambersnail,
Kanab
Oxyloma haydeni kanabensis
Wherever found
E
Campeloma,
slender
Campeloma decampi
Wherever found
E
Cavesnail,
Tumbling Creek
Antrobia culveri
Wherever found
E
Elimia, lacy
Elimia crenatella
Wherever found
T
Hornsnail, rough Pleurocera foremani
Wherever found
E
Limpet, Banbury
Lanx sp.
Springs
Wherever found
E
74 FR 1937,
1/14/2009;N
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
50 CFR
226.221.CH
66 FR 29054,
5/29/2001;N
70 FR 69464,
11/16/2005.
56 FR 37668,
8/8/1991;
57 FR 13657,
4/17/1992;
57 FR 44340,
9/25/1992.
65 FR 10033,
2/25/2000.
67 FR 52879,
8/14/2002;
50 CFR
17.95(f).CH
63 FR 57610,
10/28/1998.
75 FR 67512,
11/2/2010;
50 CFR
17.95(f).CH
57 FR 59244,
12/14/1992.
Lioplax,
cylindrical
Marstonia,
armored (snail)
Lioplax cyclostomaformis
Wherever found
E
Pyrgulopsis (=Marstonia)
pachyta
Wherever found
E
Marstonia, royal Pyrgulopsis ogmorhaphe
Wherever found
E
Pebblesnail, flat
Wherever found
E
Wherever found
E
Lepyrium showalteri
Pecos assiminea Assiminea pecos
Riversnail,
Anthony's
Riversnail,
Anthony's
Riversnail,
Anthony's
Athearnia anthonyi
Athearnia anthonyi
Athearnia anthonyi
Wherever found,
except where listed as
E
an experimental
population
U.S.A. (AL—specified
portions of the
XN
Tennessee River; see
§17.85(a)(1))
U.S.A. (TN—specified
portions of the French
Broad and Holston
XN
Rivers; see §17.85(b)
(1))
63 FR 57610,
10/28/1998.
65 FR 10033,
2/25/2000.
59 FR 17994,
4/15/1994.
63 FR 57610,
10/28/1998.
76 FR 33036,
6/7/2011;
50 CFR
17.95(f).CH
59 FR 17994,
4/15/1994.
66 FR 32250,
6/14/2001;
50 CFR
17.85(a).10j
72 FR 52434,
9/13/2007;
50 CFR
17.85(b).10j
75 FR 67512,
11/2/2010;
50 CFR
17.95(f).CH
63 FR 57610,
10/28/1998.
63 FR 57610,
10/28/1998.
63 FR 57610,
10/28/1998.
57 FR 59244,
12/14/1992.
Rocksnail,
interrupted
Leptoxis foremani
Wherever found
E
Rocksnail,
painted
Leptoxis taeniata
Wherever found
T
Rocksnail, plicate Leptoxis plicata
Wherever found
E
Rocksnail, round Leptoxis ampla
Wherever found
T
Taylorconcha serpenticola
Wherever found
T
Succinea chittenangoensis
Wherever found
T
43 FR 28932,
7/3/1978.
Triodopsis platysayoides
Wherever found
T
43 FR 28932,
7/3/1978.
Samoana fragilis
Wherever found
E
80 FR 59423,
10/1/2015.
Partula radiolata
Wherever found
E
80 FR 59423,
10/1/2015.
Partula gibba
Wherever found
E
80 FR 59423,
10/1/2015.
Discus macclintocki
Wherever found
E
43 FR 28932,
7/3/1978.
Snail, Bliss
Rapids
Snail,
Chittenango
ovate amber
Snail, flat-spired
three-toothed
Snail, fragile tree
(Akaleha dogas,
Denden)
Snail, Guam tree
(Akaleha,
Denden)
Snail, humped
tree (Akaleha,
Denden)
Snail, Iowa
Pleistocene
Snail, Lanai tree Partulina semicarinata
Wherever found
E
Snail, Lanai tree Partulina variabilis
Wherever found
E
Wherever found
E
Wherever found
E
Snail, Morro
shoulderband
Helminthoglypta walkeriana
(=Banded dune)
Wherever found
E
Snail, Newcomb's Erinna newcombi
Wherever found
T
Snail, Newcomb's
Newcombia cumingi
tree
Wherever found
E
Eua zebrina
Wherever found
E
Ostodes strigatus
Wherever found
E
Mesodon clarki nantahala
Wherever found
T
Anguispira picta
Wherever found
T
Physa natricina
Wherever found
E
Orthalicus reses(not
incl. nesodryas )
Wherever found
T
Tulotoma magnifica
Wherever found
T
Snail, Virginia
Polygyriscus virginianus
fringed mountain
Wherever found
E
Snails, Oahu tree Achatinella spp.
Wherever found
E
Tryonia alamosae
Wherever found
E
Pyrgulopsis bruneauensis
Wherever found
E
Pyrgulopsis chupaderae
Wherever found
E
Snail, Langford's
tree (Akaleha,
Partula langfordi
Denden)
Snail, Manus
Papustyla pulcherrima
Island tree
Snail [no
common name]
Snail [no
common name]
Snail, noonday
Snail, painted
snake coiled
forest
Snail, Snake
River physa
Snail, Stock
Island tree
Snail, tulotoma
Springsnail,
Alamosa
Springsnail,
Bruneau Hot
Springsnail,
Chupadera
78 FR 32013,
5/28/2013.
78 FR 32013,
5/28/2013.
80 FR 59423,
10/1/2015.
35 FR 8491,
6/2/1970.
59 FR 64613,
12/15/1994;
50 CFR
17.95(f).CH
65 FR 4162,
1/26/2000;
50 CFR
17.95(f).CH
78 FR 32013,
5/28/2013;
50 CFR
17.95(f).CH
81 FR 65466,
9/22/2016.
81 FR 65466,
9/22/2016.
43 FR 28932,
7/3/1978.
43 FR 28932,
7/3/1978.
57 FR 59244,
12/14/1992.
43 FR 28932,
7/3/1978.
56 FR 797,
1/9/1991;
76 FR 31866,
6/2/2011.
43 FR 28932,
7/3/1978.
46 FR 3178,
1/13/1981;
46 FR 40025,
8/6/1981.
56 FR 49646,
9/30/1991.
58 FR 5938,
1/25/1993.
77 FR 41088,
7/12/2012;
50 CFR
17.95(f).CH
Springsnail,
Koster's
Juturnia kosteria
Wherever found
E
Springsnail,
Phantom
Pyrgulopsis texana
Wherever found
E
Springsnail,
Roswell
Pyrgulopsis roswellensis
Wherever found
E
Springsnail, San
Pyrgulopsis bernardina
Bernardino
Wherever found
T
Springsnail,
Socorro
Pyrgulopsis neomexicana
Wherever found
E
Springsnail,
Three Forks
Pyrgulopsis trivialis
Wherever found
E
Tryonia, Diamond Pseudotryonia adamantina
Wherever found
E
Tryonia,
Gonzales
Wherever found
E
Wherever found
E
Tryonia circumstriata
Tryonia, Phantom Tryonia cheatumi
76 FR 33036,
6/7/2011;
50 CFR
17.95(f).CH
78 FR 41227,
7/9/2013;
50 CFR
17.95(f).CH
76 FR 33036,
6/7/2011;
50 CFR
17.95(f).CH
77 FR 23060,
4/17/2012;
50 CFR
17.95(f).CH
56 FR 49646,
9/30/1991.
77 FR 23060,
4/17/2012;
50 CFR
17.95(f).CH
78 FR 41227,
7/9/2013;
50 CFR
17.95(f).CH
78 FR 41227,
7/9/2013;
50 CFR
17.95(f).CH
78 FR 41227,
7/9/2013;
50 CFR
17.95(f).CH
Insects
Bee, bumble,
rusty patched
Bombus affinis
Wherever found
E
Bee, yellow-faced Hylaeus anthracinus
Wherever found
E
Bee, yellow-faced Hylaeus assimulans
Wherever found
E
Bee, yellow-faced Hylaeus facilis
Wherever found
E
Bee, yellow-faced Hylaeus hilaris
Wherever found
E
Bee, yellow-faced Hylaeus kuakea
Wherever found
E
Bee, yellow-faced Hylaeus longiceps
Wherever found
E
Bee, yellow-faced Hylaeus mana
Wherever found
E
82 FR 3186,
1/11/2017.
81 FR 67786,
9/30/2016.
81 FR 67786,
9/30/2016.
81 FR 67786,
9/30/2016.
81 FR 67786,
9/30/2016.
81 FR 67786,
9/30/2016.
81 FR 67786,
9/30/2016.
81 FR 67786,
9/30/2016.
Beetle, American
Nicrophorus americanus
burying
Beetle, American
Nicrophorus americanus
burying
Entire, except where
listed as an
E
experimental
population
In southwestern
Missouri, the counties
XN
of Cedar, St. Clair,
Bates, and Vernon
Beetle, Casey's
June
Dinacoma caseyi
Wherever found
E
Beetle, Coffin
Cave mold
Batrisodes texanus
Wherever found
E
Beetle, Comal
Springs dryopid
Stygoparnus comalensis
Wherever found
E
Beetle, Comal
Springs riffle
Heterelmis comalensis
Wherever found
E
Beetle, delta
green ground
Elaphrus viridis
Wherever found
T
Beetle, Helotes
mold
Batrisodes venyivi
Wherever found
E
Beetle,
Hungerford's
crawling water
Brychius hungerfordi
Wherever found
E
Beetle,
Kretschmarr
Cave mold
Texamaurops reddelli
Wherever found
E
Cicindelidia floridana
U.S.A. (FL)
E
Polyphylla barbata
Wherever found
E
Beetle, (no
common name)
Rhadine exilis
Wherever found
E
Beetle, (no
common name)
Rhadine infernalis
Wherever found
E
Beetle, Miami
tiger
Beetle, Mount
Hermon June
54 FR 29652,
7/13/1989.
77 FR 16712,
3/22/2012;
50 CFR
17.85(c).10j
76 FR 58954,
9/22/2011;
50 CFR
17.95(i).CH
53 FR 36029,
9/16/1988;
58 FR 43818,
8/18/1993.
62 FR 66295,
12/18/1997;
50 CFR
17.95(i).CH
62 FR 66295,
12/18/1997;
50 CFR
17.95(i).CH
45 FR 52807,
8/8/1980;
50 CFR
17.95(i).CH
70 FR 69854,
11/17/2005;
50 CFR
17.95(i).CH
59 FR 10580,
3/7/1994.
53 FR 36029,
9/16/1988;
58 FR 43818,
8/18/1993.
81 FR 68985,
10/5/2016.
62 FR 3616,
1/24/1997.
70 FR 69854,
11/17/2005;
50 CFR
17.95(i).CH
70 FR 69854,
11/17/2005;
50 CFR
17.95(i).CH
Beetle,
Northeastern
beach tiger
Beetle, Ohlone
tiger
Beetle, Puritan
tiger
Cicindela dorsalis dorsalis
Wherever found
T
Cicindela ohlone
Wherever found
E
Cicindela puritana
Wherever found
T
Beetle, Salt
Creek tiger
Cicindela nevadica lincolniana
Wherever found
E
Beetle, Tooth
Cave ground
Rhadine persephone
Wherever found
E
Beetle, valley
elderberry
longhorn
Desmocerus californicus
dimorphus
Wherever found
T
Butterfly,
Bartram's scrub- Strymon acis bartrami
hairstreak
Wherever found
E
Butterfly, bay
checkerspot
Euphydryas editha bayensis
Wherever found
T
Speyeria zerene behrensii
Wherever found
E
Speyeria callippe callippe
Wherever found
E
Butterfly,
Behren's
silverspot
Butterfly, callippe
silverspot
Butterfly, cassius
blue
Butterfly,
ceraunus blue
Butterfly,
Corsican
swallowtail
Butterfly, El
Segundo blue
Butterfly,
Fender's blue
55 FR 32088,
8/7/1990.
66 FR 50340,
8/3/2001.
55 FR 32088,
8/7/1990.
70 FR 58335,
10/6/2005;
50 CFR
17.95(i).CH
53 FR 36029,
9/16/1988.
45 FR 52803,
8/8/1980;
50 CFR
17.95(i).CH
79 FR 47221,
8/12/2014;
50 CFR
17.95(i).CH
52 FR 35366,
9/18/1987;
50 CFR
17.95(i).CH
62 FR 64306,
12/5/1997.
Hemiargus ceraunus
antibubastus
Coastal south and
central FL
Coastal south and
central FL
62 FR 64306,
12/5/1997.
T
77 FR 20948,
(S/A) 4/6/2012.
T
77 FR 20948,
(S/A) 4/6/2012.
Papilio hospiton
Wherever found
E
Euphilotes battoides allyni
Wherever found
E
Icaricia icarioides fenderi
Wherever found
E
Wherever found
E
Wherever found
E
58 FR 4356,
1/14/1993.
Wherever found
E
57 FR 59236,
12/14/1992.
Leptotes cassius theonus
Butterfly, Florida
Anaea troglodyta floridalis
leafwing
Butterfly,
Homerus
Papilio homerus
swallowtail
Butterfly, Karner
Lycaeides melissa samuelis
blue
58 FR 4356,
1/14/1993.
41 FR 22041,
6/14/1976.
65 FR 3875,
1/25/2000;
50 CFR
17.95(i).CH
79 FR 47221,
8/12/2014;
50 CFR
17.95(i).CH
Butterfly, Lange's
metalmark
Butterfly, lotis
blue
Butterfly, Luzon
peacock
swallowtail
Butterfly, Mariana
eight-spot
(Ababbang,
Libweibwogh)
Butterfly, Mariana
wandering
(Ababbang,
Libweibwogh)
Butterfly, Miami
blue
Butterfly, mission
blue
Wherever found
E
Lycaeides argyrognomon lotis
Wherever found
E
Papilio chikae
Wherever found
E
58 FR 4356,
1/14/1993.
Hypolimnas octocula
marianensis
Wherever found
E
80 FR 59423,
10/1/2015.
Vagrans egistina
Wherever found
E
80 FR 59423,
10/1/2015.
Cyclargus thomasi
bethunebakeri
Wherever found
E
Icaricia icarioides missionensis Wherever found
Butterfly,
Mitchell's satyr
Neonympha mitchellii mitchellii Wherever found
Butterfly, Mount
Charleston blue
Icaricia (Plebejus) shasta
charlestonensis
Wherever found
Butterfly, Myrtle's
Speyeria zerene myrtleae
silverspot
Wherever found
Butterfly,
nickerbean blue
Coastal south and
central FL
Cyclargus ammon
Butterfly, Oregon
Speyeria zerene hippolyta
silverspot
Butterfly, Oregon
Speyeria zerene hippolyta
silverspot
Butterfly, Palos
Verdes blue
Glaucopsyche lygdamus
palosverdesensis
Butterfly, Queen
Alexandra's
Troides alexandrae
birdwing
Butterfly, Quino
checkerspot
41 FR 22041,
6/14/1976.
41 FR 22041,
6/14/1976.
Apodemia mormo langei
Euphydryas editha quino
77 FR 20948,
4/6/2012.
41 FR 22041,
E
6/14/1976.
56 FR 28825,
6/25/1991;
E
57 FR 21564,
5/20/1992.
78 FR 57749,
9/19/2013;
E
50 CFR
17.95(i).CH
57 FR 27848,
E
6/22/1992.
77 FR 20948,
T
4/6/2012;
(S/A) 50 CFR
17.47(a).4d
Wherever found,
except where listed as
T
an experimental
population
U.S.A. (OR—specified
portions of Clatsop and
XN
Tillamook Counties;
see §17.85(d))
45 FR 44935,
7/2/1980; 50 CFR
17.95(i).CH
82 FR 28567;
06/23/2017.
Wherever found
E
45 FR 44935,
7/2/1980;
50 CFR
17.95(i).CH
Wherever found
E
54 FR 38950,
9/21/1989.
E
62 FR 2313,
1/16/1997;
50 CFR
17.95(i).CH
Wherever found
Butterfly, Saint
Francis' satyr
Neonympha mitchellii francisci
Wherever found
E
Butterfly, San
Bruno elfin
Callophrys mossii bayensis
Wherever found
E
Butterfly, Schaus Heraclides aristodemus
swallowtail
ponceanus
Wherever found
E
Butterfly, Smith's
Euphilotes enoptes smithi
blue
Wherever found
E
Butterfly, Taylor's
Euphydryas editha taylori
checkerspot
Wherever found
E
Butterfly,
Uncompahgre
fritillary
Boloria acrocnema
Wherever found
E
Damselfly,
blackline
Hawaiian
Megalagrion nigrohamatum
nigrolineatum
59 FR 18324,
4/18/1994;
60 FR 5264,
1/26/1995.
41 FR 22041,
6/14/1976.
41 FR 17736,
4/28/1976;
49 FR 34501,
8/31/1984.
41 FR 22041,
6/14/1976.
78 FR 61451,
10/3/2013;
50 CFR
17.95(i).CH
56 FR 28712,
6/24/1991.
77 FR 57647,
9/18/2012;
50 CFR
17.95(i).CH
77 FR 57647,
9/18/2012;
50 CFR
17.95(i).CH
52 FR 21481,
6/5/1987;
50 CFR
17.95(i).CH
77 FR 57647,
9/18/2012;
50 CFR
17.95(i).CH
Wherever found
E
Damselfly,
Megalagrion leptodemas
crimson Hawaiian
Wherever found
E
Damselfly, flying
Megalagrion nesiotes
earwig Hawaiian
Wherever found
E
Damselfly,
Megalagrion oceanicum
oceanic Hawaiian
Wherever found
E
Damselfly,
orangeblack
Hawaiian
Wherever found
E
81 FR 67786,
9/30/2016.
Megalagrion xanthomelas
Damselfly, Pacific
Megalagrion pacificum
Hawaiian
Wherever found
E
52 FR 21481,
6/5/1987;
50 CFR
17.95(i).CH
Damselfly, Rota
blue (Dulalas
Luta, Dulalas
Luuta)
Wherever found
E
80 FR 59423,
10/1/2015.
Ischnura luta
Dragonfly, Hine's
Somatochlora hineana
emerald
Wherever found
E
Fly, Delhi Sands Rhaphiomidas terminatus
flower-loving
abdominalis
Wherever found
E
60 FR 5267,
1/26/1995;
50 CFR
17.95(i).CH
58 FR 49881,
9/23/1993.
Fly, Hawaiian
picture-wing
Drosophila aglaia
Wherever found
E
Fly, Hawaiian
picture-wing
Drosophila differens
Wherever found
E
Fly, Hawaiian
picture-wing
Drosophila digressa
Wherever found
E
Fly, Hawaiian
picture-wing
Drosophila hemipeza
Wherever found
E
Fly, Hawaiian
picture-wing
Drosophila heteroneura
Wherever found
E
Fly, Hawaiian
picture-wing
Drosophila montgomeryi
Wherever found
E
Fly, Hawaiian
picture-wing
Drosophila mulli
Wherever found
T
Fly, Hawaiian
picture-wing
Drosophila musaphilia
Wherever found
E
Fly, Hawaiian
picture-wing
Drosophila neoclavisetae
Wherever found
E
Fly, Hawaiian
picture-wing
Drosophila obatai
Wherever found
E
Fly, Hawaiian
picture-wing
Drosophila ochrobasis
Wherever found
E
Fly, Hawaiian
picture-wing
Drosophila sharpi
Wherever found
E
Fly, Hawaiian
picture-wing
Drosophila substenoptera
Wherever found
E
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
78 FR 64637,
10/29/2013.
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
Fly, Hawaiian
picture-wing
Drosophila tarphytrichia
Wherever found
E
Grasshopper,
Zayante bandwinged
Trimerotropis infantilis
Wherever found
E
Moth, Blackburn's
Manduca blackburni
sphinx
Wherever found
E
Moth, Kern
primrose sphinx
Euproserpinus euterpe
Wherever found
T
Naucorid, Ash
Meadows
Ambrysus amargosus
Wherever found
T
U.S.A., (Lassen
County, CA; Washoe
County, NV)
E
Skipper, Carson Pseudocopaeodes eunus
wandering
obscurus
Skipper, Dakota
Hesperia dacotae
Wherever found
T
Skipper, Laguna
Pyrgus ruralis lagunae
Mountains
Wherever found
E
Skipper, Pawnee
Hesperia leonardus montana
montane
Wherever found
T
Skipperling,
Poweshiek
Wherever found
E
Stonefly,
Lednia tumana
meltwater lednian
Wherever found
T
Stonefly, western
Zapada glacier
glacier
Wherever found
T
Oarisma poweshiek
71 FR 26835,
5/9/2006;
50 CFR
17.95(i).CH
62 FR 3616,
1/24/1997;
50 CFR
17.95(i).CH
65 FR 4770,
2/1/2000;
50 CFR
17.95(i).CH
45 FR 24088,
4/8/1980.
50 FR 20777,
5/20/1985;
50 CFR
17.95(i).CH
67 FR 51116,
8/7/2002.
79 FR 63671,
10/24/2014;
50 CFR
17.95(i);CH
50 CFR
17.47(b).4d
62 FR 2313,
1/16/1997;
50 CFR
17.95(i).CH
52 FR 36176,
9/25/1987.
79 FR 63671,
10/24/2014;
50 CFR
17.95(i).CH
84 FR 64210,
11/21/2019;
50 CFR
17.47(c).4d
84 FR 64210,
11/21/2019;
50 CFR
17.47(c).4d
Arachnids
Harvestman, Bee
Texella reddelli
Creek Cave
Wherever found
E
53 FR 36029,
9/16/1988;
58 FR 43818,
8/18/1993.
Harvestman,
Bone Cave
Texella reyesi
Wherever found
E
Harvestman,
Cokendolpher
cave
Texella cokendolpheri
Wherever found
E
Meshweaver,
Circurina venii
Braken Bat Cave
Wherever found
E
Meshweaver,
Government
Circurina vespera
Canyon Bat Cave
Wherever found
E
Meshweaver,
Madla Cave
Cicurina madla
Wherever found
E
Meshweaver,
Robber Baron
Cave
Cicurina baronia
Wherever found
E
Pseudoscorpion,
Tartarocreagris texana
Tooth Cave
Wherever found
E
Spider,
Government
Neoleptoneta microps
Canyon Bat Cave
Wherever found
E
Spider, ivory
Poecilotheria subfusca
ornamental tiger
Wherever found
E
Spider, Kauai
cave wolf
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Adelocosa anops
Spider, ornate
Poecilotheria ornata
tiger
Spider,
Poecilotheria vittata
Pedersen's tiger
Spider, Smith's
Poecilotheria smithi
tiger
Spider, spruce-fir
Microhexura montivaga
moss
Spider, Sri Lanka
Poecilotheria fasciata
ornamental tiger
Spider, Tooth
Neoleptoneta myopica
Cave
Crustaceans
53 FR 36029,
9/16/1988;
58 FR 43818,
8/18/1993.
65 FR 69624,
11/17/2000;
50 CFR
17.95(g).CH
65 FR 69624,
11/17/2000;
50 CFR
17.95(g).CH
65 FR 69624,
11/17/2000;
50 CFR
17.95(g).CH
65 FR 69624,
11/17/2000;
50 CFR
17.95(g).CH
65 FR 69624,
11/17/2000;
50 CFR
17.95(g).CH
53 FR 36029,
9/16/1988.
65 FR 69624,
11/17/2000;
50 CFR
17.95(g).CH
83 FR 36755,
7/31/2018.
65 FR 2348,
1/14/2000;
50 CFR
17.95(g).CH
83 FR 36755,
7/31/2018.
83 FR 36755,
7/31/2018.
83 FR 36755,
7/31/2018.
60 FR 6968,
2/6/1995;
50 CFR
17.95(g).CH
83 FR 36755,
7/31/2018.
53 FR 36029,
9/16/1988.
Amphipod,
diminutive
Gammarus hyalleloides
Wherever found
E
Wherever found
E
Wherever found
E
Amphipod, Kauai
Spelaeorchestia koloana
cave
Wherever found
E
Amphipod, Noel's Gammarus desperatus
Wherever found
E
Amphipod, Peck's Stygobromus (=Stygonectes)
cave
Pecki
Wherever found
E
Amphipod, Pecos Gammarus pecos
Wherever found
E
Crayfish, Big
Sandy
Cambarus callainus
Wherever found
T
Crayfish, cave
Cambarus aculabrum
Wherever found
E
Crayfish, cave
Cambarus zophonastes
Wherever found
E
Wherever found
E
Wherever found
E
Crayfish, Shasta Pacifastacus fortis
Wherever found
E
Fairy shrimp,
Conservancy
Branchinecta conservatio
Wherever found
E
Fairy shrimp,
longhorn
Branchinecta longiantenna
Wherever found
E
Fairy shrimp,
Riverside
Streptocephalus woottoni
Wherever found
E
Wherever found
E
Amphipod, Hay's
Stygobromus hayi
Spring
Amphipod, Illinois
Gammarus acherondytes
Cave
Crayfish,
ambarus veteranus
Guyandotte River
Crayfish,
Orconectes shoupi
Nashville
Fairy shrimp, San
Branchinecta sandiegonensis
Diego
78 FR 41227,
7/9/2013;
50 CFR
17.95(h).CH
47 FR 5425,
2/5/1982.
63 FR 46900,
9/3/1998.
65 FR 2348,
1/14/2000;
50 CFR
17.95(h).CH
76 FR 33036,
6/7/2011;
50 CFR
17.95(h).CH
62 FR 66295,
12/18/1997;
50 CFR
17.95(h).CH
78 FR 41227,
7/9/2013;
50 CFR
17.95(h).CH
81 FR 20449,
4/7/2016.
58 FR 25742,
4/27/1993.
52 FR 11170,
4/7/1987.
81 FR 20449,
4/7/2016.
51 FR 34410,
9/3/1986.
53 FR 38460,
9/30/1988.
59 FR 48136,
9/19/1994;
50 CFR
17.95(h).CH
59 FR 48136,
9/19/1994;
50 CFR
17.95(h).CH
58 FR 41384,
8/3/1993;
50 CFR
17.95(h).CH
62 FR 4925,
2/3/1997;
50 CFR
17.95(h).CH
Fairy shrimp,
vernal pool
Branchinecta lynchi
Wherever found
E
Isopod, Lee
County cave
Lirceus usdagalun
Wherever found
E
Wherever found
T
Thermosphaeroma thermophilus Wherever found
E
Isopod, Madison
Antrolana lira
Cave
Isopod, Socorro
Shrimp, Alabama
Palaemonias alabamae
cave
Shrimp,
Procaris hawaiana
anchialine pool
Shrimp,
Vetericaris chaceorum
anchialine pool
Shrimp, California
Syncaris pacifica
freshwater
Wherever found
E
Wherever found
E
Wherever found
E
Wherever found
E
Shrimp, Kentucky
Palaemonias ganteri
cave
Wherever found
E
Shrimp, Squirrel
Palaemonetes cummingi
Chimney cave
Wherever found
T
Tadpole shrimp,
vernal pool
Wherever found
E
Lepidurus packardi
59 FR 48136,
9/19/1994;
50 CFR
17.95(h).CH
57 FR 54722,
11/20/1992.
47 FR 43699,
10/4/1982;
50 CFR
17.46(a).4d
43 FR 12690,
3/27/1978.
53 FR 34696,
9/7/1988.
81 FR 67786,
9/30/2016.
78 FR 64637,
10/29/2013.
53 FR 43884,
10/31/1988.
48 FR 46337,
10/12/1983;
50 CFR
17.95(h).CH
55 FR 25588,
6/21/1990.
59 FR 48136,
9/19/1994;
50 CFR
17.95(h).CH
Corals
Coral, (no
common name)
Acropora globiceps
Wherever found
T
Coral, (no
common name)
Acropora jacquelineae
Wherever found
T
Coral, (no
common name)
Acropora lokani
Wherever found
T
Coral, (no
common name)
Acropora pharaonis
Wherever found
T
Coral, (no
common name)
Acropora retusa
Wherever found
T
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
Coral, (no
common name)
Acropora rudis
Wherever found
T
Coral, (no
common name)
Acropora speciosa
Wherever found
T
Coral, (no
common name)
Acropora tenella
Wherever found
T
Coral, (no
common name)
Anacropora spinosa
Wherever found
T
Coral, (no
common name)
Cantharellus noumeae
Wherever found
E
Coral, (no
common name)
Euphyllia paradivisa
Wherever found
T
Coral, (no
common name)
Isopora crateriformis
Wherever found
T
Coral, (no
common name)
Montipora australiensis
Wherever found
T
Coral, (no
common name)
Pavona diffluens
Wherever found
T
Coral, (no
common name)
Porites napopora
Wherever found
T
Coral, (no
common name)
Seriatopora aculeata
Wherever found
T
Coral, (no
common name)
Siderastrea glynni
Wherever found
E
Coral, (no
common name)
Tubastraea floreana
Wherever found
E
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
80 FR 60560,
10/7/2015; N 81
FR 76311,
11/2/2016.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
80 FR 60560,
10/7/2015; N 81
FR 76311,
11/2/2016.
80 FR 60560,
10/7/2015; N 81
FR 76311,
11/2/2016.
Coral, boulder
star
Orbicella franksi
Wherever found
T
Coral, elkhorn
Acropora palmata
Wherever found
T
Coral, lobed star Orbicella annularis
Wherever found
T
Coral,
Orbicella faveolata
mountainous star
Wherever found
T
Coral, pillar
Dendrogyra cylindrus
Wherever found
T
Coral, rough
cactus
Mycetophyllia ferox
Wherever found
T
Coral, staghorn
Acropora cervicornis
Wherever found
T
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014;
50 CFR
223.208;4d
50 CFR
226.216.CH
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014.
76 FR 20558,
4/13/2011;
79 FR 42687,
7/23/2014;
79 FR 53852,
9/10/2014;N
79 FR 67356,
11/13/2014;
50 CFR
223.208;4d
50 CFR
226.216.CH
Cephalopods
Nautilus,
chambered
Nautilus pompilius
Wherever found
T
83 FR 48976,
9/28/2018;N 84
FR 13809,
4/8/2019.
[81 FR 51556, Aug. 4, 2016, as amended at 81 FR 53332, Aug. 12, 2016; 81 FR 59090, Aug. 26, 2016; 81 FR
62659, Sept. 12, 2016; 81 FR 65507, Sept. 22, 2016; 81 FR 67214, 67856, Sept. 30, 2016; 81 FR 68984, 69007,
Oct. 5, 2016; 81 FR 69425, Oct. 6, 2016; 81 FR 76313, Nov. 2, 2016; 81 FR 93640, Dec. 21, 2016; 82 FR 3208,
Jan 11, 2017; 82 FR 16540, 16704, Apr. 5, 2017; 82 FR 20284, May 1, 2017; 82 FR 28577, 28588, June 23, 2017;
82 FR 30632, June 30, 2017; 82 FR 43885, 43896, 43907, Sept. 20, 2017; 83 FR 278, Jan. 3, 2018; 83 FR 2087,
Jan. 16, 2018; 83 FR 3099, Jan. 23, 2018; 83 FR 5735, Feb. 9, 2018; 83 FR 14198, Apr. 3, 2018; 83 FR 14982,
Apr. 6, 2018; 83 FR 16242, Apr. 16, 2018; 83 FR 17110, Apr. 18, 2018; 83 FR 36772, July 31, 2018; 83 FR 39916,
Aug. 13, 2018; 83 FR 58753, Nov. 21, 2018; 83 FR 67139, Dec. 28, 2018; 84 FR 6310, Feb. 26, 2019; 84 FR
13811, Apr. 8, 2019; 84 FR 25003, May 30, 2019; 84 FR 37145, July 31, 2019; 84 FR 48308, Sept. 13, 2019; 84
FR 52659, Oct. 2, 2019; 84 FR 52800, Oct. 3, 2019; 84 FR 54463, Oct. 9, 2019; 84 FR 56135, Oct. 21, 2019; 84
FR 64226, Nov. 21, 2019; 84 FR 69946, Dec. 19, 2019; 85 FR 189, Jan. 2, 2020]
return arrow Back to Top
§17.12 Endangered and threatened plants.
(a) The list in paragraph (h) of this section contains the plant species determined by the Service or the National
Marine Fisheries Service (NMFS) of the Department of Commerce's National Oceanic and Atmospheric
Administration (hereafter in this section referred to as “the Services”) to be endangered species or threatened
species. It also contains the plant species treated as endangered or threatened because they are similar in
appearance to and may be confused with endangered or threatened species (see §§17.50 through 17.52). The
“Common name,” “Scientific name,” “Where listed,” and “Status” columns provide regulatory information; together,
they identify listed plant species within the meaning of the Act and describe where they are protected. When a
taxon has more than one entry, the “Where listed” or “Status” column will identify its status in each relevant
geographic area. The listing of a particular taxon includes all lower taxonomic units.
(b) “Scientific name” column. The Services use the most recently accepted scientific name. In cases where
confusion might arise, one or more synonyms are provided in parentheses within the “Scientific name” column.
The Services will rely to the extent practicable on the Integrated Taxonomic Information System (ITIS) to determine
a species' scientific name. ITIS incorporates the naming principles established by the International Code of
Nomenclature for algae, fungi, and plants (see paragraph (g) of this section). If the scientific name in ITIS differs
from the scientific name adopted for use under the Convention on International Trade in Endangered Species of
Wild Fauna and Flora (CITES), the CITES nomenclature will be provided in brackets “[ ]” within the “Scientific
name” column following the ITIS nomenclature.
(c) “Common name” column. Although common names are included, they cannot be relied upon for identification
of any specimen, since they may vary greatly in local usage. In cases where confusion might arise, one or more
synonyms are provided in parentheses within the “Common name” column.
(d) “Where listed” column. The “Where listed” column sets forth the geographic area where the species is listed for
purposes of the Act. Except when providing a geographic description of an experimental population designation,
“Wherever found” will be used to indicate the Act's protections apply to all individuals of the species, wherever
found.
(e) “Status” column. Within the “Status” column, the following abbreviations are used:
Abbreviation
E
T
E (S/A)
T (S/A)
XE
XN
Regulatory status the abbreviation represents
Endangered species.
Threatened species.
Endangered based on similarity of appearance to an existing listed species.
Threatened based on similarity of appearance to an existing listed species.
Essential experimental population (See subpart H of this part).
Nonessential experimental population (See subpart H of this part).
(f) “Listing Citations and Applicable Rules” column. The “Listing Citations and Applicable Rules” column is
nonregulatory in nature and is provided for informational and navigational purposes only. Please note that the
sections of part 17 that include designations of critical habitat for plants are organized by family name. A link to the
Integrated Taxonomic Information System (ITIS), which displays the taxonomic hierarchy of a species, including its
family name, is provided on each species' profile page accessible through the Service's Web site
(http://www.fws.gov/endangered/) or information is available directly through the ITIS (http://www.itis.gov/).
(1) Within the “Listing Citations and Applicable Rules” column, the following superscripts are used:
SuperscriptDescription of citation or rule
N
NMFS listing citation (NMFS Lead).
J
Both FWS and NMFS listing citation (Joint Jurisdiction).
CH
Critical habitat rule.
4d
Species-specific “4(d)” rule (a rule issued under the authority of section 4(d) of the Act).
Species-specific “10(j)” rule (a rule issued under the authority of section 10(j) of the
10j
Act).
(2) Listing citations contain the volume, document starting page number, and publication date of the Federal
Register publication(s) in which a species' status was assessed. At least since 1973, these documents have
included a statement indicating the basis for the listing or reclassification, as well as the effective date(s) of the
listing or other rules that changed how the species was identified in the list in paragraph (h) of this section.
(3) “Critical habitat” and “Species-specific” rules superscripts provide cross-references to other sections in part 17
or part 222, 223, or 226 of chapter II of this title where critical habitat and species-specific rules are found. The
species-specific superscripts also identify experimental populations. Experimental populations (superscript “10j”)
are a separate citation, with one of the following symbols in the “Status” column: “XE” for an essential experimental
population and “XN” for a nonessential experimental population.
(4) This column is for reference and navigational purposes only. All other appropriate rules in part 17, parts 217
through 226 of chapter II of this title, and part 402 of chapter IV of this title apply, if no species-specific rules are
referenced. In addition, other rules in this title could relate to such species (for example, port-of-entry
requirements). The references in the “Listing Citations and Applicable Rules” column do not comprise a
comprehensive list of all regulations that the Services might apply to the species or to the regulations of other
Federal agencies or State or local governments.
(g) The Services will rely to the extent practicable on ITIS (http://www.itis.gov) and standard references adopted for
CITES (http://cites.org).
(h) The “List of Endangered and Threatened Plants” is provided in the table in this paragraph (h):
Scientific name
Common name
Where
listed
Listing
citations and
Status
applicable
rules
Flowering Plants
Wherever
E
found
Wherever
E
found
Wherever
E
found
Abronia macrocarpa
Large-fruited sand-verbena
Abutilon eremitopetalum
No common name
Abutilon menziesii
Ko`oloa`ula
Abutilon sandwicense
No common name
Wherever
E
found
Acaena exigua
Liliwai
Wherever
E
found
Acanthomintha ilicifolia
San Diego thornmint
Wherever
T
found
Acanthomintha obovata ssp. duttonii San Mateo thornmint
Wherever
E
found
53 FR 37975,
9/28/1988.
56 FR 47686,
9/20/1991.
51 FR 34412,
9/26/1986.
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1).CH
63 FR 54938,
10/13/1998;
50 CFR
17.96(a).CH
50 FR 37858,
9/18/1985.
Achyranthes mutica
No common name
Achyranthes splendens var. rotundata Round-leaved chaff-flower
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
T
found
Wherever
T
found
Wherever
E
found
Acmispon dendroideus var. traskiae
San Clemente Island lotus
Aconitum noveboracense
Northern wild monkshood
Aeschynomene virginica
Sensitive joint-vetch
Agalinis acuta
Sandplain gerardia
Agave eggersiana
No common name
Wherever
E
found
Alectryon macrococcus
Mahoe
Wherever
E
found
Allium munzii
Munz's onion
Wherever
E
found
Alopecurus aequalis var. sonomensis Sonoma alopecurus
Wherever
E
found
Amaranthus brownii
No common name
Wherever
E
found
Amaranthus pumilus
Seabeach amaranth
Ambrosia cheiranthifolia
South Texas ambrosia
Ambrosia pumila
San Diego ambrosia
Amorpha crenulata
Crenulate lead-plant
Amphianthus pusillus
Little amphianthus
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
61 FR 53108,
10/10/1996;
50 CFR
17.99(k).CH
51 FR 10518,
3/26/1986;
50 CFR
17.99(i).CH
42 FR 40685,
8/11/1977.
43 FR 17910,
4/26/1978.
57 FR 21569,
5/20/1992.
53 FR 34701,
9/7/1988.
79 FR 53303,
9/9/2014;
50 CFR
17.96(a).CH
57 FR 20772,
5/15/1992;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c) ;CH
50 CFR
17.99(e) );CH
50 CFR
17.99(i).CH
63 FR 54975,
10/13/1998;
50 CFR
17.96(a).CH
62 FR 54791,
10/22/1997.
61 FR 43178,
8/21/1996;
50 CFR
17.99(g).CH
58 FR 18035,
4/7/1993.
59 FR 43648,
8/24/1994.
67 FR 44372,
7/2/2002;
50 CFR
17.96.CH
50 FR 29345,
7/18/1985.
53 FR 3560,
2/5/1988.
Wherever
E
found
Amsinckia grandiflora
Large-flowered fiddleneck
Amsonia kearneyana
Kearney's blue-star
Apios priceana
Price's potato-bean
Arabis georgiana
Georgia rockcress
Arabis hoffmannii
Hoffmann's rock-cress
Arabis mcdonaldiana
McDonald's rock-cress
Arabis (=Boechera) perstellata
Braun's Rock-cress
Arabis serotina
Shale barren rock-cress
Arctomecon humilis
Dwarf bear-poppy
Arctostaphylos confertiflora
Santa Rosa Island
manzanita
Arctostaphylos franciscana
Franciscan manzanita
Arctostaphylos
glandulosa ssp. crassifolia
Del Mar manzanita
Arctostaphylos hookeri var. ravenii
Presidio manzanita
Arctostaphylos morroensis
Morro manzanita
Arctostaphylos myrtifolia
Ione manzanita
Arctostaphylos pallida
Pallid manzanita
Arenaria cumberlandensis
Cumberland sandwort
Arenaria paludicola
Marsh sandwort
Arenaria ursina
Bear Valley sandwort
Wherever
T
found
Argemone
pleiacantha ssp. pinnatisecta
Sacramento prickly-poppy
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
T
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
50 FR 19374,
5/8/1985;
50 CFR
17.96(a).CH
54 FR 2131,
1/19/1989.
55 FR 429,
1/5/1990.
79 FR 54627,
9/12/2014;
50 CFR
17.96(a).CH
62 FR 40954,
7/31/1997.
43 FR 44810,
9/28/1978.
60 FR 56,
1/3/1995;
50 CFR
17.96(a).CH
54 FR 29655,
7/13/1989.
44 FR 64250,
11/6/1979.
62 FR 40954,
7/31/1997.
77 FR 54434,
9/5/2012;
50 CFR
17.96(a).CH
61 FR 52370,
10/7/1996.
44 FR 61910,
10/26/1979.
59 FR 64613,
12/15/1994.
64 FR 28403,
5/26/1999.
63 FR 19842,
4/22/1998.
53 FR 23745,
6/23/1988.
58 FR 41378,
8/3/1993.
63 FR 49006,
9/14/1998;
50 CFR
17.96(a).CH
54 FR 35302,
8/24/1989.
Argyroxiphium kauense
Mauna Loa silversword
Wherever
E
found
Argyroxiphium
sandwicense ssp. macrocephalum
`Ahinahina
Wherever
T
found
Argyroxiphium
sandwicense ssp. sandwicense
`Ahinahina
Argythamnia blodgettii
Blodgett's silverbush
Aristida chaseae
No common name
Aristida portoricensis
Pelos del diablo
Asclepias meadii
Mead's milkweed
Asclepias welshii
Welsh's milkweed
Wherever
T
found
Asimina tetramera
Four-petal pawpaw
Wherever
E
found
Astelia waialealae
Painiu
Wherever
E
found
Astragalus albens
Cushenbury milk-vetch
Wherever
E
found
Astragalus ampullarioides
Shivwits milkvetch
Wherever
E
found
Astragalus applegatei
Applegate's milk-vetch
Astragalus bibullatus
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Guthrie's (=Pyne's) ground- Wherever
E
plum
found
Astragalus brauntonii
Braunton's milk-vetch
Astragalus clarianus
Clara Hunt's milk-vetch
Astragalus
cremnophylax var. cremnophylax
Sentry milk-vetch
Astragalus holmgreniorum
Holmgren milkvetch
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
58 FR 18029,
4/7/1993;
50 CFR
17.99(k).CH
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1).CH
51 FR 9814,
3/1/1986.
81 FR 66842,
9/29/2016.
58 FR 25755,
4/27/1993.
55 FR 32255,
8/8/1990.
53 FR 33992,
9/1/1988.
52 FR 41435,
10/28/1987;
50 CFR
17.96(a).CH
51 FR 34415,
9/26/1986.
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
59 FR 43652,
8/24/1994;
50 CFR
17.96(a).CH
66 FR 49560,
9/28/2001;
50 CFR
17.96(a).CH
58 FR 40547,
7/28/1993.
56 FR 48748,
9/26/1991.
62 FR 4172,
1/29/1997;
50 CFR
17.96(a).CH
62 FR 54791,
10/22/1997.
55 FR 50184,
12/5/1990.
66 FR 49560,
9/28/2001;
50 CFR
17.96(a).CH
Astragalus humillimus
Mancos milk-vetch
Wherever
E
found
Astragalus jaegerianus
Lane Mountain milk-vetch
Wherever
E
found
Astragalus
lentiginosus var. coachellae
Coachella Valley milk-vetch
Wherever
E
found
Astragalus
lentiginosus var. piscinensis
Fish Slough milk-vetch
Wherever
T
found
Astragalus magdalenae var. peirsonii Peirson's milk-vetch
Wherever
T
found
Astragalus montii
Heliotrope milkvetch
Wherever
T
found
Astragalus osterhoutii
Kremmling Osterhout
milkvetch
Wherever
E
found
Astragalus phoenix
Ash Meadows milk-vetch
Wherever
T
found
Astragalus
pycnostachyus var. lanosissimus
Ventura Marsh milk-vetch
Wherever
E
found
Astragalus robbinsii var. jesupi
Jesup's milk-vetch
Astragalus tener var. titi
Coastal dunes milk-vetch
Astragalus tricarinatus
Triple-ribbed milk-vetch
Astrophytum asterias
Star cactus
Atriplex coronata var. notatior
San Jacinto Valley
crownscale
Auerodendron pauciflorum
No common name
Ayenia limitaris
Tamaulipan Kidneypetal
Baccharis vanessae
Encinitas baccharis
Banara vanderbiltii
Palo de Ramón
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
50 FR 26568,
6/27/1985.
63 FR 53596,
10/6/1998;
50 CFR
17.96(a).CH
63 FR 53596,
10/6/1998;
50 CFR
17.96(a).CH
63 FR 53596,
10/6/1998;
50 CFR
17.96(a).CH
63 FR 53596,
10/6/1998;
50 CFR
17.96(a).CH
52 FR 42652,
11/6/1987;
50 CFR
17.96(a).CH
54 FR 29658,
7/13/1989.
50 FR 20777,
5/20/1985;
50 CFR
17.96(a).CH
66 FR 27901,
5/21/2001;
50 CFR
17.96(a).CH
52 FR 21481,
6/5/1987.
63 FR 43100,
8/12/1998.
63 FR 53596,
10/6/1998.
58 FR 53804,
10/18/1993.
63 FR 54975,
10/13/1998;
50 CFR
17.96(a).CH
59 FR 9935,
3/2/1994.
59 FR 43648,
8/24/1994.
61 FR 52370,
10/7/1996.
52 FR 1459,
1/14/1987.
Baptisia arachnifera
Hairy rattleweed
Wherever
E
found
Berberis nevinii
Nevin's barberry
Wherever
E
found
Berberis pinnata ssp. insularis
Island barberry
Wherever
E
found
Betula uber
Virginia round-leaf birch
Wherever
T
found
Bidens amplectens
Kookoolau
Wherever
E
found
Bidens campylotheca ssp. pentamera Kookoolau
Wherever
E
found
Bidens
campylotheca ssp. waihoiensis
Kookoolau
Wherever
E
found
Bidens conjuncta
Kookoolau
Wherever
E
found
Bidens
hillebrandiana ssp. hillebrandiana
Kookoolau
Bidens micrantha ssp. ctenophylla
Kookoolau
Bidens micrantha ssp. kalealaha
Kookoolau
Wherever
E
found
Bidens wiebkei
Kookoolau
Wherever
E
found
Blennosperma bakeri
Sonoma sunshine
Boltonia decurrens
Decurrent false aster
Bonamia grandiflora
Florida bonamia
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
T
found
43 FR 17910,
4/26/1978.
63 FR 54956,
10/13/1998;
50 CFR
17.96(a).CH
62 FR 40954,
7/31/1997.
43 FR 17910,
4/26/1978;
59 FR 59173,
11/16/1994.
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
78 FR 32013,
5/28/2013.
78 FR 64637,
10/29/2013.
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1).CH
57 FR 46325,
10/8/1992;
50 CFR
17.99(c).CH
56 FR 61173,
12/2/1991.
53 FR 45858,
11/14/1988.
52 FR 42068,
11/2/1987.
Bonamia menziesii
No common name
Wherever
E
found
Brickellia mosieri
Florida Brickell-bush
Wherever
found
Brighamia insignis
Olulu
Wherever
E
found
Brighamia rockii
Pua ala
Wherever
E
found
Brodiaea filifolia
Thread-leaved brodiaea
Wherever
T
found
Brodiaea pallida
Chinese Camp brodiaea
Bulbophyllum guamense
Buxus vahlii
Wherever
T
found
Siboyas halumtanu, Siboyan Wherever
T
halom tano
found
Wherever
Vahl's boxwood
E
found
Calamagrostis hillebrandii
No common name
Wherever
E
found
Callicarpa ampla
Capá rosa
Wherever
E
found
Callirhoe scabriuscula
Texas poppy-mallow
Wherever
E
found
Calochortus tiburonensis
Tiburon mariposa lily
Calyptranthes thomasiana
No common name
Wherever
T
found
Wherever
E
found
59 FR 56333,
11/10/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(k);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i);CH
50 CFR
17.99(c).CH
79 FR 52567,
9/4/2014;
50 CFR
17.96(a).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(a)(2).CH
57 FR 46325,
10/8/1992;
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1).CH
63 FR 54975,
10/13/1998;
50 CFR
17.96(a).CH
63 FR 49022,
9/14/1998.
80 FR 59423,
10/1/2015.
50 FR 32572,
8/13/1985.
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
57 FR 14782,
4/22/1992.
46 FR 3184,
1/13/1981;
46 FR 40025,
8/6/1981.
60 FR 6671,
2/3/1995.
59 FR 8138,
2/18/1994.
Calyptridium pulchellum
Calyptronoma rivalis
Calystegia stebbinsii
Camissonia benitensis
Campanula robinsiae
Wherever
T
found
Wherever
Palma de manaca
T
found
Wherever
Stebbins' morning-glory
E
found
Wherever
San Benito evening-primrose
T
found
Wherever
Brooksville bellflower
E
found
Mariposa pussypaws
Canavalia molokaiensis
Awikiwiki
Wherever
E
found
Canavalia napaliensis
Awikiwiki
Wherever
E
found
Canavalia pubescens
Awikiwiki
Wherever
E
found
Calamagrostis expansa
Maui reedgrass
Cardamine micranthera
Small-anthered bittercress
Carex albida
White sedge
Carex lutea
Golden sedge
Wherever
E
found
Carex specuicola
Navajo sedge
Wherever
T
found
Castilleja affinis ssp. neglecta
Tiburon paintbrush
Wherever
E
found
Castilleja campestris ssp. succulenta Fleshy owl's-clover
Wherever
T
found
Castilleja cinerea
Ash-gray Indian paintbrush
Wherever
T
found
Castilleja grisea
San Clemente Island
paintbrush
Castilleja levisecta
Golden paintbrush
Castilleja mollis
Soft-leaved paintbrush
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
63 FR 49022,
9/14/1998.
55 FR 4157,
2/6/1990.
61 FR 54346,
10/18/1996.
50 FR 5755,
2/12/1985.
54 FR 31190,
7/27/1989.
57 FR 46325,
10/8/1992;
50 CFR
17.99(c).CH
76 FR 15609,
5/5/2011;
50 CFR
17.99(a).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
81 FR 67786,
9/30/2016.
54 FR 38947,
9/21/1989.
62 FR 54791,
10/22/1997.
67 FR 3120,
1/23/2002;
50 CFR
17.96(a).CH
50 FR 19370,
5/8/1985;
50 CFR
17.96(a).CH
60 FR 6671,
2/3/1995.
62 FR 14338,
3/26/1997;
50 CFR
17.96(a).CH
63 FR 49006,
9/14/1998;
50 CFR
17.96(a).CH
42 FR 40682,
8/11/1977.
62 FR 31740,
6/11/1997.
62 FR 40954,
7/31/1997.
Wherever
E
found
Catesbaea melanocarpa
No common name
Caulanthus californicus
California jewelflower
Ceanothus ferrisae
Coyote ceanothus
Ceanothus ophiochilus
Vail Lake ceanothus
Wherever
T
found
Ceanothus roderickii
Pine Hill ceanothus
Wherever
E
found
Cenchrus agrimonioides
Kamanomano
Wherever
E
found
Centaurium namophilum
Spring-loving centaury
Wherever
T
found
Cercocarpus traskiae
Catalina Island mountainmahogany
Cereus eriophorus var. fragrans
Fragrant prickly-apple
Chamaecrista
glandulosa var. mirabilis
No common name
Chamaecrista lineata var. keyensis
Big Pine partridge pea
Chamaesyce deltoidea ssp. deltoidea Deltoid spurge
Chamaesyce
deltoidea ssp. pinetorum
Pineland sandmat
Chamaesyce deltoidea ssp.serpyllum Wedge spurge
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
T
found
Chamaesyce garberi
Garber's spurge
Chamaesyce hooveri
Hoover's spurge
Wherever
T
found
Chamaesyce
skottsbergii var. skottsbergii
Akoko (Ewa Plains akoko)
Wherever
E
found
64 FR 13116,
3/17/1999;
50 CFR
17.96(a).CH
55 FR 29361,
7/19/1990.
60 FR 6671,
2/3/1995.
63 FR 54956,
10/13/1998;
50 CFR
17.96(a).CH
61 FR 54346,
10/18/1996.
61 FR 53108,
10/10/1996;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
50 FR 20777,
5/20/1985;
50 CFR
17.96(a).CH
62 FR 42692,
8/8/1997.
50 FR 45618,
11/1/1985.
55 FR 12788,
4/5/1990.
81 FR 66842,
9/29/2016.
50 FR 29345,
7/18/1985.
82 FR 46691,
10/06/2017.
81 FR 66842,
9/29/2016.
50 FR 29345,
7/18/1985.
62 FR 14338,
3/26/1997;
50 CFR
17.96(a).CH
47 FR 36846,
8/24/1982;
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
Charpentiera densiflora
Papala
Wherever
E
found
Chionanthus pygmaeus
Pygmy fringe-tree
Wherever
E
found
Chlorogalum purpureum
Purple amole (Camatta
Canyon amole)
Wherever
T
found
Chorizanthe howellii
Howell's spineflower
Chorizanthe orcuttiana
Orcutt's spineflower
Chorizanthe
pungens var. hartwegiana
Ben Lomond spineflower
Chorizanthe pungens var. pungens
Monterey spineflower
Wherever
T
found
Chorizanthe robusta var. hartwegii
Scotts Valley spineflower
Wherever
E
found
Chorizanthe robusta var. robusta
Robust spineflower
Wherever
E
found
Chorizanthe valida
Sonoma spineflower
Wherever
E
found
Chromolaena frustrata
Cape Sable thoroughwort
Wherever
E
found
Chrysopsis floridana
Florida golden aster
Cirsium fontinale var. fontinale
Fountain thistle
Cirsium fontinale var. obispoense
Chorro Creek bog thistle
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Cirsium hydrophilum var. hydrophilum Suisun thistle
Wherever
E
found
Cirsium loncholepis
La Graciosa thistle
Wherever
E
found
Cirsium pitcheri
Pitcher's thistle
Wherever
T
found
76 FR 15609,
5/5/2011;
50 CFR
17.99(a).CH
52 FR 2227,
1/21/1987.
65 FR 14878,
3/20/2000;
50 CFR
17.96(a).CH
57 FR 27848,
6/22/1992.
61 FR 52370,
10/7/1996.
59 FR 5499,
2/4/1994.
59 FR 5499,
2/4/1994;
50 CFR
17.96(a).CH
59 FR 5499,
2/4/1994;
50 CFR
17.96(a).CH
59 FR 5499,
2/4/1994;
50 CFR
17.96(b).CH
57 FR 27848,
6/22/1992.
78 FR 63795,
10/24/2013;
50 CFR
17.96(a);CH
50 CFR
17.96(h).CH
51 FR 17974,
5/16/1986.
60 FR 6671,
2/3/1995.
59 FR 64613,
12/15/1994.
62 FR 61916,
11/20/1997;
50 CFR
17.96(a).CH
65 FR 14888,
3/20/2000;
50 CFR
17.96(a).CH
53 FR 27137,
7/18/1988.
Cirsium vinaceum
Sacramento Mountains
thistle
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Clarkia franciscana
Presidio clarkia
Clarkia imbricata
Vine Hill clarkia
Clarkia speciosa ssp. immaculata
Pismo clarkia
Clarkia springvillensis
Springville clarkia
Clematis morefieldii
Morefield's leather-flower
Clematis socialis
Alabama leather-flower
Clermontia drepanomorpha
Oha wai
Wherever
E
found
Clermontia lindseyana
Oha wai
Wherever
E
found
Clermontia oblongifolia ssp. brevipes Oha wai
Wherever
E
found
Clermontia
oblongifolia ssp. mauiensis
Oha wai
Wherever
E
found
Clermontia peleana
Oha wai
Wherever
E
found
Clermontia pyrularia
Oha wai
Wherever
E
found
Clermontia samuelii
Oha wai
Wherever
E
found
Clitoria fragrans
Pigeon wings
Wherever
T
found
52 FR 22933,
6/16/1987.
60 FR 6671,
2/3/1995.
62 FR 54791,
10/22/1997.
59 FR 64613,
12/15/1994.
63 FR 49022,
9/14/1998.
57 FR 21562,
5/20/1992.
51 FR 34420,
9/26/1986.
61 FR 53137,
10/10/1996;
50 CFR
17.99(k).CH
59 FR 10305,
3/4/1994;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(k).CH
57 FR 46325,
10/8/1992;
50 CFR
17.99(c).CH
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1).CH
59 FR 10305,
3/4/1994;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(k).CH
59 FR 10305,
3/4/1994;
50 CFR
17.99(k).CH
64 FR 48307,
9/3/1999;
50 CFR
17.99(e)(1).CH
58 FR 25746,
4/27/1993.
Colubrina oppositifolia
Kauila
Conradina brevifolia
Short-leaved rosemary
Conradina etonia
Etonia rosemary
Conradina glabra
Apalachicola rosemary
Conradina verticillata
Cumberland rosemary
Consolea corallicola
Cactus, Florida semaphore
Cordia bellonis
No common name
Cordylanthus
maritimus ssp. maritimus
Salt marsh bird's-beak
Cordylanthus mollis ssp. mollis
Soft bird's-beak
Cordylanthus palmatus
Palmate-bracted bird's-beak
Cordylanthus tenuis ssp. capillaris
Pennell's bird's-beak
Cornutia obovata
Palo de nigua
Coryphantha minima
Nellie's cory cactus
Coryphantha ramillosa
Bunched cory cactus
Coryphantha robbinsorum
Cochise pincushion cactus
Coryphantha scheeri var. robustispina Pima pineapple cactus
Coryphantha sneedii var. leei
Lee pincushion cactus
Coryphantha sneedii var. sneedii
Sneed pincushion cactus
Cranichis ricartii
None
Crescentia portoricensis
Higuero de Sierra
Crotalaria avonensis
Avon Park harebells
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
T
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
59 FR 10305,
3/4/1994;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i);CH
50 CFR
17.99(k).CH
58 FR 37432,
7/12/1993.
58 FR 37432,
7/12/1993.
58 FR 37432,
7/12/1993.
56 FR 60937,
11/29/1991.
78 FR 63795,
10/24/2013;
50 CFR
17.96(a).CH
62 FR 1645,
1/10/1997.
43 FR 44810,
9/28/1978.
62 FR 61916,
11/20/1997;
50 CFR
17.96(a).CH
51 FR 23765,
7/1/1986.
60 FR 6671,
2/3/1995.
53 FR 11610,
4/7/1988.
44 FR 64738,
11/7/1979.
44 FR 64247,
11/6/1979.
51 FR 952,
1/9/1986.
58 FR 49875,
9/23/1993.
44 FR 61554,
10/25/1979.
44 FR 64741,
11/7/1979.
56 FR 60933,
11/29/1991.
52 FR 46085,
12/4/1987.
58 FR 25746,
4/27/1993.
Cryptantha crassipes
Terlingua Creek cats-eye
Cucurbita
Okeechobee gourd
okeechobeensis ssp. okeechobeensis
Wherever
E
found
Wherever
E
found
Cyanea acuminata
Haha
Wherever
E
found
Cyanea asarifolia
Haha
Wherever
E
found
Cyanea asplenifolia
Haha
Wherever
E
found
Cyanea calycina
Haha
Wherever
E
found
Cyanea copelandii ssp. copelandii
Haha
Wherever
E
found
Cyanea
copelandii ssp. haleakalaensis
Haha
Wherever
E
found
Cyanea crispa
Haha
Wherever
E
found
Cyanea dolichopoda
Haha
Wherever
E
found
Cyanea dunbariae
Haha
Wherever
E
found
Cyanea duvalliorum
Haha
Wherever
E
found
Cyanea eleeleensis
Haha
Wherever
E
found
Cyanea gibsonii
No common name
Wherever
E
found
Cyanea glabra
Haha
Wherever
E
found
56 FR 49634,
9/30/1991.
58 FR 37432,
7/12/1993.
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
59 FR 10305,
3/4/1994.
64 FR 48307,
9/3/1999;
50 CFR
17.99(e)(1).CH
59 FR 14482,
3/28/1994;
50 CFR
17.99(i).CH
76 FR 15609,
5/5/2011;
50 CFR
17.99(a).CH
61 FR 53130,
10/10/1996;
50 CFR
17.99(c).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
76 FR 15609,
5/5/2011;
50 CFR
17.99(a).CH
56 FR 47686,
9/20/1991.
64 FR 48307,
9/3/1999;
50 CFR
17.99(e)(1).CH
Cyanea grimesiana ssp. grimesiana
Haha
Wherever
E
found
Cyanea grimesiana ssp. obatae
Haha
Wherever
E
found
Cyanea hamatiflora ssp. carlsonii
Haha
Wherever
E
found
Cyanea hamatiflora ssp. hamatiflora Haha
Wherever
E
found
Cyanea horrida
Haha nui
Wherever
E
found
Cyanea humboltiana
Haha
Wherever
E
found
Cyanea kauaulaensis
No common name
Wherever
E
found
Cyanea kolekoleensis
Haha
Wherever
E
found
Cyanea koolauensis
Haha
Wherever
E
found
Cyanea kuhihewa
Haha
Wherever
E
found
Cyanea kunthiana
Haha
Wherever
E
found
Cyanea lanceolata
Haha
Wherever
E
found
61 FR 53108,
10/10/1996;
50 CFR
17.99(c);CH
50 CFR
17.99(i).CH
59 FR 32932,
6/27/1994;
78 FR 32013,
5/28/2013;
50 CFR
17.99(i).CH
59 FR 10305,
3/4/1994;
50 CFR
17.99(k).CH
64 FR 48307,
9/3/1999;
50 CFR
17.99(e)(1).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
81 FR 67786,
9/30/2016.
76 FR 15609,
5/5/2011;
50 CFR
17.99(a).CH
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
76 FR 15609,
5/5/2011;
50 CFR
17.99(a).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
Cyanea lobata
Haha
Wherever
E
found
Cyanea longiflora
Haha
Wherever
E
found
Cyanea magnicalyx
Haha
Wherever
E
found
Cyanea mannii
Haha
Wherever
E
found
Cyanea maritae
Haha
Wherever
E
found
Cyanea marksii
Haha
Cyanea mauiensis
Haha
Cyanea mceldowneyi
Haha
Wherever
E
found
Cyanea munroi
Haha
Wherever
E
found
Cyanea obtusa
Haha
Wherever
E
found
Cyanea pinnatifida
Haha
Wherever
E
found
Cyanea platyphylla
Haha
Wherever
E
found
Cyanea procera
Haha
Wherever
E
found
Cyanea profuga
Haha
Wherever
E
found
Wherever
E
found
Wherever
E
found
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1).CH
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
57 FR 46325,
10/8/1992;
50 CFR
17.99(c).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
78 FR 64637,
10/29/2013.
78 FR 32013,
5/28/2013.
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(c).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
61 FR 53137,
10/10/1996;
50 CFR
17.99(k).CH
57 FR 46325,
10/8/1992;
50 CFR
17.99(c).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(c).CH
Cyanea purpurellifolia
Haha
Wherever
E
found
Cyanea recta
Haha
Wherever
T
found
Cyanea remyi
Haha
Wherever
E
found
Cyanea shipmanii
Haha
Wherever
E
found
Cyanea solanacea
Popolo
Wherever
E
found
Cyanea st.-johnii
Haha
Wherever
E
found
Cyanea stictophylla
Haha
Wherever
E
found
Cyanea superba
No common name
Wherever
E
found
Cyanea tritomantha
Aku
Wherever
E
found
Cyanea truncata
Haha
Wherever
E
found
Cyanea undulata
No common name
Wherever
E
found
Cycladenia humilis var. jonesii
Jones cycladenia
Cycas micronesica
Fadang, Faadang
Cyperus fauriei
No common name
Wherever
E
found
Cyperus neokunthianus
No common name
Wherever
E
found
Wherever
T
found
Wherever
T
found
77 FR 57647,
9/18/2012.
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
59 FR 10305,
3/4/1994;
50 CFR
17.99(k).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(c).CH
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
59 FR 10305,
3/4/1994;
50 CFR
17.99(k).CH
56 FR 46235,
9/11/1991;
50 CFR
17.99(i).CH
78 FR 64637,
10/29/2013.
59 FR 14482,
3/28/1994;
50 CFR
17.99(i).CH
56 FR 47695,
9/20/1991;
50 CFR
17.99(a)(1).CH
51 FR 16526,
5/5/1986.
80 FR 59423,
10/1/2015.
59 FR 10305,
3/4/1994;
50 CFR
17.99(c);CH
50 CFR
17.99(k).CH
81 FR 67786,
9/30/2016.
Cyperus pennatiformis
No common name
Wherever
E
found
Cyperus trachysanthos
Puukaa
Wherever
E
found
Cyrtandra crenata
Ha`iwale
Wherever
E
found
Cyrtandra cyaneoides
Mapele
Wherever
E
found
Cyrtandra dentata
Haiwale
Wherever
E
found
Cyrtandra ferripilosa
Haiwale
Wherever
E
found
Cyrtandra filipes
Haiwale
Wherever
E
found
Cyrtandra giffardii
Haiwale
Wherever
E
found
Cyrtandra gracilis
Haiwale
Wherever
E
found
Cyrtandra hematos
Haiwale
Wherever
E
found
Cyrtandra kaulantha
Haiwale
Wherever
E
found
59 FR 56333,
11/10/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(g);CH
50 CFR
17.99(i).CH
61 FR 53108,
10/10/1996;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(i);CH
50 CFR
17.99(c).CH
59 FR 14482,
3/28/1994.
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1).CH
59 FR 10305,
3/4/1994;
50 CFR
17.99(k).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
81 FR 67786,
9/30/2016.
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
Cyrtandra limahuliensis
Haiwale
Wherever
T
found
Cyrtandra munroi
Haiwale
Wherever
E
found
Cyrtandra nanawaleensis
Haiwale
Wherever
E
found
Cyrtandra oenobarba
Haiwale
Wherever
E
found
Cyrtandra oxybapha
Haiwale
Wherever
E
found
Cyrtandra paliku
Haiwale
Wherever
E
found
Cyrtandra polyantha
Haiwale
Wherever
E
found
Cyrtandra sessilis
Haiwale
Wherever
E
found
Cyrtandra subumbellata
Haiwale
Wherever
E
found
Cyrtandra tintinnabula
Haiwale
Wherever
E
found
Cyrtandra viridiflora
Haiwale
Wherever
E
found
Cyrtandra wagneri
Haiwale
Wherever
E
found
Cyrtandra waiolani
Haiwale
Wherever
E
found
Dalea carthagenensis var. floridana
Florida prairie-clover
Dalea foliosa
Leafy prairie-clover
Wherever
E
found
Wherever
E
found
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1).CH
78 FR 64637,
10/29/2013.
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
59 FR 14482,
3/28/1994;
50 CFR
17.99(i).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
59 FR 10305,
3/4/1994;
50 CFR
17.99(k).CH
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
78 FR 64637,
10/29/2013.
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
82 FR 46691,
10/06/2017.
56 FR 19953,
5/1/1991.
Daphnopsis hellerana
No common name
Deeringothamnus pulchellus
Beautiful pawpaw
Deeringothamnus rugelii
Rugel's pawpaw
Wherever
E
found
Wherever
E
found
Wherever
E
found
Deinandra (= Hemizonia) conjugens Otay tarplant
Wherever
T
found
Deinandra increscens ssp. villosa
Gaviota tarplant
Wherever
E
found
Delissea rhytidosperma
No common name
Wherever
E
found
Delissea rivularis
Haha
Wherever
E
found
Delissea subcordata
Oha
Wherever
E
found
Delissea undulata
No common name
Wherever
E
found
Delphinium bakeri
Baker's larkspur
Wherever
E
found
Delphinium luteum
Yellow larkspur
Wherever
E
found
Delphinium variegatum ssp. kinkiense
San Clemente Island
larkspur
Dendrobium guamense
No common name
Dicerandra christmanii
Garrett's mint
Wherever
E
found
Dicerandra cornutissima
Longspurred mint
Wherever
E
found
Wherever
E
found
Wherever
T
found
53 FR 23740,
6/23/1988.
51 FR 34415,
9/26/1986.
51 FR 34415,
9/26/1986.
63 FR 54938,
10/13/1998;
50 CFR
17.96(a).CH
65 FR 14888,
3/20/2000;
50 CFR
17.96(a).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
61 FR 53070,
10/10/1996;
68 FR 9115,
2/27/2003;
50 CFR
17.99(a)(1).CH
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
61 FR 53124,
10/10/1996;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(k).CH
65 FR 4156,
1/26/2000;
50 CFR
17.96(a).CH
65 FR 4156,
1/26/2000;
50 CFR
17.96(a).CH
42 FR 40682,
8/11/1977.
80 FR 59423,
10/1/2015.
50 FR 45621,
11/1/1985;
54 FR 38946,
9/21/1989.
50 FR 45621,
11/1/1985.
Wherever
E
found
Dicerandra frutescens
Scrub mint
Dicerandra immaculata
Lakela's mint
Digitaria pauciflora
Florida crabgrass
Diplacus vandenbergensis
Vandenberg monkeyflower
Wherever
E
found
Dodecahema leptoceras
Slender-horned spineflower
Wherever
E
found
Dubautia herbstobatae
Naenae
Wherever
E
found
Dubautia imbricata ssp. imbricata
Naenae
Wherever
E
found
Dubautia kalalauensis
Naenae
Wherever
E
found
Dubautia kenwoodii
Naenae
Wherever
E
found
Dubautia latifolia
Koholapehu
Wherever
E
found
Dubautia pauciflorula
Naenae
Wherever
E
found
Dubautia plantaginea ssp. humilis
Naenae
Wherever
E
found
Dubautia plantaginea ssp. magnifolia Naenae
Wherever
E
found
Dubautia waialealae
Naenae
Wherever
E
found
Dudleya abramsii ssp. parva
Conejo dudleya
Wherever
T
found
Wherever
E
found
Wherever
T
found
50 FR 45621,
11/1/1985;
54 FR 38946,
9/21/1989.
50 FR 20212,
5/15/1985.
82 FR 46691,
10/06/2017.
79 FR 50844,
8/26/2014;
50 CFR
17.96(a).CH
52 FR 36265,
9/28/1987.
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
57 FR 20580,
5/13/1992;
50 CFR
17.99(a)(1).CH
56 FR 47695,
9/20/1991;
50 CFR
17.99(a)(1).CH
64 FR 48307,
9/3/1999;
50 CFR
17.99(e)(1).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
62 FR 4172,
1/29/1997.
Echinocactus
horizonthalonius var. nicholii
Echinocereus
chisoensis var. chisoensis
Wherever
T
found
Santa Monica Mountains
Wherever
T
dudleya
found
Wherever
Santa Cruz Island dudleya
T
found
Wherever
Santa Clara Valley dudleya
E
found
Wherever
Laguna Beach liveforever
T
found
Santa Barbara Island
Wherever
E
liveforever
found
Wherever
Verity's dudleya
T
found
Wherever
Smooth coneflower
E
found
Wherever
Nichol's Turk's head cactus
E
found
Wherever
Chisos hedgehog cactus
T
found
Echinocereus fendleri var. kuenzleri
Kuenzler hedgehog cactus
Dudleya cymosa ssp. marcescens
Dudleya cymosa ssp. ovatifolia
Dudleya nesiotica
Dudleya setchellii
Dudleya stolonifera
Dudleya traskiae
Dudleya verityi
Echinacea laevigata
Echinocereus
reichenbachii var. albertii
Echinocereus
triglochidiatus var. arizonicus
Marcescent dudleya
Black lace cactus
Arizona hedgehog cactus
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Echinocereus viridiflorus var. davisii
Davis's green pitaya
Echinomastus
erectocentrus var. acunensis
Acuña cactus
Wherever
E
found
Echinomastus mariposensis
Lloyd's Mariposa cactus
Wherever
T
found
Enceliopsis nudicaulis var. corrugata Ash Meadows sunray
Wherever
T
found
Eragrostis fosbergii
Wherever
E
found
Fosberg's love grass
Wherever
E
found
Wherever
Eriastrum densifolium ssp. sanctorum Santa Ana River woolly-star
E
found
Eremalche kernensis
Kern mallow
Erigeron decumbens
Willamette daisy
Wherever
E
found
62 FR 4172,
1/29/1997.
62 FR 4172,
1/29/1997.
62 FR 40954,
7/31/1997.
60 FR 6671,
2/3/1995.
63 FR 54938,
10/13/1998.
43 FR 17910,
4/26/1978.
62 FR 4172,
1/29/1997.
57 FR 46340,
10/8/1992.
44 FR 61927,
10/26/1979.
53 FR 38453,
9/30/1988.
44 FR 61924,
10/26/1979; 83
FR 21928,
5/11/2018.
44 FR 61918,
10/26/1979.
44 FR 61556,
10/25/1979.
44 FR 64738,
11/7/1979.
78 FR 60607,
10/1/2013;
50 CFR
17.96(a).CH
44 FR 64247,
11/6/1979.
50 FR 20777,
5/20/1985;
50 CFR
17.96(a).CH
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
55 FR 29361,
7/19/1990.
52 FR 36265,
9/28/1987.
65 FR 3875,
1/25/2000;
50 CFR
17.96.CH
Erigeron parishii
Parish's daisy
Erigeron rhizomatus
Zuni fleabane
Eriodictyon altissimum
Wherever
T
found
Wherever
T
found
Wherever
Indian Knob mountain balm
E
found
Eriodictyon capitatum
Lompoc yerba santa
Wherever
E
found
Eriogonum apricum
(incl. var. prostratum)
Ione (incl. Irish Hill)
buckwheat
Wherever
E
found
Eriogonum codium
Umtanum desert buckwheat
Wherever
T
found
Eriogonum gypsophilum
Gypsum wild-buckwheat
Wherever
T
found
Eriogonum
kennedyi var. austromontanum
Southern mountain wildbuckwheat
Wherever
T
found
Eriogonum
longifolium var. gnaphalifolium
Scrub buckwheat
Wherever
T
found
Eriogonum ovalifolium var. vineum
Cushenbury buckwheat
Wherever
E
found
Eriogonum ovalifolium var. williamsiaeSteamboat buckwheat
Wherever
E
found
Eriogonum pelinophilum
Clay-loving wild buckwheat
Wherever
E
found
Eriophyllum latilobum
San Mateo woolly sunflower
Eryngium aristulatum var. parishii
San Diego button-celery
Eryngium constancei
Loch Lomond coyote-thistle
Wherever
E
found
Eryngium cuneifolium
Snakeroot
Wherever
E
found
Wherever
E
found
Wherever
E
found
59 FR 43652,
8/24/1994;
50 CFR
17.96(a).CH
50 FR 16680,
4/26/1985.
59 FR 64613,
12/15/1994.
65 FR 14888,
3/20/2000;
50 CFR
17.96(a).CH
64 FR 28403,
5/26/1999.
78 FR 23983,
4/23/2013;
50 CFR
17.96(a).CH
46 FR 5730,
1/19/1981;
46 FR 40025,
8/6/1981;
50 CFR
17.96(a).CH
63 FR 49006,
9/14/1998;
50 CFR
17.96(a).CH
58 FR 25746,
4/27/1993.
59 FR 43652,
8/24/1994;
50 CFR
17.96(a).CH
51 FR 24669,
7/8/1986.
49 FR 28562,
7/13/1984;
50 CFR
17.96(a).CH
60 FR 6671,
2/3/1995.
58 FR 41384,
8/3/1993.
50 FR 31187,
8/1/1985;
51 FR 45904,
12/23/1986.
52 FR 2227,
1/21/1987.
Erysimum capitatum var. angustatum Contra Costa wallflower
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Erysimum menziesii
Menzies' wallflower
Erysimum teretifolium
Ben Lomond wallflower
Erythronium propullans
Minnesota dwarf trout lily
Eugenia bryanii
No common name
Eugenia haematocarpa
Uvillo
Eugenia koolauensis
Nioi
Wherever
E
found
Eugenia woodburyana
No common name
Wherever
E
found
Euphorbia (=Chamaesyce)
celastroides var. kaenana
Akoko
Wherever
E
found
Euphorbia (=Chamaesyce) deppeana Akoko
Wherever
E
found
Euphorbia (=Chamaesyce) eleanoriaeAkoko
Wherever
E
found
Euphorbia haeleeleana
Akoko
Wherever
E
found
Euphorbia (=Chamaesyce) halemanui Akoko
Wherever
E
found
43 FR 17910,
4/26/1978;
50 CFR
17.96(a).CH
57 FR 27848,
6/22/1992.
59 FR 5499,
2/4/1994.
51 FR 10521,
3/26/1986.
80 FR 59423,
10/1/2015.
59 FR 60565,
11/25/1994.
59 FR 14482,
3/28/1994;
50 CFR
17.99(c);CH
50 CFR
17.99(i).CH
59 FR 46715,
9/9/1994.
56 FR 55770,
10/29/1991;
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
59 FR 14482,
3/28/1994;
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
61 FR 53108,
10/10/1996;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(i).CH
57 FR 20580,
5/13/1992;
50 CFR
17.99(a)(1).CH
Euphorbia (=Chamaesyce) herbstii
Akoko
Wherever
E
found
Euphorbia (=Chamaesyce)
kuwaleana
Akoko
Wherever
E
found
Euphorbia (=Chamaesyce) remyivar .
Akoko
kauaiensis
Wherever
E
found
Euphorbia (=Chamaesyce) remyivar .
Akoko
remyi
Wherever
E
found
Euphorbia (=Chamaesyce) rockii
Akoko
Wherever
E
found
Euphorbia telephioides
Telephus spurge
Eutrema penlandii
Mosquito Range mustard
Exocarpos luteolus
Heau
Exocarpos menziesii
Heau
Festuca hawaiiensis
No common name
Festuca ligulata
Guadalupe fescue
Festuca molokaiensis
No common name
Wherever
T
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
61 FR 53089,
10/10/1996;
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
56 FR 55770,
10/29/1991;
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
76 FR 15609,
5/5/2011;
50 CFR
17.99(a).CH
76 FR 15609,
5/5/2011;
50 CFR
17.99(a).CH
61 FR 53089,
10/10/1996;
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
57 FR 19813,
5/8/1992.
58 FR 40539,
7/28/1993.
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
81 FR 67786,
9/30/2016.
81 FR 67786,
9/30/2016.
82 FR 42245,
9/7/2017.
78 FR 32013,
5/28/2013;
50 CFR
17.99(c).CH
Flueggea neowawraea
Mehamehame
Wherever
E
found
Fremontodendron
californicum ssp. decumbens
Pine Hill flannelbush
Wherever
E
found
Fremontodendron mexicanum
Mexican flannelbush
Wherever
E
found
Fritillaria gentneri
Gentner's fritillary
Galactia smallii
Small's milkpea
Galium buxifolium
Island bedstraw
Galium californicum ssp. sierrae
El Dorado bedstraw
Gardenia brighamii
Hawaiian gardenia (Na`u)
Gardenia mannii
Nanu
Gardenia remyi
Nanu
Geocarpon minimum
No common name
Geranium arboreum
Nohoanu
Wherever
E
found
Geranium hanaense
Nohoanu
Wherever
E
found
Geranium hillebrandii
Nohoanu
Wherever
E
found
Geranium kauaiense
Nohoanu
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
59 FR 56333,
11/10/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i);CH
50 CFR
17.99(k).CH
61 FR 54346,
10/18/1996.
63 FR 54956,
10/13/1998;
50 CFR
17.96(a).CH
64 FR 69195,
12/10/1999.
50 FR 29345,
7/18/1985.
62 FR 40954,
7/31/1997.
61 FR 54346,
10/18/1996.
50 FR 33728,
8/21/1985.
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
81 FR 67786,
9/30/2016.
52 FR 22930,
6/16/1987.
57 FR 20589,
5/13/1992;
50 CFR
17.99(e)(1).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
Geranium multiflorum
Nohoanu
Gesneria pauciflora
No common name
Geum radiatum
Gilia tenuiflora ssp. arenaria
Gilia tenuiflora ssp. hoffmannii
Goetzea elegans
Wherever
E
found
Wherever
T
found
Wherever
Spreading avens
E
found
Wherever
Monterey gilia
E
found
Hoffmann's slender-flowered Wherever
E
gilia
found
Beautiful goetzea or
Wherever
E
matabuey
found
Gonocalyx concolor
No common name
Wherever
E
found
Gouania hillebrandii
No common name
Wherever
E
found
Gouania meyenii
No common name
Wherever
E
found
Gouania vitifolia
No common name
Wherever
E
found
Grindelia fraxino-pratensis
Ash Meadows gumplant
Wherever
T
found
Hackelia venusta
Showy stickseed
Wherever
E
found
Halophila johnsonii
Johnson's seagrass
Wherever
T
found
Haplostachys haplostachya
No common name
Wherever
E
found
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1).CH
60 FR 12483,
3/7/1995.
55 FR 12793,
4/5/1990.
57 FR 27848,
6/22/1992.
62 FR 40954,
7/31/1997.
50 FR 15564,
4/19/1985.
79 FR 53303,
9/9/2014;
50 CFR
17.96(a).CH
49 FR 44753,
11/19/1984;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(e)(2);CH
50 CFR
17.96(a).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(i).CH
59 FR 32932,
6/27/1994;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(k).CH
50 FR 20777,
5/20/1985;
50 CFR
17.96(a).CH
67 FR 5515,
2/6/2002.
63 FR 49035,
9/14/1998;N
64 FR 28392,
5/26/1999;
50 CFR
226.213.CH
44 FR 62468,
10/30/1979.
Harperocallis flava
Harper's beauty
Wherever
E
found
Harrisia aboriginum
Prickly-apple, aboriginal
Wherever
E
found
Harrisia portoricensis
Higo chumbo
Wherever
T
found
Hedeoma todsenii
Todsen's pennyroyal
Wherever
E
found
Hedyotis cookiana
Awiwi
Wherever
E
found
Hedyotis megalantha
Pau dedu, Pao doodu
Hedyotis purpurea var. montana
Roan Mountain bluet
Helenium virginicum
Virginia sneezeweed
Helianthemum greenei
Island rush-rose
Helianthus paradoxus
Pecos (=puzzle, =paradox)
sunflower
Helianthus schweinitzii
Schweinitz's sunflower
Helianthus verticillatus
Whorled sunflower
Helonias bullata
Swamp pink
Heritiera longipetiolata
Ufa halumtanu, Ufa halom
tano
Hesperolinon congestum
Marin dwarf-flax
Hesperomannia arborescens
No common name
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
T
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
44 FR 56862,
10/2/1979.
78 FR 63795,
10/24/2013;
50 CFR
17.96(a).CH
55 FR 32252,
8/8/1990.
46 FR 5730,
1/19/1981;
46 FR 40025,
8/6/1981;
50 CFR
17.96(a).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
80 FR 59423,
10/1/2015.
55 FR 12793,
4/5/1990.
63 FR 59239,
11/3/1998.
62 FR 40954,
7/31/1997.
64 FR 56583,
10/20/1999;
50 CFR
17.96(a).CH
56 FR 21087,
5/7/1991.
79 FR 44712,
8/1/2014.
53 FR 35076,
9/9/1988.
80 FR 59423,
10/1/2015.
60 FR 6671,
2/3/1995.
59 FR 14482,
3/28/1994;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(c);CH
50 CFR
17.99(i).CH
Hesperomannia arbuscula
No common name
Wherever
E
found
Hesperomannia lydgatei
No common name
Wherever
E
found
Hexastylis naniflora
Dwarf-flowered heartleaf
Hibiscadelphus distans
Kauai hau kuahiwi
Hibiscadelphus giffardianus
Hau kuahiwi
Wherever
E
found
Hibiscadelphus hualalaiensis
Hau kuahiwi
Wherever
E
found
Hibiscadelphus woodii
Hau kuahiwi
Wherever
E
found
Hibiscus
arnottianus ssp. immaculatus
Kokio keokeo
Wherever
E
found
Hibiscus brackenridgei
Mao hau hele
Wherever
E
found
Hibiscus clayi
Clay's hibiscus
Wherever
E
found
Hibiscus dasycalyx
Neches River rose-mallow
Wherever
T
found
Wherever
T
found
Wherever
E
found
56 FR 55770,
10/29/1991;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
56 FR 47695,
9/20/1991;
50 CFR
17.99(a)(1).CH
54 FR 14964,
4/14/1989.
51 FR 15903;
4/29/1986.
61 FR 53137,
10/10/1996;
50 CFR
17.99(k).CH
61 FR 53137,
10/10/1996;
50 CFR
17.99(k).CH
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
57 FR 46325,
10/8/1992;
50 CFR
17.99(c).CH
59 FR 5633,
11/11/1994;
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(e)(2);CH
50 CFR
17.99(i);CH
50 CFR
17.99(k).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
78 FR 56025,
9/11/2013;
50 CFR
17.96(a).CH
Hibiscus waimeae ssp. hannerae
Kokio keokeo
Wherever
E
found
Hoffmannseggia tenella
Slender rush-pea
Wherever
E
found
Holocarpha macradenia
Santa Cruz tarplant
Wherever
T
found
Howellia aquatilis
Water howellia
Wherever
T
found
Hudsonia montana
Mountain golden heather
Wherever
T
found
Hymenoxys herbacea
Lakeside daisy
Hymenoxys texana
Texas prairie dawn-flower
Hypericum cumulicola
Highlands scrub hypericum
Ilex cookii
Cook's holly
Ilex sintenisii
None
Iliamna corei
Peter's Mountain mallow
Ipomopsis polyantha
Pagosa skyrocket
Ipomopsis sancti-spiritus
Holy Ghost ipomopsis
Iris lacustris
Dwarf lake iris
Ischaemum byrone
Hilo ischaemum
Wherever
E
found
Isodendrion hosakae
Aupaka
Wherever
T
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
50 FR 45621,
11/1/1985.
65 FR 14898,
3/20/2000;
50 CFR
17.96(a).CH
59 FR 35860,
7/14/1994.
45 FR 69360,
10/20/1980;
50 CFR
17.96(a).CH
53 FR 23742,
6/23/1988.
51 FR 8681,
3/13/1986.
52 FR 2227,
1/21/1987.
52 FR 22936,
6/16/1986.
57 FR 14782,
4/22/1992.
51 FR 17343,
5/12/1986.
76 FR 45053,
7/27/2011;
50 CFR
17.96(a).CH
59 FR 13836,
3/23/1994.
53 FR 37972,
9/28/1988.
59 FR 10305,
3/4/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(k).CH
56 FR 1454,
1/14/1991;
50 CFR
17.99(k).CH
Isodendrion laurifolium
Aupaka
Wherever
E
found
Isodendrion longifolium
Aupaka
Wherever
T
found
Isodendrion pyrifolium
Wahine noho kula
Wherever
E
found
Isotria medeoloides
Small whorled pogonia
Wherever
T
found
Ivesia kingii var. eremica
Ash Meadows ivesia
Wherever
T
found
Ivesia webberi
Webber's ivesia
Wherever
T
found
Wherever
E
found
Wherever
Jatropha costaricensis
Costa Rican jatropha
E
found
Wherever
Joinvillea ascendens ssp. ascendens Ohe
E
found
Wherever
Juglans jamaicensis
Nogal or West Indian walnut
E
found
Wherever
Justicia cooleyi
Cooley's water-willow
E
found
Wherever
Kadua cordata ssp. remyi
Kopa
E
found
Jacquemontia reclinata
Beach jacquemontia
Kadua coriacea
Kioele
Wherever
E
found
61 FR 53108,
10/10/1996;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(i).CH
61 FR 53108,
10/10/1996;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(i).CH
59 FR 10305,
3/4/1994;
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
47 FR 39827,
9/9/1982;
59 FR 50852,
10/6/1994.
50 FR 20777,
5/20/1985;
50 CFR
17.96(a).CH
79 FR 31878,
6/3/2014;
50 CFR
17.96(a).CH
58 FR 62046,
11/24/1993.
49 FR 30199,
7/27/1984.
81 FR 67786,
9/30/2016.
62 FR 1691,
1/13/1997.
54 FR 31190,
7/27/1989.
64 FR 48307,
9/3/1999.
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
Wherever
E
found
Kadua degeneri
No common name
Kadua fluviatilis
Kamapuaa
Kadua haupuensis
No common name
Kadua laxiflora
Pilo
Wherever
E
found
Kadua parvula
No common name
Wherever
E
found
Kadua (=Hedyotis) st.-johnii
No common name
Wherever
E
found
Kanaloa kahoolawensis
Kohe malama malama o
kanaloa
Wherever
E
found
Keysseria erici
No common name
Wherever
E
found
Keysseria helenae
No common name
Wherever
E
found
Kokia cookei
Cooke's koki`o
Wherever
E
found
Kokia drynarioides
Koki`o
Wherever
E
found
Kokia kauaiensis
Koki`o
Wherever
E
found
Korthalsella degeneri
Hulumoa
Wherever
E
found
Wherever
E
found
Wherever
E
found
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
81 FR 67786,
9/30/2016.
81 FR 67786,
9/30/2016.
57 FR 46325,
10/8/1992;
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
56 FR 49639,
9/30/1991;
50 CFR
17.99(a)(1).CH
64 FR 48307,
9/3/1999;
50 CFR
17.99(e)(2).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
44 FR 62470,
10/30/1979;
50 CFR
17.99(c).CH
49 FR 47397,
12/4/1984;
50 CFR
17.96(a).CH
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
Labordia cyrtandrae
Kamakahala
Wherever
E
found
Labordia helleri
Kamakahala
Wherever
E
found
Labordia lydgatei
Kamakahala
Wherever
E
found
Labordia pumila
Kamakahala
Wherever
E
found
Labordia tinifolia var. lanaiensis
Kamakahala
Labordia lorenciana
No common name
Labordia tinifolia var. wahiawaensis
Kamakahala
Wherever
E
found
Labordia triflora
Kamakahala
Wherever
E
found
Lasthenia burkei
Burke's goldfields
Wherever
E
found
Lasthenia conjugens
Contra Costa goldfields
Wherever
E
found
Layia carnosa
Beach layia
Leavenworthia crassa
fleshy-fruit gladecress
Leavenworthia exigua var.laciniata
Kentucky glade cress
Wherever
T
found
Leavenworthia texana
Texas golden gladecress
Wherever
E
found
Lembertia congdonii
San Joaquin wooly-threads
Lepanthes eltoroensis
No common name
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
56 FR 47695,
9/20/1991;
50 CFR
17.99(a)(1).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
64 FR 48307,
9/3/1999.
81 FR 67786,
9/30/2016.
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
64 FR 48307,
9/3/1999;
50 CFR
17.99(c).CH
56 FR 61173,
12/2/1991.
62 FR 33029,
6/18/1997;
50 CFR
17.96(a).CH
57 FR 27848,
6/22/1992.
79 FR 44712,
8/1/2014.
79 FR 25683,
5/6/2014;
50 CFR
17.96(a).CH
78 FR 56025,
9/11/2013;
50 CFR
17.96(a).CH
55 FR 29361,
7/19/1990.
56 FR 60933,
11/29/1991.
Lepidium arbuscula
Anaunau
Wherever
E
found
Lepidium barnebyanum
Barneby ridge-cress
Wherever
E
found
Lepidium papilliferum
Slickspot peppergrass
Wherever
T
found
Lepidium orbiculare
Anaunau
Leptocereus grantianus
No common name
Lespedeza leptostachya
Prairie bush-clover
Lesquerella congesta
Dudley Bluffs bladderpod
Lesquerella kingii ssp. bernardina
San Bernardino Mountains
bladderpod
Lesquerella lyrata
Lyrate bladderpod
Lesquerella pallida
White bladderpod
Lesquerella perforata
Spring Creek bladderpod
Lesquerella thamnophila
Zapata bladderpod
Lesquerella tumulosa
Kodachrome bladderpod
Lessingia germanorum (=L.
g. var. germanorum)
San Francisco lessingia
Liatris helleri
Heller's blazingstar
Liatris ohlingerae
Scrub blazingstar
Lilaeopsis schaffneriana var. recurva Huachuca water-umbel
Lilium occidentale
Western lily
Lilium pardalinum ssp. pitkinense
Pitkin Marsh lily
Limnanthes floccosa ssp. californica Butte County meadowfoam
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
T
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
55 FR 39860,
9/28/1990.
74 FR 52013,
10/8/2009;
81 FR 55058,
8/17/2016.
81 FR 67786,
9/30/2016.
58 FR 11550,
2/26/1993.
52 FR 781,
1/9/1987.
55 FR 4152,
2/6/1990.
59 FR 43652,
8/24/1994;
50 CFR
17.96(a).CH
55 FR 39864,
9/28/1990.
52 FR 7424,
3/11/1987.
61 FR 67493,
12/23/1996.
64 FR 63745,
11/22/1999;
50 CFR
17.96(a).CH
58 FR 52027,
10/6/1993.
62 FR 33368,
6/19/1997.
52 FR 44397,
11/19/1987.
54 FR 31190,
7/27/1989.
62 FR 665,
1/6/1997;
50 CFR
17.96(a).CH
59 FR 42171,
8/17/1994.
62 FR 54791,
10/22/1997.
57 FR 24192,
6/8/1992;
50 CFR
17.96(a).CH
large-flowered woolly
Limnanthes floccosa ssp. grandiflora
meadowfoam
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Limnanthes vinculans
Sebastopol meadowfoam
Lindera melissifolia
Pondberry
Linum arenicola
Sand flax
Linum carteri var. carteri
Carter's small-flowered flax
Wherever
E
found
Lipochaeta fauriei
Nehe
Wherever
E
found
Lipochaeta lobata var. leptophylla
Nehe
Wherever
E
found
Lipochaeta micrantha
Nehe
Wherever
E
found
Lipochaeta venosa
No common name
Wherever
E
found
Lipochaeta waimeaensis
Nehe
Wherever
E
found
Lithophragma maximum
San Clemente Island
woodland-star
Wherever
E
found
Lobelia
(gaudichaudii ssp.) koolauensis
No common name
Wherever
E
found
Lobelia monostachya
No common name
Wherever
E
found
Lobelia niihauensis
No common name
Wherever
E
found
Lobelia oahuensis
No common name
Wherever
E
found
67 FR 68004,
11/7/2002;
50 CFR
17.96(a).CH
56 FR 61173,
12/2/1991.
51 FR 27495,
7/31/1986.
81 FR 66842,
9/29/2016.
79 FR 52567,
9/4/2014;
50 CFR
17.96(a).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
44 FR 62468,
10/30/1979.
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
62 FR 42692,
8/8/1997.
61 FR 53089,
10/10/1996;
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
59 FR 14482,
3/28/1994;
50 CFR
17.99(i).CH
Lomatium bradshawii
Bradshaw's desert-parsley
Wherever
E
found
Lomatium cookii
Cook's lomatium (Cook's
desert parsley)
Wherever
E
found
Lupinus aridorum
Scrub lupine
Lupinus nipomensis
Nipomo Mesa lupine
Lupinus sulphureus ssp. kincaidii
Kincaid's lupine
Lupinus tidestromii
Clover lupine
Lyonia truncata var. proctorii
No common name
Lysimachia asperulaefolia
Rough-leaved loosestrife
Lysimachia daphnoides
Lehua makanoe
Wherever
E
found
Lysimachia filifolia
No common name
Wherever
E
found
Lysimachia iniki
No common name
Wherever
E
found
Lysimachia lydgatei
No common name
Wherever
E
found
Lysimachia maxima
No common name
Wherever
E
found
Lysimachia pendens
No common name
Wherever
E
found
Lysimachia scopulensis
No common name
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
53 FR 38448,
9/30/1988.
67 FR 68004,
11/7/2002;
50 CFR
17.96(a).CH
52 FR 11172,
4/7/1987.
65 FR 14888,
3/20/2000.
65 FR 3875,
3/25/2000;
50 CFR
17.96.CH
57 FR 27848,
6/22/1992.
58 FR 25755,
4/27/1993.
52 FR 22585,
6/12/1987.
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(i).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1).CH
61 FR 53130,
10/10/1996;
50 CFR
17.99(c).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
Lysimachia venosa
No common name
Macbridea alba
White birds-in-a-nest
Maesa walkeri
No common name
Malacothamnus clementinus
Malacothamnus
fasciculatus var. nesioticus
Malacothrix indecora
San Clemente Island bushmallow
Santa Cruz Island
bushmallow
Santa Cruz Island
malacothrix
Wherever
E
found
Wherever
T
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Malacothrix squalida
Island malacothrix
Manihot walkerae
Walker's manioc
Marshallia mohrii
Mohr's Barbara's buttons
Melanthera kamolensis
Nehe
Wherever
E
found
Melanthera tenuifolia
Nehe
Wherever
E
found
Melicope adscendens
Alani
Wherever
E
found
Melicope balloui
Alani
Wherever
E
found
Melicope christophersenii
Alani
Wherever
E
found
Melicope degeneri
Alani
Wherever
E
found
Melicope haupuensis
Alani
Wherever
E
found
Melicope hiiakae
Alani
Wherever
E
found
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
57 FR 19813,
5/8/1992.
80 FR 59423,
10/1/2015.
42 FR 40682,
8/11/1977.
62 FR 40954,
7/31/1997.
62 FR 40954,
7/31/1997.
62 FR 40954,
7/31/1997.
56 FR 49850,
10/2/1991.
53 FR 34698,
9/7/1988.
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
59 FR 62346,
12/5/1994;
50 CFR
17.99(e)(1).CH
59 FR 62346,
12/5/1994;
50 CFR
17.99(e)(1).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
Melicope knudsenii
Alani
Wherever
E
found
Melicope lydgatei
Alani
Wherever
E
found
Melicope makahae
Alani
Wherever
E
found
Melicope mucronulata
Alani
Wherever
E
found
Melicope munroi
Alani
Wherever
E
found
Melicope ovalis
Alani
Wherever
E
found
Melicope pallida
Alani
Wherever
E
found
Melicope paniculata
Alani
Wherever
E
found
Melicope puberula
Alani
Wherever
E
found
Melicope quadrangularis
Alani
Wherever
E
found
Melicope reflexa
Alani
Wherever
E
found
Melicope saint-johnii
Alani
Wherever
E
found
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(e)(1).CH
59 FR 14482,
3/28/1994;
50 CFR
17.99(i).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
57 FR 20772,
5/15/1992;
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1).CH
64 FR 48307,
9/3/1999;
50 CFR
17.99(c).CH
59 FR 62346,
12/5/1994;
50 CFR
17.99(e)(1).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(i).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
59 FR 9304,
2/25/1994.
57 FR 46325,
10/8/1992;
50 CFR
17.99(c).CH
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
Melicope zahlbruckneri
Alani
Wherever
E
found
Mentzelia leucophylla
Ash Meadows blazing-star
Wherever
T
found
Mezoneuron kavaiense
Uhi uhi
Wherever
E
found
Mimulus michiganensis (=Mimulus
glabratus var. michiganensis )
Michigan monkey-flower
Wherever
E
found
Mirabilis macfarlanei
MacFarlane's four-o'clock
Wherever
T
found
Mitracarpus maxwelliae
No common name
Mitracarpus polycladus
No common name
Monardella viminea
Willowy monardella
Wherever
E
found
Mucuna sloanei var.persericea
Sea bean
Wherever
E
found
Myrcia paganii
No common name
Myrsine fosbergii
Kolea
Myrsine juddii
Kolea
Wherever
E
found
Myrsine knudsenii
Kolea
Wherever
E
found
Myrsine linearifolia
Kolea
Wherever
T
found
Myrsine mezii
Kolea
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
61 FR 53137,
10/10/1996;
50 CFR
17.99(k).CH
50 FR 20777,
5/20/1985;
50 CFR
17.96(a).CH
51 FR 24672,
7/8/1986.
55 FR 25596,
6/21/1990;
75 FR 55686,
9/14/2010.
44 FR 61912,
10/26/1979;
61 FR 10693,
3/15/1996.
59 FR 46715,
9/9/1994.
59 FR 46715,
9/9/1994.
63 FR 54938,
10/13/1998;
50 CFR
17.96(a).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
59 FR 8138,
2/18/1994.
81 FR 67786,
9/30/2016.
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
63 FR 54975,
10/13/1998;
50 CFR
17.96(a).CH
Myrsine vaccinioides
Kolea
Wherever
E
found
Navarretia fossalis
Spreading navarretia
Wherever
T
found
Few-flowered navarretia
Wherever
E
found
62 FR 33029,
6/18/1997.
Many-flowered navarretia
Wherever
E
found
Neostapfia colusana
Colusa grass
Wherever
T
found
Neraudia angulata
No common name
Wherever
E
found
Neraudia ovata
No common name
Wherever
E
found
Neraudia sericea
No common name
Wherever
E
found
Nervilia jacksoniae
No common name
Nesogenes rotensis
No common name
Nitrophila mohavensis
Amargosa niterwort
Wherever
E
found
Nolina brittoniana
Britton's beargrass
Wherever
E
found
Nothocestrum breviflorum
Aiea
Wherever
E
found
Nothocestrum latifolium
Aiea
Wherever
E
found
Nothocestrum peltatum
Aiea
Wherever
E
found
62 FR 33029,
6/18/1997.
62 FR 14338,
3/26/1997;
50 CFR
17.96(a).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
61 FR 53137,
10/10/1996;
50 CFR
17.99(k).CH
59 FR 56333,
11/10/1994;
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(e)(2).CH
80 FR 59423,
10/1/2015.
69 FR 10335,
3/5/2004.
50 FR 20777,
5/20/1985;
50 CFR
17.96(a).CH
58 FR 25746,
4/27/1993.
59 FR 10305,
3/4/1994;
50 CFR
17.99(k).CH
81 FR 67786,
9/30/2016.
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
Navarretia
leucocephala ssp. pauciflora (=N.
pauciflora)
Navarretia
leucocephala ssp. plieantha
Wherever
T
found
Wherever
E
found
Wherever
E
found
Nototrichium humile
Kului
Ochrosia haleakalae
Holei
Ochrosia kilaueaensis
Holei
Oenothera deltoides ssp. howellii
Antioch Dunes eveningprimrose
Opuntia treleasei
Bakersfield cactus
Orcuttia californica
California Orcutt grass
Orcuttia inaequalis
San Joaquin Valley Orcutt
grass
Wherever
T
found
Orcuttia pilosa
Hairy Orcutt grass
Wherever
T
found
Orcuttia tenuis
Slender Orcutt grass
Wherever
T
found
Orcuttia viscida
Sacramento Orcutt grass
Wherever
T
found
Osmoxylon mariannense
No common name
Ottoschulzia rhodoxylon
Palo de rosa
Oxypolis canbyi
Canby's dropwort
Oxytheca parishii var. goodmaniana
Cushenbury oxytheca
Wherever
E
found
Oxytropis campestris var. chartacea
Fassett's locoweed
Wherever
T
found
Panicum fauriei var. carteri
Carter's panicgrass
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
56 FR 55770,
10/29/1991;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
81 FR 67786,
9/30/2016.
59 FR 10305,
3/4/1994.
43 FR 17910,
4/26/1978;
50 CFR
17.96(a).CH
55 FR 29361,
7/19/1990.
58 FR 41384,
8/3/1993.
62 FR 14338,
3/26/1997;
50 CFR
17.96(a).CH
62 FR 14338,
3/26/1997;
50 CFR
17.96(a).CH
62 FR 14338,
3/26/1997;
50 CFR
17.96(a).CH
62 FR 14338,
3/26/1997;
50 CFR
17.96(a).CH
69 FR 10335,
3/5/2004.
55 FR 13488,
4/10/1990.
51 FR 6690,
2/25/1986.
59 FR 43652,
8/24/1994;
50 CFR
17.96(a).CH
53 FR 37970,
9/28/1988.
48 FR 46328,
10/12/1983;
50 CFR
17.96(a).CH
Wherever
E
found
Panicum niihauense
Lau ehu
Paronychia chartacea
Papery whitlow-wort
Parvisedum leiocarpum
Lake County stonecrop
Pedicularis furbishiae
Furbish lousewort
Pediocactus bradyi
Brady pincushion cactus
Pediocactus despainii
San Rafael cactus
Pediocactus knowltonii
Knowlton cactus
Pediocactus
peeblesianus var. fickeiseniae
Fickeisen plains cactus
Pediocactus
peeblesianus var. fickeiseniae
Fickeisen plains cactus
Wherever
E
found
Pediocactus sileri
Siler pincushion cactus
Wherever
T
found
Pediocactus winkleri
Winkler cactus
Wherever
T
found
Penstemon debilis
Parachute beardtongue
Wherever
T
found
Penstemon haydenii
Blowout penstemon
Penstemon penlandii
Kremmling beardtongue
Pentachaeta bellidiflora
White-rayed pentachaeta
Pentachaeta lyonii
Lyon's pentachaeta
Wherever
E
found
Peperomia subpetiolata
Alaala wai nui
Wherever
E
found
Peperomia wheeleri
Wheeler's peperomia
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
61 FR 53108,
10/10/1996;
50 CFR
17.99(a)(1).CH
52 FR 2227,
1/21/1987.
62 FR 33029,
6/18/1997.
43 FR 17910,
4/26/1978.
44 FR 61784,
10/26/1979.
52 FR 34914,
9/16/1987.
44 FR 62244,
10/29/1979.
78 FR 60607,
10/1/2013.
78 FR 60607,
10/1/2013;
50 CFR
17.96(a).CH
44 FR 61786,
10/26/1979;
58 FR 68476,
12/27/1993.
63 FR 44587,
8/20/1998.
76 FR 45053,
7/27/2011;
50 CFR
17.96(a).CH
52 FR 32926,
9/1/1987.
54 FR 29658,
7/13/1989.
60 FR 6671,
2/3/1995.
62 FR 4172,
1/29/1997;
50 CFR
17.96(a).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
52 FR 1459,
1/14/1987.
Wherever
T
found
Peucedanum sandwicense
Makou
Phacelia argillacea
Clay phacelia
Phacelia formosula
North Park phacelia
Phacelia insularis ssp. insularis
Island phacelia
Phacelia submutica
DeBeque phacelia
Phlox hirsuta
Yreka phlox
Phlox nivalis ssp. texensis
Texas trailing phlox
Phyllanthus saffordii
No common name
Phyllostegia bracteata
No common name
Phyllostegia brevidens
No common name
Phyllostegia floribunda
No common name
Phyllostegia glabra var. lanaiensis
No common name
Phyllostegia haliakalae
No common name
Wherever
E
found
Phyllostegia helleri
No common name
Wherever
E
found
Phyllostegia hirsuta
No common name
Wherever
E
found
Phyllostegia hispida
No common name
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
43 FR 44810,
9/28/1978.
47 FR 38540,
9/1/1982.
62 FR 40954,
7/31/1997.
76 FR 45053,
7/27/2011;
50 CFR
17.96(a).CH
65 FR 5268,
2/3/2000.
56 FR 49636,
9/30/1991.
80 FR 59423,
10/1/2015.
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
81 FR 67786,
9/30/2016.
78 FR 64637,
10/29/2013.
56 FR 47686,
9/20/1991.
78 FR 32013,
5/28/2013;
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1).CH
81 FR 67786,
9/30/2016.
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
74 FR 11319,
3/17/2009;
50 CFR
17.99(c).CH
Phyllostegia kaalaensis
No common name
Wherever
E
found
Phyllostegia knudsenii
No common name
Wherever
E
found
Phyllostegia mannii
No common name
Wherever
E
found
Phyllostegia mollis
No common name
Wherever
E
found
Phyllostegia parviflora
No common name
Wherever
E
found
Phyllostegia pilosa
No common name
Wherever
E
found
Phyllostegia racemosa
Kiponapona
Wherever
E
found
Phyllostegia renovans
No common name
Wherever
E
found
Phyllostegia stachyoides
No common name
Wherever
E
found
Phyllostegia velutina
No common name
Wherever
E
found
Phyllostegia waimeae
No common name
Wherever
E
found
Phyllostegia warshaueri
No common name
Wherever
E
found
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
57 FR 46325,
10/8/1992;
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(e)(1)CH;
50 CFR
17.99(i).CH
61 FR 53108,
10/10/1996;
50 CFR
17.99(i).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1).CH
61 FR 53137,
10/10/1996;
50 CFR
17.99(k).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
81 FR 67786,
9/30/2016.
61 FR 53137,
10/10/1996;
50 CFR
17.99(k).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
61 FR 53137,
10/10/1996;
50 CFR
17.99(k).CH
Phyllostegia wawrana
No common name
Wherever
E
found
Physaria
douglasii subsp. tuplashensis
White Bluffs bladderpod
Wherever
T
found
Physaria filiformis (= Lesquerella f.)
Missouri bladderpod
Wherever
T
found
Physaria globosa
Short's bladderpod
Physaria obcordata
Dudley Bluffs twinpod
Pilosocereus robinii
Key tree-cactus
Pinguicula ionantha
Godfrey's butterwort
Piperia yadonii
Yadon's piperia
Wherever
E
found
Pittosporum halophilum
Hoawa
Wherever
E
found
Pittosporum hawaiiense
Hoawa, haawa
Wherever
E
found
Pittosporum napaliense
Hoawa
Wherever
E
found
Pityopsis ruthii
Ruth's golden aster
Plagiobothrys hirtus
Rough popcornflower
Plagiobothrys strictus
Calistoga allocarya
Plantago hawaienis
Laukahi kuahiwi
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
78 FR 23983,
4/23/2013;
50 CFR
17.96(a).CH
52 FR 679,
1/8/1987;
68 FR 59337,
10/15/2003;
75 FR 55686,
9/14/2010.
79 FR 44712,
8/1/2014.
55 FR 4152,
2/6/1990.
49 FR 29234,
7/19/1984.
58 FR 37432,
7/12/1993.
63 FR 43100,
8/12/1998;
50 CFR
17.96(a).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(c).CH
78 FR 64637,
10/29/2013.
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
50 FR 29341,
7/18/1985.
65 FR 3866,
1/25/2000.
62 FR 54791,
10/22/1997.
59 FR 10305,
3/4/1994;
50 CFR
17.99(k).CH
Plantago princeps
Laukahi kuahiwi
Wherever
E
found
Platanthera holochila
No common name
Wherever
E
found
Platanthera integrilabia
White fringeless orchid
Platanthera leucophaea
Platanthera praeclara
Wherever
T
found
Wherever
Eastern prairie fringed orchid
T
found
Western prairie fringed
Wherever
T
orchid
found
Platydesma cornuta var. cornuta
No common name
Wherever
E
found
Platydesma cornuta var. decurrens
No common name
Wherever
E
found
Platydesma remyi
No common name
Wherever
E
found
Platydesma rostrata
Pilo kea lau lii
Wherever
E
found
Pleodendron macranthum
Chupacallos
Pleomele fernaldii
Hala pepe
Pleomele forbesii
Hala pepe
Wherever
E
found
Pleomele hawaiiensis
Hala pepe
Wherever
E
found
Wherever
E
found
Wherever
E
found
59 FR 56333,
11/10/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
61 FR 53108,
10/10/1996;
50 CFR
17.99(c);CH
50 CFR
17.99(a)(1);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
81 FR 62826,
9/13/16.
54 FR 39857,
9/28/1989.
54 FR 39857,
9/28/1989.
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
78 FR 64637,
10/29/2013.
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
59 FR 60565,
11/25/1994.
78 FR 32013,
5/28/2013.
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
61 FR 53137,
10/10/1996;
50 CFR
17.99(k).CH
Poa atropurpurea
San Bernardino bluegrass
Wherever
E
found
Poa mannii
Mann's bluegrass
Wherever
E
found
Poa napensis
Napa bluegrass
Wherever
E
found
Poa sandvicensis
Hawaiian bluegrass
Wherever
E
found
Poa siphonoglossa
No common name
Wherever
E
found
Pogogyne abramsii
San Diego mesa mint
Pogogyne nudiuscula
Otay mesa mint
Polygala lewtonii
Lewton's polygala
Polygala smallii
Tiny polygala
Polygonella basiramia
Wireweed
Polygonella myriophylla
Sandlace
Polygonum hickmanii
Scotts Valley polygonum
Wherever
E
found
Polyscias (=Tetraplasandra)
bisattenuata
No common name
Wherever
E
found
Polyscias (=Tetraplasandra) flynnii
No common name
Wherever
E
found
Polyscias (=Tetraplasandra)
gymnocarpa
Oheohe
Wherever
E
found
Polyscias (=Tetraplasandra) lydgatei No common name
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
63 FR 49006,
9/14/1998;
50 CFR
17.96(a).CH
59 FR 56330,
11/10/1994;
50 CFR
17.99(a)(1).CH
62 FR 54791,
10/22/1997.
57 FR 20580,
5/13/1992;
50 CFR
17.99(a)(1).CH
57 FR 20580,
5/13/1992;
50 CFR
17.99(a)(1).CH
43 FR 44810,
9/28/1978.
58 FR 41384,
8/3/1993.
58 FR 25746,
4/27/1993.
50 FR 29345,
7/18/1985.
52 FR 2227,
1/21/1987.
58 FR 25746,
4/27/1993.
68 FR 16979,
4/8/2003;
50 CFR
17.96(a).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
59 FR 14482,
3/28/1994;
50 CFR
17.99(i).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
Polyscias (=Munroidendron)
racemosa (=racemosum)
No common name
Wherever
E
found
Portulaca sclerocarpa
Poe
Wherever
E
found
Portulaca villosa
Ihi
Potamogeton clystocarpus
Little Aguja pondweed
Potentilla hickmanii
Hickman's potentilla
Primula maguirei
Maguire primrose
Pritchardia affinis
Loulu
Pritchardia aylmer-robinsonii
Wahane
Pritchardia bakeri
Baker's loulu
Pritchardia hardyi
Loulu
Pritchardia kaalae
Loulu
Pritchardia lanigera
Loulu
Pritchardia maideniana
Loulu
Pritchardia munroi
Loulu
Pritchardia napaliensis
Loulu
Pritchardia remota
Loulu
Pritchardia schattaueri
Loulu
Pritchardia viscosa
Prunus geniculata
Pseudobahia bahiifolia
Pseudobahia
Pseudognaphalium
sandwicensiumvar. molokaiense
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
Loulu
E
found
Wherever
Scrub plum
E
found
Wherever
Hartweg's golden sunburst
E
found
Wherever
San Joaquin adobe sunburst
T
found
Wherever
Enaena
E
found
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
59 FR 10305,
3/4/1994;
50 CFR
17.99(k).CH
81 FR 67786,
9/30/2016.
56 FR 57844,
11/14/1991.
63 FR 43100,
8/12/1998.
50 FR 33731,
8/21/1985.
59 FR 10305,
3/4/1994.
61 FR 41020,
8/7/1996.
81 FR 67786,
9/30/2016.
75 FR 18960,
4/13/2010.
61 FR 53089,
10/10/1996.
78 FR 64637,
10/29/2013.
59 FR 10305,
3/4/1994.
57 FR 46325,
10/8/1992.
61 FR 53070,
10/10/1996.
61 FR 43178,
8/21/1996;
50 CFR
17.99(g).CH
61 FR 53137,
10/10/1996.
61 FR 53070,
10/10/1996.
52 FR 2227,
1/21/1987.
62 FR 5542,
2/6/1997.
62 FR 5542,
2/6/1997.
81 FR 67786,
9/30/2016.
Kopiko
Wherever
E
found
Psychotria hexandra ssp. oahuensis Kopiko
Wherever
E
found
Psychotria hobdyi
Kopiko
Wherever
E
found
Psychotria malaspinae
Aplokating palaoan
Wherever
E
found
Pteralyxia kauaiensis
Kaulu
Wherever
E
found
Pteralyxia macrocarpa
Kaulu
Wherever
E
found
Ptilimnium nodosum
Harperella
Purshia subintegra
Arizona cliffrose
Quercus hinckleyi
Hinckley's oak
Psychotria grandiflora
Ranunculus acriformis var. aestivalis Autumn buttercup
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Ranunculus hawaiensis
Makou
Ranunculus mauiensis
Makou
Remya kauaiensis
No common name
Wherever
E
found
Remya mauiensis
Maui remya
Wherever
E
found
Remya montgomeryi
No common name
Wherever
E
found
Rhodiola integrifolia ssp. leedyi (=
Sedum integrifolium ssp. l. )
Leedy's roseroot
Wherever
T
found
Rhododendron chapmanii
Chapman rhododendron
Wherever
E
found
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
80 FR 59423,
10/1/2015.
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
53 FR 37978,
9/28/1988.
49 FR 22326,
5/29/1984.
53 FR 32824,
8/26/1988.
54 FR 30550,
7/21/1989.
81 FR 67786,
9/30/2016.
81 FR 67786,
9/30/2016.
56 FR 1450,
1/14/1991;
50 CFR
17.99(a)(1).CH
56 FR 1450,
1/14/1991;
50 CFR
17.99(e)(1).CH
56 FR 1450,
1/14/1991;
50 CFR
17.99(a)(1).CH
57 FR 14649,
4/22/1992;
75 FR 55686,
9/14/2010.
44 FR 24248,
4/24/1979.
Wherever
E
found
Wherever
T
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Rhus michauxii
Michaux's sumac
Rhynchospora knieskernii
Knieskern's beaked-rush
Ribes echinellum
Miccosukee gooseberry
Rorippa gambellii
Gambel's watercress
Sagittaria fasciculata
Bunched arrowhead
Sagittaria secundifolia
Kral's water-plantain
Sanicula mariversa
No common name
Wherever
E
found
Sanicula purpurea
No common name
Wherever
E
found
Sanicula sandwicensis
No common name
Wherever
E
found
Santalum haleakalae var.lanaiense
Lanai sandalwood or iliahi
Wherever
E
found
Santalum involutum
Iliahi
Wherever
E
found
Sarracenia oreophila
Green pitcher-plant
Wherever
E
found
Sarracenia rubra ssp. alabamensis
Sarracenia rubra ssp. jonesii
Scaevola coriacea
Alabama canebrake pitcher- Wherever
E
plant
found
Wherever
Mountain sweet pitcher-plant
E
found
Wherever
Dwarf naupaka
E
found
54 FR 39850,
9/28/1989.
56 FR 32978,
7/18/1991.
50 FR 29338,
7/18/1985.
58 FR 41378,
8/3/1993.
44 FR 43700,
7/25/1979.
55 FR 13907,
4/13/1990.
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
61 FR 53108,
10/10/1996;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
81 FR 67786,
9/30/2016.
51 FR 3182,
1/24/1986;
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(c).CH
81 FR 67786,
9/30/2016.
44 FR 54922,
9/21/1979;
45 FR 18929,
3/24/1980.
54 FR 10150,
3/10/1989.
53 FR 38470,
9/30/1988.
51 FR 17971,
5/16/1986.
Schenkia sebaeoides
Awiwi
Wherever
E
found
Schiedea adamantis
Diamond Head schiedea
Wherever
E
found
Schiedea apokremnos
Maolioli
Wherever
E
found
Schiedea attenuata
No common name
Wherever
E
found
Schiedea diffusa ssp. diffusa
No common name
Schiedea diffusa ssp.macraei
No common name
Schiedea haleakalensis
No common name
Wherever
E
found
Schiedea hawaiiensis
No common name
Wherever
E
found
Schiedea helleri
No common name
Wherever
E
found
Schiedea hookeri
No common name
Wherever
E
found
Schiedea jacobii
No common name
Wherever
E
found
Schiedea kaalae
No common name
Wherever
E
found
Schiedea kauaiensis
No common name
Wherever
E
found
Wherever
E
found
Wherever
E
found
56 FR 55770,
10/29/1991;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
49 FR 6099,
2/17/1984.
56 FR 49639,
9/30/1991;
50 CFR
17.99(a)(1).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
81 FR 67786,
9/30/2016.
78 FR 64637,
10/29/2013.
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1).CH
78 FR 64637,
10/29/2013.
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
61 FR 53108,
10/10/1996;
50 CFR
17.99(i).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
61 FR 53108,
10/10/1996;
50 CFR
17.99(a)(1).CH
Schiedea kealiae
Maolioli
Wherever
E
found
Schiedea laui
No common name
Wherever
E
found
Schiedea (=Alsinidendron) lychnoides Kuawawaenohu
Wherever
E
found
Schiedea lydgatei
No common name
Wherever
E
found
Schiedea membranacea
No common name
Wherever
E
found
Schiedea nuttallii
No common name
Wherever
E
found
Schiedea obovata
No common name
Wherever
E
found
Schiedea pubescens
Maolioli
Wherever
E
found
Schiedea salicaria
No common name
Wherever
E
found
Schiedea sarmentosa
No common name
Wherever
E
found
Schiedea spergulina var. leiopoda
No common name
Wherever
E
found
Schiedea spergulina var. spergulina
No common name
Wherever
T
found
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(c).CH
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
57 FR 46325,
10/8/1992;
50 CFR
17.99(c).CH
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
61 FR 53108,
10/10/1996;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c);CH
50 CFR
17.99(i).CH
56 FR 55770,
10/29/1991;
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
81 FR 67786,
9/30/2016.
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
61 FR 53130,
10/10/1996;
50 CFR
17.99(c).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
Schiedea stellarioides
Laulihilihi (=Maolioli)
Wherever
E
found
Schiedea trinervis
No common name
Wherever
E
found
Schiedea verticillata
No common name
Wherever
E
found
Schiedea (=Alsinidendron) viscosa
(=viscosum)
No common name
Wherever
E
found
Schoenocrambe argillacea
Clay reed-mustard
Schoenocrambe barnebyi
Barneby reed-mustard
Schoenocrambe suffrutescens
Shrubby reed-mustard
Schoepfia arenaria
None
Schwalbea americana
American chaffseed
Scirpus ancistrochaetus
Northeastern bulrush
Sclerocactus brevihamatus ssp.
tobuschii
Tobusch fishhook cactus
Wherever
T
found
Sclerocactus brevispinus
Pariette cactus
Wherever
T
found
Sclerocactus glaucus
Colorado hookless cactus
Wherever
T
found
Sclerocactus mesae-verdae
Mesa Verde cactus
Wherever
T
found
Sclerocactus wetlandicus
Uinta Basin hookless cactus
Wherever
T
found
Sclerocactus wrightiae
Wright fishhook cactus
Scutellaria floridana
Florida skullcap
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
61 FR 43178,
8/21/1996;
50 CFR
17.99(g).CH
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
57 FR 1398,
1/14/1992.
57 FR 1398,
1/14/1992.
52 FR 37416,
10/6/1987.
56 FR 16021,
4/19/1991.
57 FR 44703,
9/29/1992.
56 FR 21091,
5/7/1991.
44 FR 64736,
11/7/1979; 83
FR 22392,
5/15/2018.
44 FR 58868,
10/11/1979;
74 FR 47112,
9/15/2009.
44 FR 58868,
10/11/1979;
74 FR 47112,
9/15/2009.
44 FR 62471,
10/30/1979.
44 FR 58868,
10/11/1979;
74 FR 47112,
9/15/2009.
44 FR 58866,
10/11/1979.
57 FR 19813,
5/8/1992.
Scutellaria montana
Large-flowered skullcap
Wherever
T
found
Senecio franciscanus
San Francisco Peaks
ragwort
Wherever
T
found
Senecio layneae
Layne's butterweed
Wherever
T
found
Serianthes nelsonii
Hayun lagu (Guam), Tronkon Wherever
E
guafi (Rota)
found
Sesbania tomentosa
Ohai
Wherever
E
found
Sibara filifolia
Santa Cruz Island rock-cress
Wherever
E
found
Sicyos albus (=alba)
Anunu
Wherever
E
found
Sicyos lanceoloideus
Anunu
Sicyos macrophyllus
Anunu
Sidalcea keckii
Keck's checkermallow
Wherever
E
found
Sidalcea nelsoniana
Nelson's checker-mallow
Wherever
T
found
Sidalcea oregana var. calva
Wenatchee Mountains
checker-mallow
Wherever
E
found
Sidalcea oregana ssp. valida
Kenwood Marsh checkermallow
Sidalcea pedata
Pedate checker-mallow
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
51 FR 22521,
6/20/1986;
67 FR 1662,
1/14/2002.
48 FR 52743,
11/22/1983;
50 CFR
17.96(a).CH
61 FR 54346,
10/18/1996.
52 FR 4907,
2/18/1987;
52 FR 6651,
5/4/1987.
59 FR 56333,
11/10/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(g);CH
50 CFR
17.99(i);CH
50 CFR
17.99(k).CH
62 FR 42692,
8/8/1997.
61 FR 53137,
10/10/1996,
50 CFR
17.99(k).CH
81 FR 67786,
9/30/2016.
81 FR 67786,
9/30/2016.
65 FR 7757,
2/16/2000;
50 CFR
17.96(a).CH
58 FR 8235,
2/12/1993.
64 FR 71680,
12/22/1999;
50 CFR
17.96(a).CH
62 FR 54791,
10/22/1997.
49 FR 34497,
8/31/1984.
Sideroxylon
reclinatum ssp.austrofloridense
Everglades bully
Wherever
T
found
Silene alexandri
No common name
Wherever
E
found
Silene hawaiiensis
No common name
Wherever
T
found
Silene lanceolata
No common name
Wherever
E
found
Silene perlmanii
No common name
Wherever
E
found
Silene polypetala
Fringed campion
Silene spaldingii
Spalding's catchfly
Sisyrinchium dichotomum
White irisette
Solanum drymophilum
Erubia
Solanum guamense
Biringenas halumtanu,
Birengenas halom tano
Solanum incompletum
Popolo ku mai
Wherever
E
found
Solanum nelsonii
Popolo
Wherever
E
found
Solanum sandwicense
Aiakeakua, popolo
Wherever
E
found
Solidago houghtonii
Houghton's goldenrod
Solidago shortii
Short's goldenrod
Solidago spithamaea
Blue Ridge goldenrod
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
T
found
82 FR 46691,
10/06/2017.
57 FR 46325,
10/8/1992;
50 CFR
17.99(c).CH
59 FR 10305,
3/4/1994;
50 CFR
17.99(k).CH
57 FR 46325,
10/8/1992;
50 CFR
17.99(c);CH
50 CFR
17.99(i).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
56 FR 1932,
1/18/1991.
66 FR 51597,
10/10/2001.
56 FR 48752,
9/26/1991.
53 FR 32827,
8/26/1988.
80 FR 59423,
10/1/2015.
59 FR 56333,
10/10/1994;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(k).CH
81 FR 67786,
9/30/2016.
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(i).CH
53 FR 27134,
7/18/1988.
50 FR 36085,
9/5/1985.
50 FR 12306,
3/28/1985.
Wherever
E
found
Spermolepis hawaiiensis
No common name
Sphaeralcea gierischii
Gierisch mallow
Spigelia gentianoides
Gentian pinkroot
Spiraea virginiana
Virginia spiraea
Spiranthes delitescens
Canelo Hills ladies'-tresses
Spiranthes diluvialis
Ute ladies'-tresses
Spiranthes parksii
Navasota ladies'-tresses
Stahlia monosperma
Cóbana negra
Stenogyne
angustifolia var. angustifolia
No common name
Stenogyne bifida
No common name
Wherever
E
found
Stenogyne campanulata
No common name
Wherever
E
found
Stenogyne cranwelliae
No common name
Stenogyne kaalae ssp. sherffii
No common name
Stenogyne kanehoana
No common name
Wherever
E
found
Stenogyne kauaulaensis
No common name
Wherever
E
found
Stenogyne kealiae
No common name
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
59 FR 56333,
11/10/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c)CH;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
78 FR 49149,
8/13/2013.
55 FR 49046,
11/26/1990.
55 FR 24241,
6/15/1990.
62 FR 665,
1/6/1997.
57 FR 2048,
1/17/1992.
47 FR 19539,
5/6/1982.
55 FR 12790,
4/5/1990.
44 FR 62468,
10/30/1979.
57 FR 46325,
10/8/1992;
50 CFR
17.99(c).CH
57 FR 20580,
5/13/1992;
50 CFR
17.99(a)(1).CH
78 FR 64637,
10/29/2013.
81 FR 67786,
9/30/2016.
57 FR 20592,
5/13/1992;
50 CFR
17.99(i).CH
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
Stephanomeria malheurensis
Malheur wire-lettuce
Streptanthus albidus ssp. albidus
Metcalf Canyon jewelflower
Streptanthus niger
Tiburon jewelflower
Styrax portoricensis
Palo de jazmfn
Styrax texanus
Texas snowbells
Suaeda californica
Sea-blite, California
Swallenia alexandrae
Tabernaemontana rotensis
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Eureka dune grass, Eureka
Wherever
Valley dune grass, or Eureka
T
found
dunegrass
Wherever
No common name
T
found
Wherever
E
found
Taraxacum californicum
California taraxacum
Ternstroemia luquillensis
Palo colorado
Ternstroemia subsessilis
No common name
Tetramolopium arenarium
No common name
Tetramolopium capillare
Pamakani
Wherever
E
found
Tetramolopium filiforme
No common name
Wherever
E
found
Tetramolopium
lepidotum ssp. lepidotum
No common name
Wherever
E
found
Tetramolopium remyi
No common name
Wherever
E
found
Tetramolopium rockii
No common name
Wherever
T
found
Thalictrum cooleyi
Cooley's meadowrue
Thelypodium howellii ssp. spectabilis
Howell's spectacular
thelypody
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
47 FR 50881,
11/10/1982;
50 CFR
17.96(a).CH
60 FR 6671,
2/3/1995.
60 FR 6671,
2/3/1995.
57 FR 14782,
4/22/1992.
49 FR 40035,
10/12/1984.
59 FR 64613,
12/15/1994.
83 FR 8576,
2/27/18.
80 FR 59423,
10/1/2015.
63 FR 49006,
9/14/1988;
50 CFR
17.96(a).CH
57 FR 14782,
4/22/1992.
57 FR 14782,
4/22/1992.
59 FR 10305,
3/4/1994.
59 FR 49860,
9/30/1994;
50 CFR
17.99(e)(1).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
56 FR 47686,
9/20/1991;
50 CFR
17.99(e)(1).CH
57 FR 46325,
10/8/1992;
50 CFR
17.99(c).CH
54 FR 5935,
2/7/1989.
64 FR 28393,
5/26/1999.
Thelypodium stenopetalum
Slender-petaled mustard
Wherever
E
found
Thlaspi californicum
Kneeland Prairie pennycress
Wherever
E
found
Thymophylla tephroleuca
Ashy dogweed
Thysanocarpus conchuliferus
Tinospora homosepala
Townsendia aprica
Wherever
E
found
Wherever
Santa Cruz Island fringepod
E
found
Wherever
No common name
E
found
Wherever
Last Chance townsendia
T
found
Wherever
E
found
Trematolobelia singularis
No common name
Trichilia triacantha
Bariaco
Trifolium amoenum
Showy Indian clover
Trifolium stoloniferum
Running buffalo clover
Trifolium trichocalyx
Monterey clover
Trillium persistens
Persistent trillium
Trillium reliquum
Relict trillium
Tuberolabium guamense
No common name
Tuctoria greenei
Greene's tuctoria
Wherever
T
found
Tuctoria mucronata
Solano grass
Wherever
T
found
Urera kaalae
Opuhe
Wherever
E
found
Varronia rupicola
No common name
Wherever
T
found
Verbena californica
Red Hills vervain
Verbesina dissita
Big-leaved crownbeard
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
T
found
Wherever
T
found
49 FR 34497,
8/31/1984.
65 FR 6332,
2/9/2000;
50 CFR
17.96(a).CH
49 FR 29232,
7/19/1984.
62 FR 40954,
7/31/1997.
80 FR 59423,
10/1/2015.
50 FR 33734,
8/21/1985.
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
53 FR 3565,
2/5/1988.
62 FR 54791,
10/22/1997.
52 FR 21478,
6/5/1987.
63 FR 43100,
8/12/1998.
43 FR 17910,
4/26/1978.
53 FR 10879,
4/4/1988.
80 FR 59423,
10/1/2015.
62 FR 14338,
3/26/1997;
50 CFR
17.96(a).CH
43 FR 44810,
9/28/1978;
50 CFR
17.96(a).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
79 FR 53303,
9/9/2014;
50 CFR
17.96(a).CH
63 FR 49006,
9/14/1998.
61 FR 52370,
10/7/1996.
Wherever
E
found
Wherever
E
found
Vernonia proctorii
No common name
Vicia menziesii
Hawaiian vetch
Vigna o-wahuensis
No common name
Wherever
E
found
Viola
chamissoniana ssp. chamissoniana
Pamakani
Wherever
E
found
Viola helenae
No common name
Wherever
E
found
Viola kauaiensis var. wahiawaensis
Nani waialeale
Wherever
E
found
Viola lanaiensis
No common name
Wherever
E
found
Viola oahuensis
No common name
Wherever
E
found
Warea amplexifolia
Wide-leaf warea
Warea carteri
Carter's mustard
Wikstroemia skottsbergiana
Akia
Wikstroemia villosa
Akia
Wherever
E
found
Wilkesia hobdyi
Dwarfiliau
Wherever
E
found
Xylosma crenatum
No common name
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
58 FR 25755,
4/27/1993.
43 FR 17910,
4/26/1978.
59 FR 56333,
11/10/1994;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(e)(2);CH
50 CFR
17.99(i);CH
50 CFR
17.99(c);CH
50 CFR
17.99(k).CH
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
56 FR 47695,
9/20/1991;
50 CFR
17.99(a)(1).CH
61 FR 53070,
10/10/1996;
50 CFR
17.99(a)(1).CH
56 FR 47686,
9/20/1991.
61 FR 53089,
10/10/1996;
50 CFR
17.99(i).CH
52 FR 15501,
4/29/1987.
52 FR 2227,
1/21/1987.
81 FR 67786,
9/30/2016.
78 FR 32013,
5/28/2013;
50 CFR
17.99(e)(1).CH
57 FR 27859,
6/22/1992;
50 CFR
17.99(a)(1).CH
57 FR 20580,
5/13/1992;
50 CFR
17.99(a)(1).CH
Xyris tennesseensis
Tennessee yellow-eyed
grass
Wherever
E
found
Yermo xanthocephalus
Desert yellowhead
Wherever
T
found
Zanthoxylum dipetalum var.
tomentosum
Ae
Wherever
E
found
Zanthoxylum hawaiiense
Ae
Wherever
E
found
Zanthoxylum oahuense
Ae
Wherever
E
found
Zanthoxylum thomasianum
St. Thomas prickly-ash
Wherever
E
found
Zizania texana
Texas wild-rice
Wherever
E
found
Ziziphus celata
Florida ziziphus
Wherever
E
found
56 FR 34151,
7/26/1991.
67 FR 11442,
3/14/2002;
50 CFR
17.96(a).CH
61 FR 53137,
10/10/1996;
50 CFR
17.99(k).CH
59 FR 10305,
3/4/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
50 FR 51867,
12/20/1985.
43 FR 17910,
4/26/1978;
50 CFR
17.96(a).CH
54 FR 31190,
7/27/1989.
Conifers
Wherever
T
found
Wherever
Cupressus goveniana ssp. goveniana Gowen cypress
T
found
Wherever
Fitzroya cupressoides
Alerce or Chilean false larch
T
found
Abies guatemalensis
Guatemalan fir (=pinabete)
Hesperocyparis abramsiana
Santa Cruz cypress
Wherever
T
found
Torreya taxifolia
Florida torreya
Wherever
E
found
Ferns and Allies
44 FR 65002,
11/8/1979.
63 FR 43100,
8/12/1998.
44 FR 64730,
11/7/1979.
52 FR 675,
1/8/1987;
81 FR 8408,
2/19/2016.
49 FR 2783,
1/23/1984.
Adenophorus periens
Pendent kihi fern
Wherever
E
found
Adiantum vivesii
No common name
Wherever
E
found
Asplenium dielerectum
Asplenium-leaved diellia
Wherever
E
found
Asplenium diellaciniatum
No common name
Wherever
E
found
Asplenium (=Diellia) dielfalcatum
(=falcate)
No common name
Wherever
E
found
Asplenium (=Diellia) dielmannii
(=mannii)
No common name
Wherever
E
found
Asplenium (=Diellia) dielpallicum
(=pallida)
No common name
Wherever
E
found
Asplenium peruvianum var. insulare
No common name
Wherever
E
found
Asplenium
scolopendrium var. americanum
American hart's-tongue fern
Wherever
T
found
Asplenium (=Diellia) unisorum
(=unisora)
No common name
Wherever
E
found
59 FR 56333,
11/10/1994;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(a)(1);CH
50 CFR
17.99(i);CH
50 CFR
17.99(k).CH
58 FR 32308,
6/9/1993.
59 FR 56333,
11/10/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i);CH
50 CFR
17.99(k).CH
81 FR 67786,
9/30/2016.
56 FR 55770,
10/29/1991;
50 CFR
17.99(i).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
59 FR 9304,
2/25/1994;
50 CFR
17.99(a)(1).CH
59 FR 49025,
9/26/1994;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(k).CH
54 FR 29726,
7/14/1989.
59 FR 32932,
6/27/1994;
50 CFR
17.99(i).CH
Wherever
E
found
Ctenitis squamigera
Pauoa
Cyathea dryopteroides
Elfin tree fern
Cyclosorus boydiae
Kupukupu makalii
Deparia kaalaana
No common name
Diplazium molokaiense
No common name
Wherever
E
found
Doryopteris angelica
No common name
Wherever
E
found
Doryopteris takeuchii
No common name
Wherever
E
found
Dryopteris glabra var. pusilla
Hohiu
Wherever
E
found
Dryopteris crinalis var. podosorus
Palapalai aumakua
Wherever
E
found
Elaphoglossum serpens
None
Wherever
E
found
Huperzia mannii
Wawae`iole
Wherever
E
found
Huperzia nutans
Wawaeiole
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
59 FR 49025,
9/26/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
52 FR 22936,
6/16/1987.
81 FR 67786,
9/30/2016.
81 FR 67786,
9/30/2016.
59 FR 49025,
9/26/1994;
50 CFR
17.99(a)(1);CH
50 CFR
17.99(c);CH
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
77 FR 57647,
9/18/2012;
50 CFR
17.99(i).CH
81 FR 67786,
9/30/2016.
75 FR 18960,
4/13/2010;
50 CFR
17.99(a).CH
58 FR 32308,
6/9/1993.
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1).CH
57 FR 20772,
5/15/1992;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i).CH
Huperzia stemmermanniae
No common name
Hypolepis hawaiiensis var. mauiensis Olua
Isoetes louisianensis
Louisiana quillwort
Isoetes melanospora
Black-spored quillwort
Isoetes tegetiformans
Mat-forming quillwort
Marsilea villosa
Ihiihi
Microlepia strigosa var. mauiensis
No common name
Polystichum aleuticum
Aleutian shield-fern
Polystichum calderonense
No common name
Pteris lidgatei
No common name
Tectaria estremerana
No common name
Thelypteris inabonensis
No common name
Thelypteris pilosa var. alabamensis
Alabama streak-sorus fern
Thelypteris verecunda
No common name
Thelypteris yaucoensis
No common name
Trichomanes
punctatumssp.floridanum
Florida bristle fern
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
T
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
81 FR 67786,
9/30/2016.
81 FR 67786,
9/30/2016.
57 FR 48741,
10/28/1992.
53 FR 3560,
2/5/1988.
53 FR 3560,
2/5/1988.
57 FR 27863,
6/22/1992;
50 CFR
17.99(c);CH
50 CFR
17.99(i).CH
81 FR 67786,
9/30/2016.
53 FR 4626,
2/17/1988.
58 FR 32308,
6/9/1993.
59 FR 49025,
9/26/1994;
50 CFR
17.99(e)(1);CH
50 CFR
17.99(i);CH
50 CFR
17.99(c).CH
58 FR 32308,
6/9/1993.
58 FR 35887,
7/2/1993.
57 FR 30164,
7/8/1992.
58 FR 35887,
7/2/1993.
58 FR 35887,
7/2/1993.
80 FR 60439,
10/6/2015.
Wherever
E
found
Wherever
E
found
58 FR 25746,
4/27/1993.
60 FR 3557,
1/18/1995.
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Wherever
E
found
Lichens
Cladonia perforata
Florida perforate cladonia
Gymnoderma lineare
Rock gnome lichen
[81 FR 51583, Aug. 4, 2016, as amended at 81 FR 55301, Aug. 18, 2016; 81 FR 62832, Sept. 13, 2016; 81 FR
66864, Sept. 29, 2016; 81 FR 67857, Sept. 30, 2016; 81 FR 70059, Oct. 11, 2016; 82 FR 42259, Sept. 7, 2017; 82
FR 46715, Oct. 6, 2017; 83 FR 8603, Feb. 27, 2018; 83 FR 21936, May 11, 2018; 83 FR 22401, May 15, 2018; 83
FR 25404, June 1, 2018; 83 FR 52786, Oct. 18, 2018; 84 FR 59587, Nov. 5, 2019]
return arrow Back to Top
Subpart C—Endangered Wildlife
return arrow Back to Top
§17.21 Prohibitions.
(a) Except as provided in subpart A of this part, or under permits issued pursuant to §17.22 or §17.23, it is unlawful
for any person subject to the jurisdiction of the United States to commit, to attempt to commit, to solicit another to
commit or to cause to be committed, any of the acts described in paragraphs (b) through (f) of this section in
regard to any endangered wildlife.
(b) Import or export. It is unlawful to import or to export any endangered wildlife. Any shipment in transit through
the United States is an importation and an exportation, whether or not it has entered the country for customs
purposes.
(c) Take. (1) It is unlawful to take endangered wildlife within the United States, within the territorial sea of the
United States, or upon the high seas. The high seas shall be all waters seaward of the territorial sea of the United
States, except waters officially recognized by the United States as the territorial sea of another country, under
international law.
(2) Notwithstanding paragraph (c)(1) of this section, any person may take endangered wildlife in defense of his
own life or the lives of others.
(3) Notwithstanding paragraph (c)(1) of this section, any employee or agent of the Service, any other Federal land
management agency, the National Marine Fisheries Service, or a State conservation agency, who is designated by
his agency for such purposes, may, when acting in the course of his official duties, take endangered wildlife
without a permit if such action is necessary to:
(i) Aid a sick, injured or orphaned specimen; or
(ii) Dispose of a dead specimen; or
(iii) Salvage a dead specimen which may be useful for scientific study; or
(iv) Remove specimens which constitute a demonstrable but nonimmediate threat to human safety, provided that
the taking is done in a humane manner; the taking may involve killing or injuring only if it has not been reasonably
possible to eliminate such threat by live-capturing and releasing the specimen unharmed, in a remote area.
(4) Any taking under paragraphs (c)(2) and (3) of this section must be reported in writing to the Office of Law
Enforcement, at the address provided at 50 CFR 2.1(b), within 5 days. The specimen may only be retained,
disposed of, or salvaged under directions from the Office of Law Enforcement.
(5) Notwithstanding paragraph (c)(1) of this section, any qualified employee or agent of a State Conservation
Agency which is a party to a Cooperative Agreement with the Service in accordance with section 6(c) of the Act,
who is designated by his agency for such purposes, may, when acting in the course of his official duties take those
endangered species which are covered by an approved cooperative agreement for conservation programs in
accordance with the Cooperative Agreement, provided that such taking is not reasonably anticipated to result in:
(i) The death or permanent disabling of the specimen;
(ii) The removal of the specimen from the State where the taking occurred;
(iii) The introduction of the specimen so taken, or of any progeny derived from such a specimen, into an area
beyond the historical range of the species; or
(iv) The holding of the specimen in captivity for a period of more than 45 consecutive days.
(6) Notwithstanding paragraph (c)(1) of this section, any person acting under a valid migratory bird rehabilitation
permit issued pursuant to §21.31 of this subchapter may take endangered migratory birds without an endangered
species permit if such action is necessary to aid a sick, injured, or orphaned endangered migratory bird, provided
the permittee:
(i) Notifies the issuing Migratory Bird Permit Office immediately upon receipt of such bird (contact information for
your issuing office is listed on your permit and on the Internet at http://offices.fws.gov); and
(ii) Disposes of or transfers such birds, or their parts or feathers, as directed by the Migratory Bird Permit Office.
(7) Notwithstanding paragraph (c)(1) of this section, persons exempt from the permit requirements of §21.12(c)
and (d) of this subchapter may take sick and injured endangered migratory birds without an endangered species
permit in performing the activities authorized under §21.12(c) and (d).
(d) Possession and other acts with unlawfully taken wildlife. (1) It is unlawful to possess, sell, deliver, carry,
transport, or ship, by any means whatsoever, any endangered wildlife which was taken in violation of paragraph (c)
of this section.
Example. A person captures a whooping crane in Texas and gives it to a second person, who puts it in a closed
van and drives thirty miles, to another location in Texas. The second person then gives the whooping crane to a
third person, who is apprehended with the bird in his possession. All three have violated the law—the first by
illegally taking the whooping crane; the second by transporting an illegally taken whooping crane; and the third by
possessing an illegally taken whooping crane.
(2) Notwithstanding paragraph (d)(1) of this section, Federal and State law enforcement officers may possess,
deliver, carry, transport or ship any endangered wildlife taken in violation of the Act as necessary in performing
their official duties.
(3) Notwithstanding paragraph (d)(1) of this section, any person acting under a valid migratory bird rehabilitation
permit issued pursuant to §21.31 of this subchapter may possess and transport endangered migratory birds
without an endangered species permit when such action is necessary to aid a sick, injured, or orphaned
endangered migratory bird, provided the permittee:
(i) Notifies the issuing Migratory Bird Permit Office immediately upon receipt of such bird (contact information for
your issuing office is listed on your permit and on the Internet at http://offices.fws.gov); and
(ii) Disposes of or transfers such birds, or their parts or feathers, as directed by the Migratory Bird Permit Office.
(4) Notwithstanding paragraph (d)(1) of this section, persons exempt from the permit requirements of §21.12(c)
and (d) of this subchapter may possess and transport sick and injured endangered migratory bird species without
an endangered species permit in performing the activities authorized under §21.12(c) and (d).
(e) Interstate or foreign commerce. It is unlawful to deliver, receive, carry transport, or ship in interstate or foreign
commerce, by any means whatsoever, and in the course of a commercial activity, any endangered wildlife.
(f) Sale or offer for sale. (1) It is unlawful to sell or to offer for sale in interstate or foreign commerce any
endangered wildlife.
(2) An advertisement for the sale of endangered wildlife which carries a warning to the effect that no sale may be
consummated until a permit has been obtained from the U.S. Fish and Wildlife Service shall not be considered an
offer for sale within the meaning of this section.
(g) Captive-bred wildlife. (1) Notwithstanding paragraphs (b), (c), (e) and (f) of this section, any person may take;
export or re-import; deliver, receive, carry, transport or ship in interstate or foreign commerce, in the course of a
commercial activity; or sell or offer for sale in interstate or foreign commerce any endangered wildlife that is bred in
captivity in the United States provided either that the wildlife is of a taxon listed in paragraph (g)(6) of this section,
or that the following conditions are met:
(i) The wildlife is of a species having a natural geographic distribution not including any part of the United States,
or the wildlife is of a species that the Director has determined to be eligible in accordance with paragraph (g)(5) of
this section;
(ii) The purpose of such activity is to enhance the propagation or survival of the affected species;
(iii) Such activity does not involve interstate or foreign commerce, in the course of a commercial activity, with
respect to non-living wildlife;
(iv) Each specimen of wildlife to be re-imported is uniquely identified by a band, tattoo or other means that was
reported in writing to an official of the Service at a port of export prior to export from the United States; and
(v) Any person subject to the jurisdiction of the United States who engages in any of the activities authorized by
this paragraph does so in accordance with paragraphs (g) (2), (3) and (4) of this section, and with all other
applicable regulations in this Subchapter B.
(2) Any person subject to the jurisdiction of the United States seeking to engage in any of the activities authorized
by this paragraph must first register with the Service's Division of Management Authority at the address provided
at 50 CFR 2.1(b). Requests for registration must be submitted on an official application form (Form 3-200-41)
provided by the Service, and must include the following information:
(i) The types of wildlife sought to be covered by the registration, identified by common and scientific name to the
taxonomic level of family, genus or species;
(ii) A description of the applicant's experience in maintaining and propagating the types of wildlife sought to be
covered by the registration, and when appropriate, in conducting research directly related to maintaining and
propagating such wildlife;
(iii) Photograph(s) or other evidence clearly depicting the facilities where such wildlife will be maintained; and
(iv) a copy of the applicant's license or registration, if any, under the animal welfare regulations of the U.S.
Department of Agriculture (9 CFR part 2).
(3) Upon receipt of a complete application for registration, or the renewal or amendment of an existing registration,
under this section, the Service will publish notice of the application in the Federal Register. Each notice will invite
the submission from interested parties, within 30 days after the date of the notice, of written data, views, or
arguments with respect to the application. All information received as part of each application will be made
available to the public, upon request, as a matter of public record at every stage of the proceeding, including, but
not limited to, information needed to assess the eligibility of the applicant, such as the original application,
materials, any intervening renewal applications documenting a change in location or personnel, and the most
recent annual report.
(i) At the completion of this comment period, the Director will decide whether to approve the registration. In making
this decision, the Director will consider, in addition to the general criteria in §13.21(b) of this subchapter, whether
the expertise, facilities, or other resources available to the applicant appear adequate to enhance the propagation
or survival of the affected wildlife. Public education activities may not be the sole basis to justify issuance of a
registration or to otherwise establish eligibility for the exception granted in paragraph (g)(1) of this section.
(ii) If the Director approves the registration, the Service will publish notice of the decision in the Federal
Registerthat the registration was applied for in good faith, that issuing the registration will not operate to the
disadvantage of the species for which registration was sought, and that issuing the registration will be consistent
with the purposes and policy set forth in section 2 of the Act.
(iii) Each person so registered must maintain accurate written records of activities conducted under the registration
and allow reasonable access to Service agents for inspection purposes as set forth in §§13.46 and 13.47 of this
chapter. Each person so registered must also submit to the Director an individual written annual report of activities,
including all births, deaths, and transfers of any type.
(4) Any person subject to the jurisdiction of the United States seeking to export or conduct foreign commerce in
captive-bred endangered wildlife that will not remain under the care of that person must first obtain approval by
providing written evidence to satisfy the Director that the proposed recipient of the wildlife has expertise, facilities
or other resources adequate to enhance the propagation or survival of such wildlife and that the proposed recipient
will use such wildlife for purposes of enhancing the propagation or survival of the affected species.
(5)(i) The Director will use the following criteria to determine if wildlife of any species having a natural geographic
distribution that includes any part of the United States is eligible for the provisions of this paragraph:
(A) Whether there is a low demand for taking of the species from wild populations, either because of the success
of captive breeding or because of other reasons, and
(B) Whether the wild populations of the species are effectively protected from unauthorized taking as a result of
the inaccessibility of their habitat to humans or as a result of the effectiveness of law enforcement.
(ii) The Director will follow the procedures set forth in the Act and in the regulations thereunder with respect to
petitions and notification of the public and governors of affected States when determining the eligibility of species
for purposes of this paragraph.
(iii) In accordance with the criteria in paragraph (g)(5)(i) of this section, the Director has determined the following
species to be eligible for the provisions of this paragraph:
Laysan duck (Anas laysanensis).
(6) Exemption from registration requirement. (i) If the conditions in paragraph (g)(6)(ii) of this section are met, then
any person subject to the jurisdiction of the United States seeking to engage in any of the activities authorized by
paragraph (g)(1) of this section may do so without first registering with the Service with respect to the following
species:
(A) The bar-tailed pheasant (Syrmaticus humiae), Elliot's pheasant (S. ellioti), Mikado pheasant (S.
mikado), brown eared pheasant (Crossoptilon mantchuricum), white eared pheasant (C. crossoptilon), cheer
pheasant (Catreus wallichii), Edward's pheasant (Lophura edwardsi), Swinhoe's pheasant (L. swinhoii), Chinese
monal (Lophophorus lhuysii), and Palawan peacock pheasant (Polyplectron emphanum);
(B) Parakeets of the species Neophema pulchella and N. splendida;
(C) The Laysan duck (Anas laysanensis); and
(D) The white-winged wood duck (Cairina scutulata).
(ii) Conditions for exemption to register. The following conditions must exist for persons dealing with the species
listed in paragraph (g)(6)(i) of this section to be eligible for exemption from the requirement to register with the
Service:
(A) The purpose of the activity is to enhance the propagation or survival of the affected exempted species.
(B) Such activity does not involve interstate or foreign commerce, in the course of a commercial activity, with
respect to nonliving wildlife.
(C) Each specimen to be reimported is uniquely identified by a band, tattoo, or other means that was reported in
writing to an official of the Service at a port of export prior to export of the specimen from the United States.
(D) No specimens of the taxa in paragraph (g)(6)(i) of this section that were taken from the wild may be imported
for breeding purposes absent a definitive showing that the need for new bloodlines can be met only by wild
specimens, that suitable foreign-bred, captive individuals are unavailable, and that wild populations can sustain
limited taking. In addition, an import permit must be issued under §17.22.
(E) Any permanent exports of such specimens meet the requirements of paragraph (g)(4) of this section.
(F) Each person claiming the benefit of the exception in paragraph (g)(1) of this section must maintain accurate
written records of activities, including births, deaths, and transfers of specimens, and make those records
accessible to Service agents for inspection at reasonable hours as set forth in §§13.46 and 13.47 of this chapter.
(h) U.S. captive-bred scimitar-horned oryx, addax, and dama gazelle. Notwithstanding paragraphs (b), (c), (e), and
(f) of this section, any person subject to the jurisdiction of the United States may take; export or re-import; deliver,
receive, carry, transport or ship in interstate or foreign commerce, in the course of a commercial activity; or sell or
offer for sale in interstate or foreign commerce live wildlife, including embryos and gametes, and sport-hunted
trophies of scimitar-horned oryx (Oryx dammah), addax (Addax nasomaculatus), and dama gazelle (Gazella
dama) provided:
(1) The purpose of such activity is associated with the management or transfer of live wildlife, including embryos
and gametes, or sport hunting in a manner that contributes to increasing or sustaining captive numbers or to
potential reintroduction to range countries;
(2) The specimen was captive-bred, in accordance with §17.3, within the United States;
(3) All live specimens of that species held by the captive-breeding operation are managed in a manner that
prevents hybridization of the species or subspecies;
(4) All live specimens of that species held by the captive-breeding operation are managed in a manner that
maintains genetic diversity;
(5) Any export of or foreign commerce in a specimen meets the requirements of paragraph (g)(4) of this section,
as well as parts 13, 14, and 23 of this chapter;
(6) Each specimen to be re-imported is uniquely identified by a tattoo or other means that is reported on the
documentation required under paragraph (h)(5) of this section; and
(7) Each person claiming the benefit of the exception of this paragraph (h) must maintain accurate written records
of activities, including births, deaths, and transfers of specimens, and make those records accessible to Service
officials for inspection at reasonable hours set forth in §§13.46 and 13.47 of this chapter.
(8) The sport-hunted trophy consists of raw or tanned parts, such as bones, hair, head, hide, hooves, horns, meat,
skull, rug, taxidermied head, shoulder, or full body mount, of a specimen that was taken by the hunter during a
sport hunt for personal use. It does not include articles made from a trophy, such as worked, manufactured, or
handicraft items for use as clothing, curios, ornamentation, jewelry, or other utilitarian items for commercial
purposes.
[40 FR 44415, Sept. 26, 1975, as amended at 40 FR 53400, Nov. 18, 1975; 41 FR 19226, May 11, 1976; 44 FR
31580, May 31, 1979; 44 FR 54007, Sept. 17, 1979; 58 FR 68325, Dec. 27, 1993; 63 FR 48640, Sept. 11, 1998;
68 FR 2919, Jan. 22, 2003; 68 FR 61136, Oct. 27, 2003; 70 FR 52318, Sept. 2, 2005; 77 FR 438, Jan. 5, 2012; 77
FR 43175, July 24, 2012; 79 FR 15252, Mar. 19, 2014; 79 FR 30418, May 27, 2014; 79 FR 43965, July 29, 2014;
81 FR 19930, Apr. 6, 2016]
return arrow Back to Top
§17.22 Permits for scientific purposes,
enhancement of propagation or survival, or for
incidental taking.
Upon receipt of a complete application, the Director may issue a permit authorizing any activity otherwise
prohibited by §17.21, in accordance with the issuance criteria of this section, for scientific purposes, for enhancing
the propagation or survival, or for the incidental taking of endangered wildlife. Such permits may authorize a single
transaction, a series of transactions, or a number of activities over a specific period of time. (See §17.32 for
permits for threatened species.) The Director shall publish notice in the Federal Register of each application for a
permit that is made under this section. Each notice shall invite the submission from interested parties, within 30
days after the date of the notice, of written data, views, or arguments with respect to the application. The 30-day
period may be waived by the Director in an emergency situation where the life or health of an endangered animal
is threatened and no reasonable alternative is available to the applicant. Notice of any such waiver shall be
published in the Federal Register within 10 days following issuance of the permit.
(a)(1) Application requirements for permits for scientific purposes or for the enhancement of propagation or
survival.A person wishing to get a permit for an activity prohibited by §17.21 submits an application for activities
under this paragraph. The Service provides Form 3-200 for the application to which all of the following must be
attained:
(i) The common and scientific names of the species sought to the covered by the permit, as well as the number,
age, and sex of such species, and the activity sought to be authorized (such as taking, exporting, selling in
interstate commerce);
(ii) A statement as to whether, at the time of application, the wildlife sought to be covered by the permit (A) is still in
the wild, (B) has already been removed from the wild, or (C) was born in captivity;
(iii) A resume of the applicant's attempts to obtain the wildlife sought to be covered by the permit in a manner
which would not cause the death or removal from the wild of such wildlife;
(iv) If the wildlife sought to be covered by the permit has already been removed from the wild, the country and
place where such removal occurred; if the wildlife sought to be covered by the permit was born in captivity, the
country and place where such wildlife was born;
(v) A complete description and address of the institution or other facility where the wildlife sought to be covered by
the permit will be used, displayed, or maintained;
(vi) If the applicant seeks to have live wildlife covered by the permit, a complete description, including photographs
or diagrams, of the facilities to house and/or care for the wildlife and a resume of the experience of those person
who will be caring for the wildlife;
(vii) A full statement of the reasons why the applicant is justified in obtaining a permit including the details of the
activities sought to be authorized by the permit;
(viii) If the application is for the purpose of enhancement of propagation, a statement of the applicant's willingness
to participate in a cooperative breeding program and to maintain or contribute data to a studbook;
(2) Issuance criteria. Upon receiving an application completed in accordance with paragraph (a)(1) of this section,
the Director will decide whether or not a permit should be issued. In making this decision, the Director shall
consider, in addition to the general criteria in §13.21(b) of this subchapter, the following factors:
(i) Whether the purpose for which the permit is required is adequate to justify removing from the wild or otherwise
changing the status of the wildlife sought to be covered by the permit;
(ii) The probable direct and indirect effect which issuing the permit would have on the wild populations of the
wildlife sought to be covered by the permit;
(iii) Whether the permit, if issued, would in any way, directly or indirectly, conflict with any known program intended
to enhance the survival probabilities of the population from which the wildlife sought to be covered by the permit
was or would be removed;
(iv) Whether the purpose for which the permit is required would be likely to reduce the threat of extinction facing
the species of wildlife sought to be covered by the permit;
(v) The opinions or views of scientists or other persons or organizations having expertise concerning the wildlife or
other matters germane to the application; and
(vi) Whether the expertise, facilities, or other resources available to the applicant appear adequate to successfully
accomplish the objectives stated in the application.
(3) Permit conditions. In addition to the general conditions set forth in part 13 of this subchapter, every permit
issued under this paragraph shall be subject to the special condition that the escape of living wildlife covered by
the permit shall be immediately reported to the Service office designated in the permit.
(4) Duration of permits. The duration of permits issued under this paragraph shall be designated on the face of the
permit.
(b)(1) Application requirements for permits for incidental taking. A person wishing to get a permit for an activity
prohibited by §17.21(c) submits an application for activities under this paragraph. The Service provides Form 3200 for the application to which all of the following must be attached:
(i) A complete description of the activity sought to be authorized;
(ii) The common and scientific names of the species sought to be covered by the permit, as well as the number,
age, and sex of such species, if known;
(iii) A conservation plan that specifies:
(A) The impact that will likely result from such taking;
(B) What steps the applicant will take to monitor, minimize, and mitigate such impacts, the funding that will be
available to implement such steps, and the procedures to be used to deal with unforeseen circumstances;
(C) What alternative actions to such taking the applicant considered and the reasons why such alternatives are not
proposed to be utilized; and
(D) Such other measures that the Director may require as being necessary or appropriate for purposes of the plan;
(2) Issuance criteria. (i) Upon receiving an application completed in accordance with paragraph (b)(1) of this
section, the Director will decide whether or not a permit should be issued. The Director shall consider the general
issuance criteria in §13.21(b) of this subchapter, except for §13.21(b)(4), and shall issue the permit if he or she
finds that:
(A) The taking will be incidental;
(B) The applicant will, to the maximum extent practicable, minimize and mitigate the impacts of such takings;
(C) The applicant will ensure that adequate funding for the conservation plan and procedures to deal with
unforeseen circumstances will be provided;
(D) The taking will not appreciably reduce the likelihood of the survival and recovery of the species in the wild;
(E) The measures, if any, required under paragraph (b)(1)(iii)(D) of this section will be met; and
(F) He or she has received such other assurances as he or she may require that the plan will be implemented.
(ii) In making his or her decision, the Director shall also consider the anticipated duration and geographic scope of
the applicant's planned activities, including the amount of listed species habitat that is involved and the degree to
which listed species and their habitats are affected.
(3) Permit conditions. In addition to the general conditions set forth in part 13 of this subchapter, every permit
issued under this paragraph shall contain such terms and conditions as the Director deems necessary or
appropriate to carry out the purposes of the permit and the conservation plan including, but not limited to,
monitoring and reporting requirements deemed necessary for determining whether such terms and conditions are
being complied with. The Director shall rely upon existing reporting requirements to the maximum extent
practicable.
(4) Duration of permits. The duration of permits issued under this paragraph shall be sufficient to provide adequate
assurances to the permittee to commit funding necessary for the activities authorized by the permit, including
conservation activities and land use restrictions. In determining the duration of a permit, the Director shall consider
the duration of the planned activities, as well as the possible positive and negative effects associated with permits
of the proposed duration on listed species, including the extent to which the conservation plan will enhance the
habitat of listed species and increase the long-term survivability of such species.
(5) Assurances provided to permittee in case of changed or unforeseen circumstances. The assurances in this
paragraph (b)(5) apply only to incidental take permits issued in accordance with paragraph (b)(2) of this section
where the conservation plan is being properly implemented, and apply only with respect to species adequately
covered by the conservation plan. These assurances cannot be provided to Federal agencies. This rule does not
apply to incidental take permits issued prior to March 25, 1998. The assurances provided in incidental take permits
issued prior to March 25, 1998 remain in effect, and those permits will not be revised as a result of this rulemaking.
(i) Changed circumstances provided for in the plan. If additional conservation and mitigation measures are
deemed necessary to respond to changed circumstances and were provided for in the plan's operating
conservation program, the permittee will implement the measures specified in the plan.
(ii) Changed circumstances not provided for in the plan. If additional conservation and mitigation measures are
deemed necessary to respond to changed circumstances and such measures were not provided for in the plan's
operating conservation program, the Director will not require any conservation and mitigation measures in addition
to those provided for in the plan without the consent of the permittee, provided the plan is being properly
implemented.
(iii) Unforeseen circumstances. (A) In negotiating unforeseen circumstances, the Director will not require the
commitment of additional land, water, or financial compensation or additional restrictions on the use of land, water,
or other natural resources beyond the level otherwise agreed upon for the species covered by the conservation
plan without the consent of the permittee.
(B) If additional conservation and mitigation measures are deemed necessary to respond to unforeseen
circumstances, the Director may require additional measures of the permittee where the conservation plan is being
properly implemented, but only if such measures are limited to modifications within conserved habitat areas, if any,
or to the conservation plan's operating conservation program for the affected species, and maintain the original
terms of the conservation plan to the maximum extent possible. Additional conservation and mitigation measures
will not involve the commitment of additional land, water or financial compensation or additional restrictions on the
use of land, water, or other natural resources otherwise available for development or use under the original terms
of the conservation plan without the consent of the permittee.
(C) The Director will have the burden of demonstrating that unforeseen circumstances exist, using the best
scientific and commercial data available. These findings must be clearly documented and based upon reliable
technical information regarding the status and habitat requirements of the affected species. The Director will
consider, but not be limited to, the following factors:
(1) Size of the current range of the affected species;
(2) Percentage of range adversely affected by the conservation plan;
(3) Percentage of range conserved by the conservation plan;
(4) Ecological significance of that portion of the range affected by the conservation plan;
(5) Level of knowledge about the affected species and the degree of specificity of the species' conservation
program under the conservation plan; and
(6) Whether failure to adopt additional conservation measures would appreciably reduce the likelihood of survival
and recovery of the affected species in the wild.
(6) Nothing in this rule will be construed to limit or constrain the Director, any Federal, State, local, or Tribal
government agency, or a private entity, from taking additional actions at its own expense to protect or conserve a
species included in a conservation plan.
(7) Discontinuance of permit activity. Notwithstanding the provisions of §13.26 of this subchapter, a permittee
under this paragraph (b) remains responsible for any outstanding minimization and mitigation measures required
under the terms of the permit for take that occurs prior to surrender of the permit and such minimization and
mitigation measures as may be required pursuant to the termination provisions of an implementing agreement,
habitat conservation plan, or permit even after surrendering the permit to the Service pursuant to §13.26 of this
subchapter. The permit shall be deemed canceled only upon a determination by the Service that such minimization
and mitigation measures have been implemented. Upon surrender of the permit, no further take shall be
authorized under the terms of the surrendered permit.
(8) Criteria for revocation. A permit issued under paragraph (b) of this section may not be revoked for any reason
except those set forth in §13.28(a)(1) through (4) of this subchapter or unless continuation of the permitted activity
would be inconsistent with the criterion set forth in 16 U.S.C. 1539(a)(2)(B)(iv) and the inconsistency has not been
remedied.
(c)(1) Application requirements for permits for the enhancement of survival through Safe Harbor Agreements. The
applicant must submit an application for a permit under this paragraph (c) to the appropriate Regional Director,
U.S. Fish and Wildlife Service, for the Region where the applicant resides or where the proposed activity is to
occur (for appropriate addresses, see 50 CFR 10.22), if the applicant wishes to engage in any activity prohibited
by §17.21. The applicant must submit an official Service application form (3-200.54) that includes the following
information:
(i) The common and scientific names of the listed species for which the applicant requests incidental take
authorization;
(ii) A description of how incidental take of the listed species pursuant to the Safe Harbor Agreement is likely to
occur, both as a result of management activities and as a result of the return to baseline; and
(iii) A Safe Harbor Agreement that complies with the requirements of the Safe Harbor policy available from the
Service.
(2) Issuance criteria. Upon receiving an application completed in accordance with paragraph (c)(1) of this section,
the Director will decide whether or not to issue a permit. The Director shall consider the general issuance criteria in
§13.21(b) of this subchapter, except for §13.21(b)(4), and may issue the permit if he or she finds:
(i) The take will be incidental to an otherwise lawful activity and will be in accordance with the terms of the Safe
Harbor Agreement;
(ii) The implementation of the terms of the Safe Harbor Agreement is reasonably expected to provide a net
conservation benefit to the affected listed species by contributing to the recovery of listed species included in the
permit, and the Safe Harbor Agreement otherwise complies with the Safe Harbor policy available from the Service;
(iii) The probable direct and indirect effects of any authorized take will not appreciably reduce the likelihood of
survival and recovery in the wild of any listed species;
(iv) Implementation of the terms of the Safe Harbor Agreement is consistent with applicable Federal, State, and
Tribal laws and regulations;
(v) Implementation of the terms of the Safe Harbor Agreement will not be in conflict with any ongoing conservation
or recovery programs for listed species covered by the permit; and
(vi) The applicant has shown capability for and commitment to implementing all of the terms of the Safe Harbor
Agreement.
(3) Permit conditions. In addition to any applicable general permit conditions set forth in part 13 of this subchapter,
every permit issued under this paragraph (c) is subject to the following special conditions:
(i) A requirement for the participating property owner to notify the Service of any transfer of lands subject to a Safe
Harbor Agreement;
(ii) When appropriate, a requirement for the permittee to give the Service reasonable advance notice (generally at
least 30 days) of when he or she expects to incidentally take any listed species covered under the permit. Such
notification will provide the Service with an opportunity to relocate affected individuals of the species, if possible
and appropriate; and
(iii) Any additional requirements or conditions the Director deems necessary or appropriate to carry out the
purposes of the permit and the Safe Harbor Agreement.
(4) Permit effective date. Permits issued under this paragraph (c) become effective the day of issuance for species
covered by the Safe Harbor Agreement.
(5) Assurances provided to permittee. (i) The assurances in paragraph (c)(5) (ii) of this section (c)(5) apply only to
Safe Harbor permits issued in accordance with paragraph (c)(2) of this section where the Safe Harbor Agreement
is being properly implemented, and apply only with respect to species covered by the Agreement and permit.
These assurances cannot be provided to Federal agencies. The assurances provided in this section apply only to
Safe Harbor permits issued after July 19, 1999.
(ii) The Director and the permittee may agree to revise or modify the management measures set forth in a Safe
Harbor Agreement if the Director determines that such revisions or modifications do not change the Director's prior
determination that the Safe Harbor Agreement is reasonably expected to provide a net conservation benefit to the
listed species. However, the Director may not require additional or different management activities to be
undertaken by a permittee without the consent of the permittee.
(6) Additional actions. Nothing in this rule will be construed to limit or constrain the Director, any Federal, State,
local or Tribal government agency, or a private entity, from taking additional actions at its own expense to protect
or conserve a species included in a Safe Harbor Agreement.
(7) Criteria for revocation. The Director may not revoke a permit issued under paragraph (c) of this section except
as provided in this paragraph. The Director may revoke a permit for any reason set forth in §13.28(a)(1) through
(4) of this subchapter. The Director may revoke a permit if continuation of the permitted activity would either
appreciably reduce the likelihood of survival and recovery in the wild of any listed species or directly or indirectly
alter designated critical habitat such that it appreciably diminishes the value of that critical habitat for both the
survival and recovery of a listed species. Before revoking a permit for either of the latter two reasons, the Director,
with the consent of the permittee, will pursue all appropriate options to avoid permit revocation. These options may
include, but are not limited to: extending or modifying the existing permit, capturing and relocating the species,
compensating the landowner to forgo the activity, purchasing an easement or fee simple interest in the property, or
arranging for a third-party acquisition of an interest in the property.
(8) Duration of permits. The duration of permits issued under this paragraph (c) must be sufficient to provide a net
conservation benefit to species covered in the enhancement of survival permit. In determining the duration of a
permit, the Director will consider the duration of the planned activities, as well as the positive and negative effects
associated with permits of the proposed duration on covered species, including the extent to which the
conservation activities included in the Safe Harbor Agreement will enhance the survival and contribute to the
recovery of listed species included in the permit.
(d)(1) Application requirements for permits for the enhancement of survival through Candidate Conservation
Agreements with Assurances (CCAAs). The applicant must submit an application for a permit under this paragraph
(d) to the appropriate Regional Director, U.S. Fish and Wildlife Service, for the Region where the applicant resides
or where the proposed activity is to occur (for appropriate addresses, see 50 CFR 10.22). When a species covered
by a (CCAA) is listed as endangered and the applicant wishes to engage in activities identified in the Agreement
and otherwise prohibited by §17.31, the applicant must apply for an enhancement of survival permit for species
covered by the Agreement. The permit will become valid if and when covered proposed, candidate or other
unlisted species is listed as an endangered species. The applicant must submit an official Service application form
(3-200.54) that includes the following information:
(i) The common and scientific names of the species for which the applicant requests incidental take authorization;
(ii) A description of the land use or water management activity for which the applicant requests incidental take
authorization; and
(iii) A CCAA that complies with the requirements of the CCAA with Assurances policy available from the Service.
(2) Issuance criteria. Upon receiving an application completed in accordance with paragraph (d)(1) of this section,
the Director will decide whether or not to issue a permit. The Director shall consider the general issuance criteria in
§13.21(b) of this subchapter, except for §13.21(b)(4), and may issue the permit if he or she finds:
(i) The take will be incidental to an otherwise lawful activity and will be in accordance with the terms of the CCAA;
(ii) The implementation of the terms of the CCAA is reasonably expected to provide a net conservation benefit to
the affected covered species by contributing to the conservation of the species included in the permit, and the
CCAA otherwise complies with the Candidate Conservation Agreement with Assurances policy available from the
Service;
(iii) The probable direct and indirect effects of any authorized take will not appreciably reduce the likelihood of
survival and recovery in the wild of any species;
(iv) Implementation of the terms of the CCAA is consistent with applicable Federal, State, and Tribal laws and
regulations;
(v) Implementation of the terms of the CCAA will not be in conflict with any ongoing conservation programs for
species covered by the permit; and
(vi) The applicant has shown capability for and commitment to implementing all of the terms of the CCAA.
(3) Permit conditions. In addition to any applicable general permit conditions set forth in part 13 of this subchapter,
every permit issued under this paragraph (d) is subject to the following special conditions:
(i) A requirement for the property owner to notify the Service of any transfer of lands subject to a CCAA;
(ii) When appropriate, a requirement for the permittee to give the Service reasonable advance notice (generally at
least 30 days) of when he or she expects to incidentally take any listed species covered under the permit. Such
notification will provide the Service with an opportunity to relocate affected individuals of the species, if possible
and appropriate; and
(iii) Any additional requirements or conditions the Director deems necessary or appropriate to carry out the
purposes of the permit and the CCAA.
(4) Permit effective date. Permits issued under this paragraph (d) become effective for a species covered by a
CCAA on the effective date of a final rule that lists a covered species as endangered.
(5) Assurances provided to permittee in case of changed or unforeseen circumstances. The assurances in this
paragraph (d)(5) apply only to permits issued in accordance with paragraph (d)(2) where the (CCAA) is being
properly implemented, and apply only with respect to species adequately covered by the CCAA. These
assurances cannot be provided to Federal agencies.
(i) Changed circumstances provided for in the Agreement. If the Director determines that additional conservation
measures are necessary to respond to changed circumstances and these measures were set forth in the
Agreement, the permittee will implement the measures specified in the Agreement.
(ii) Changed circumstances not provided for in the Agreement. If the Director determines that additional
conservation measures not provided for in the Agreement are necessary to respond to changed circumstances,
the Director will not require any conservation measures in addition to those provided for in the Agreement without
the consent of the permittee, provided the Agreement is being properly implemented.
(iii) Unforeseen circumstances. (A) In negotiating unforeseen circumstances, the Director will not require the
commitment of additional land, water, or financial compensation or additional restrictions on the use of land, water,
or other natural resources beyond the level otherwise agreed upon for the species covered by the Agreement
without the consent of the permittee.
(B) If the Director determines additional conservation measures are necessary to respond to unforeseen
circumstances, the Director may require additional measures of the permittee where the Agreement is being
properly implemented, but only if such measures maintain the original terms of the Agreement to the maximum
extent possible. Additional conservation measures will not involve the commitment of additional land, water, or
financial compensation or additional restrictions on the use of land, water, or other natural resources otherwise
available for development or use under the original terms of the Agreement without the consent of the permittee.
(C) The Director will have the burden of demonstrating that unforeseen circumstances exist, using the best
scientific and commercial data available. These findings must be clearly documented and based upon reliable
technical information regarding the status and habitat requirements of the affected species. The Director will
consider, but not be limited to, the following factors:
(1) Size of the current range of the affected species;
(2) Percentage of range adversely affected by the Agreement;
(3) Percentage of range conserved by the Agreement;
(4) Ecological significance of that portion of the range affected by the Agreement;
(5) Level of knowledge about the affected species and the degree of specificity of the species' conservation
program under the Agreement; and
(6) Whether failure to adopt additional conservation measures would appreciably reduce the likelihood of survival
and recovery of the affected species in the wild.
(6) Additional actions. Nothing in this rule will be construed to limit or constrain the Director, any Federal, State,
local or Tribal government agency, or a private entity, from taking additional actions at its own expense to protect
or conserve a species included in a CCAA.
(7) Criteria for revocation. The Director may not revoke a permit issued under paragraph (d) of this section except
as provided in this paragraph. The Director may revoke a permit for any reason set forth in §13.28(a)(1) through
(4) of this subchapter. The Director may revoke a permit if continuation of the permitted activity would either
appreciably reduce the likelihood of survival and recovery in the wild of any listed species or directly or indirectly
alter designated critical habitat such that it appreciably diminishes the value of that critical habitat for both the
survival and recovery of a listed species. Before revoking a permit for either of the latter two reasons, the Director,
with the consent of the permittee, will pursue all appropriate options to avoid permit revocation. These options may
include, but are not limited to: extending or modifying the existing permit, capturing and relocating the species,
compensating the landowner to forgo the activity, purchasing an easement or fee simple interest in the property, or
arranging for a third-party acquisition of an interest in the property.
(8) Duration. The duration of a CCAA covered by a permit issued under this paragraph (d) must be sufficient to
achieve a net conservation benefit to the species covered by the permit and the Agreement and otherwise comply
with the Candidate Conservation Agreement with Assurances policy available from the Service.
(e) Objection to permit issuance. (1) In regard to any notice of a permit application published in the Federal
Register, any interested party that objects to the issuance of a permit, in whole or in part, may, during the comment
period specified in the notice, request notification of the final action to be taken on the application. A separate
written request shall be made for each permit application. Such a request shall specify the Service's permit
application number and state the reasons why that party believes the applicant does not meet the issuance criteria
contained in §§13.21 and 17.22 of this subchapter or other reasons why the permit should not be issued.
(2) If the Service decides to issue a permit contrary to objections received pursuant to paragraph (c)(1) of this
section, then the Service shall, at least ten days prior to issuance of the permit, make reasonable efforts to contact
by telephone or other expedient means, any party who has made a request pursuant to paragraph (c)(1) of this
section and inform that party of the issuance of the permit. However, the Service may reduce the time period or
dispense with such notice if it determines that time is of the essence and that delay in issuance of the permit
would: (i) Harm the specimen or population involved; or (ii) unduly hinder the actions authorized under the permit.
(3) The Service will notify any party filing an objection and request for notice under paragraph (c)(1) of this section
of the final action taken on the application, in writing. If the Service has reduced or dispensed with the notice
period referred to in paragraph (c)(2) of this section, it will include its reasons therefore in such written notice.
[50 FR 39687, Sept. 30, 1985, as amended at 63 FR 8871, Feb. 23, 1998; 63 FR 52635, Oct. 1, 1998; 64 FR
32711, June 17, 1999; 64 FR 52676, Sept. 30, 1999; 69 FR 24092, May 3, 2004; 69 FR 29670, May 25, 2004; 69
FR 71731, Dec. 10, 2004; 81 FR 95055, Dec. 27, 2016]
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§17.23 Economic hardship permits.
Upon receipt of a complete application, the Director may issue a permit authorizing any activity otherwise
prohibited by §17.21, in accordance with the issuance criteria of this section in order to prevent undue economic
hardship. The Director shall publish notice in the Federal Register of each application for a permit that is made
under this section. Each notice shall invite the submission from interested parties, within 30 days after the date of
the notice, of written data, views, or arguments with respect to the application. The 30-day period may be waived
by the Director in an emergency situation where the life or health of an endangered animal is threatened and no
reasonable alternative is available to the applicant. Notice of any such waiver shall be published in the Federal
Register within 10 days following issuance of the permit.
(a) Application requirements. Applications for permits under this section must be submitted to the Director by the
person allegedly suffering undue economic hardship because his desired activity is prohibited by §17.21. Each
application must be submitted on an official application form (Form 3-200) provided by the Service, and must
include, as an attachment, all of the information required in §17.22 plus the following additional information:
(1) The possible legal, economic or subsistence alternatives to the activity sought to be authorized by the permit;
(2) A full statement, accompanied by copies of all relevant contracts and correspondence, showing the applicant's involvement with the wildlife sought to be covered by the permit (as well as his involvement with similar
wildlife), including, where applicable, that portion of applicant's income derived from the taking of such wildlife, or
the subsistence use of such wildlife, during the calendar year immediately preceding either the notice in
the Federal Register of review of the status of the species or of the proposal to list such wildlife as endangered,
whichever is earliest;
(3) Where applicable, proof of a contract or other binding legal obligation which:
(i) Deals specifically with the wildlife sought to be covered by the permit;
(ii) Became binding prior to the date when the notice of a review of the status of the species or the notice of
proposed rulemaking proposing to list such wildlife as endangered was published in the Federal
Register,whichever is earlier; and
(iii) Will cause monetary loss of a given dollar amount if the permit sought under this section is not granted.
(b) Issuance criteria. Upon receiving an application completed in accordance with paragraph (a) of this section, the
Director will decide whether or not a permit should be issued under any of the three categories of economic
hardship, as defined in section 10(b)(2) of the Act. In making his decisions, the Director shall consider, in addition
to the general criteria in §13.21(b) of this subchapter, the following factors:
(1) Whether the purpose for which the permit is being requested is adequate to justify removing from the wild or
otherwise changing the status of the wildlife sought to be covered by the permit;
(2) The probable direct and indirect effect which issuing the permit would have on the wild populations of the
wildlife sought to be covered by the permit;
(3) The economic, legal, subsistence, or other alternatives or relief available to the applicant;
(4) The amount of evidence that the applicant was in fact party to a contract or other binding legal obligation which;
(i) Deals specifically with the wildlife sought to be covered by the permit; and
(ii) Became binding prior to the date when the notice of a review of the status of the species or the notice of
proposed rulemaking proposing to list such wildlife as endangered was published in the Federal
Register,whichever is earlier.
(5) The severity of economic hardship which the contract or other binding legal obligation referred to in paragraph
(b)(4) of this section would cause if the permit were denied;
(6) Where applicable, the portion of the applicant's income which would be lost if the permit were denied, and the
relationship of that portion to the balance of his income;
(7) Where applicable, the nature and extent of subsistence taking generally by the applicant; and
(8) The likelihood that applicant can reasonably carry out his desired activity within one year from the date a notice
is published in the Federal Register to review status of such wildlife, or to list such wildlife as endangered,
whichever is earlier.
(c) Permit conditions. In addition to the general conditions set forth in part 13 of this subchapter, every permit
issued under this section shall be subject to the following special conditions:
(1) In addition to any reporting requirements contained in the permit itself, the permittee shall also submit to the
Director a written report of his activities pursuant to the permit. Such report must be postmarked or actually
delivered no later than 10 days after completion of the activity.
(2) The death or escape of all living wildlife covered by the permit shall be immediately reported to the Service's
office designated in the permit.
(d) Duration of permits issued under this section shall be designated on the face of the permit. No permit issued
under this section, however, shall be valid for more than one year from the date a notice is published in
the Federal Register to review status of such wildlife, or to list such wildlife as endangered, whichever is earlier.
[40 FR 44415, Sept. 26, 1975, as amended at 40 FR 53400, Nov. 18, 1975; 40 FR 58307, Dec. 16, 1975; 50 FR
39688, Sept. 30, 1985]
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Subpart D—Threatened Wildlife
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§17.31 Prohibitions.
(a) Except as provided in §§17.4 through 17.8, or in a permit issued under this subpart, all of the provisions of
§17.21, except §17.21(c)(5), shall apply to threatened species of wildlife that were added to the List of Endangered
and Threatened Wildlife in §17.11(h) on or prior to September 26, 2019, unless the Secretary has promulgated
species-specific provisions (see paragraph (c) of this section).
(b) In addition to any other provisions of this part, any employee or agent of the Service, of the National Marine
Fisheries Service, or of a State conservation agency that is operating a conservation program pursuant to the
terms of a cooperative agreement with the Service in accordance with section 6(c) of the Act, who is designated by
that agency for such purposes, may, when acting in the course of official duties, take those threatened species of
wildlife that are covered by an approved cooperative agreement to carry out conservation programs.
(c) Whenever a species-specific rule in §§17.40 through 17.48 applies to a threatened species, none of the
provisions of paragraphs (a) and (b) of this section will apply. The species-specific rule will contain all the
applicable prohibitions and exceptions.
[84 FR 44760, Aug. 27, 2019]
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§17.32 Permits—general.
Upon receipt of a complete application the Director may issue a permit for any activity otherwise prohibited with
regard to threatened wildlife. Such permit shall be governed by the provisions of this section unless a special rule
applicable to the wildlife, appearing in §§17.40 to 17.48, of this part provides otherwise. Permits issued under this
section must be for one of the following purposes: Scientific purposes, or the enhancement of propagation or
survival, or economic hardship, or zoological exhibition, or educational purposes, or incidental taking, or special
purposes consistent with the purposes of the Act. Such permits may authorize a single transaction, a series of
transactions, or a number of activities over a specific period of time.
(a)(1) Application requirements for permits for scientific purposes, or the enhancement of propagation or survival,
or economic hardship, or zoological exhibition, or educational purposes, or special purposes consistent with the
purposes of the Act. A person wishing to get a permit for an activity prohibited by §17.31 submits an application for
activities under this paragraph. The Service provides Form 3-200 for the application to which as much of the
following information relating to the purpose of the permit must be attached:
(i) The Common and scientific names of the species sought to be covered by the permit, as well as the number,
age, and sex of such species, and the activity sought to be authorized (such as taking, exporting, selling in
interstate commerce);
(ii) A statement as to whether, at the time of application, the wildlife sought to be covered by the permit (A) is still in
the wild, (B) has already been removed from the wild, or (C) was born in captivity;
(iii) A resume of the applicant's attempts to obtain the wildlife sought to be covered by the permit in a manner
which would not cause the death or removal from the wild of such wildlife;
(iv) If the wildlife sought to be covered by the permit has already been removed from the wild, the country and
place where such removal occurred; if the wildlife sought to be covered by permit was born in captivity, the country
and place where such wildlife was born;
(v) A complete description and address of the institution or other facility where the wildlife sought to be covered by
the permit will be used, displayed, or maintained;
(vi) If the applicant seeks to have live wildlife covered by the permit, a complete description, including photographs
or diagrams, of the facilities to house and/or care for the wildlife and a resume of the experience of those persons
who will be caring for the wildlife;
(vii) A full statement of the reasons why the applicant is justified in obtaining a permit including the details of the
activities sought to be authorized by the permit;
(viii) If the application is for the purpose of enhancement of propagation, a statement of the applicant's willingness
to participate in a cooperative breeding program and to maintain or contribute data to a studbook;
(2) Issuance criteria. Upon receiving an application completed in accordance with paragraph (a)(1) of this section,
the Director will decide whether or not a permit should be issued. In making this decision, the Director shall
consider, in addition to the general criteria in §13.21(b) of this subchapter, the following factors:
(i) Whether the purpose for which the permit is required is adequate to justify removing from the wild or otherwise
changing the status of the wildlife sought to be covered by the permit;
(ii) The probable direct and indirect effect which issuing the permit would have on the wild populations of the
wildlife sought to be covered by the permit;
(iii) Whether the permit, if issued, would in any way, directly or indirectly, conflict with any known program intended
to enhance the survival probabilities of the population from which the wildlife sought to be covered by the permit
was or would be removed;
(iv) Whether the purpose for which the permit is required would be likely to reduce the threat of extinction facing
the species of wildlife sought to be covered by the permit;
(v) The opinions or views of scientists or other persons or organizations having expertise concerning the wildlife or
other matters germane to the application; and
(vi) Whether the expertise, facilities, or other resources available to the applicant appear adequate to successfully
accomplish the objectives stated in the application.
(3) Permit conditions. In addition to the general conditions set forth in part 13 of this subchapter, every permit
issued under this paragraph shall be subject to the special condition that the escape of living wildlife covered by
the permit shall be immediately reported to the Service office designated in the permit.
(4) Duration of permits. The duration of permits issued under this paragraph shall be designated on the face of the
permit.
(b)(1) Application requirements for permits for incidental taking. (i) A person wishing to get a permit for an activity
prohibited by §17.31 submits an application for activities under this paragraph.
(ii) The director shall publish notice in the Federal Register of each application for a permit that is made under this
section. Each notice shall invite the submission from interested parties, within 30 days after the date of the notice,
of written data, views, or arguments with respect to the application.
(iii) Each application must be submitted on an official application (Form 3-200) provided by the Service, and must
include as an attachment, all of the following information:
(A) A complete description of the activity sought to be authorized;
(B) The common and scientific names of the species sought to be covered by the permit, as well as the number,
age, and sex of such species, if known;
(C) A conservation plan that specifies:
(1) The impact that will likely result from such taking;
(2) What steps the applicant will take to monitor, minimize, and mitigate such impacts, the funding that will be
available to implement such steps, and the procedures to be used to deal with unforeseen circumstances;
(3) What alternative actions to such taking the applicant considered and the reasons why such alternatives are not
proposed to be utilized; and
(4) Such other measures that the Director may require as being necessary or appropriate for purposes of the plan.
(2) Issuance criteria. (i) Upon receiving an application completed in accordance with paragraph (b)(1) of this
section, the Director will decide whether or not a permit should be issued. The Director shall consider the general
issuance criteria in 13.21(b) of this subchapter, except for 13.21(b)(4), and shall issue the permit if he or she finds
that:
(A) The taking will be incidental;
(B) The applicant will, to the maximum extent practicable, minimize and mitigate the impacts of such takings;
(C) The applicant will ensure that adequate funding for the conservation plan and procedures to deal with
unforeseen circumstances will be provided;
(D) The taking will not appreciably reduce the likelihood of the survival and recovery of the species in the wild;
(E) The measures, if any, required under paragraph (b)(1)(iii)(D) of this section will be met; and
(F) He or she has received such other assurances as he or she may require that the plan will be implemented.
(ii) In making his or her decision, the Director shall also consider the anticipated duration and geographic scope of
the applicant's planned activities, including the amount of listed species habitat that is involved and the degree to
which listed species and their habitats are affected.
(3) Permit conditions. In addition to the general conditions set forth in part 13 of this subchapter, every permit
issued under this paragraph shall contain such terms and conditions as the Director deems necessary or
appropriate to carry out the purposes of the permit and the conservation plan including, but not limited to,
monitoring and reporting requirements deemed necessary for determining whether such terms and conditions are
being complied with. The Director shall rely upon existing reporting requirements to the maximum extent
practicable.
(4) Duration of permits. The duration of permits issued under this paragraph shall be sufficient to provide adequate
assurances to the permittee to commit funding necessary for the activities authorized by the permit, including
conservation activities and land use restrictions. In determining the duration of a permit, the Director shall consider
the duration of the planned activities, as well as the possible positive and negative effects associated with permits
of the proposed duration on listed species, including the extent to which the conservation plan will enhance the
habitat of listed species and increase the long-term survivability of such species.
(5) Assurances provided to permittee in case of changed or unforeseen circumstances. The assurances in this
paragraph (b)(5) apply only to incidental take permits issued in accordance with paragraph (b)(2) of this section
where the conservation plan is being properly implemented, and apply only with respect to species adequately
covered by the conservation plan. These assurances cannot be provided to Federal agencies. This rule does not
apply to incidental take permits issued prior to March 25, 1998. The assurances provided in incidental take permits
issued prior to March 25, 1998 remain in effect, and those permits will not be revised as a result of this rulemaking.
(i) Changed circumstances provided for in the plan. If additional conservation and mitigation measures are
deemed necessary to respond to changed circumstances and were provided for in the plan's operating
conservation program, the permittee will implement the measures specified in the plan.
(ii) Changed circumstances not provided for in the plan. If additional conservation and mitigation measures are
deemed necessary to respond to changed circumstances and such measures were not provided for in the plan's
operating conservation program, the Director will not require any conservation and mitigation measures in addition
to those provided for in the plan without the consent of the permittee, provided the plan is being properly
implemented.
(iii) Unforeseen circumstances. (A) In negotiating unforeseen circumstances, the Director will not require the
commitment of additional land, water, or financial compensation or additional restrictions on the use of land, water,
or other natural resources beyond the level otherwise agreed upon for the species covered by the conservation
plan without the consent of the permittee.
(B) If additional conservation and mitigation measures are deemed necessary to respond to unforeseen
circumstances, the Director may require additional measures of the permittee where the conservation plan is being
properly implemented, but only if such measures are limited to modifications within conserved habitat areas, if any,
or to the conservation plan's operating conservation program for the affected species, and maintain the original
terms of the conservation plan to the maximum extent possible. Additional conservation and mitigation measures
will not involve the commitment of additional land, water or financial compensation or additional restrictions on the
use of land, water, or other natural resources otherwise available for development or use under the original terms
of the conservation plan without the consent of the permittee.
(C) The Director will have the burden of demonstrating that such unforeseen circumstances exist, using the best
scientific and commercial data available. These findings must be clearly documented and based upon reliable
technical information regarding the status and habitat requirements of the affected species. The Director will
consider, but not be limited to, the following factors:
(1) Size of the current range of the affected species;
(2) Percentage of range adversely affected by the conservation plan;
(3) Percentage of range conserved by the conservation plan;
(4) Ecological significance of that portion of the range affected by the conservation plan;
(5) Level of knowledge about the affected species and the degree of specificity of the species' conservation
program under the conservation plan; and
(6) Whether failure to adopt additional conservation measures would appreciably reduce the likelihood of survival
and recovery of the affected species in the wild.
(6) Nothing in this rule will be construed to limit or constrain the Director, any Federal, State, local, or Tribal
government agency, or a private entity, from taking additional actions at its own expense to protect or conserve a
species included in a conservation plan.
(7) Discontinuance of permit activity. Notwithstanding the provisions of §13.26 of this subchapter, a permittee
under this paragraph (b) remains responsible for any outstanding minimization and mitigation measures required
under the terms of the permit for take that occurs prior to surrender of the permit and such minimization and
mitigation measures as may be required pursuant to the termination provisions of an implementing agreement,
habitat conservation plan, or permit even after surrendering the permit to the Service pursuant to §13.26 of this
subchapter. The permit shall be deemed canceled only upon a determination by the Service that such minimization
and mitigation measures have been implemented. Upon surrender of the permit, no further take shall be
authorized under the terms of the surrendered permit.
(8) Criteria for revocation. A permit issued under paragraph (b) of this section may not be revoked for any reason
except those set forth in §13.28(a)(1) through (4) of this subchapter or unless continuation of the permitted activity
would be inconsistent with the criterion set forth in 16 U.S.C. 1539(a)(2)(B)(iv) and the inconsistency has not been
remedied.
(c)(1) Application requirements for permits for the enhancement of survival through Safe Harbor Agreements. The
applicant must submit an application for a permit under this paragraph (c) to the appropriate Regional Director,
U.S. Fish and Wildlife Service, for the Region where the applicant resides or where the proposed action is to occur
(for appropriate addresses, see 50 CFR 10.22), if the applicant wishes to engage in any activity prohibited by
§17.31. The applicant must submit an official Service application form (3-200.54) that includes the following
information:
(i) The common and scientific names of the listed species for which the applicant requests incidental take
authorization;
(ii) A description of how incidental take of the covered species pursuant to the Safe Harbor Agreement is likely to
occur, both as a result of management activities and as a result of the return to baseline;
(iii) A Safe Harbor Agreement that complies with the requirements of the Safe Harbor policy available from the
Service; and
(iv) The Director must publish notice in the Federal Register of each application for a permit that is made under
this paragraph (c). Each notice must invite the submission from interested parties within 30 days after the date of
the notice of written data, views, or arguments with respect to the application. The procedures included in
§17.22(e) for permit objection apply to any notice published by the Director under this paragraph (c).
(2) Issuance criteria. Upon receiving an application completed in accordance with paragraph (c)(1) of this section,
the Director will decide whether or not to issue a permit. The Director shall consider the general issuance criteria in
§13.21(b) of this subchapter, except for §13.21(b)(4), and may issue the permit if he or she finds:
(i) The take will be incidental to an otherwise lawful activity and will be in accordance with the terms of the Safe
Harbor Agreement;
(ii) The implementation of the terms of the Safe Harbor Agreement is reasonably expected to provide a net
conservation benefit to the affected listed species by contributing to the recovery of listed species included in the
permit, and the Safe Harbor Agreement otherwise complies with the Safe Harbor policy available from the Service;
(iii) The probable direct and indirect effects of any authorized take will not appreciably reduce the likelihood of
survival and recovery in the wild of any listed species;
(iv) Implementation of the terms of the Safe Harbor Agreement is consistent with applicable Federal, State, and
Tribal laws and regulations;
(v) Implementation of the terms of the Safe Harbor Agreement will not be in conflict with any ongoing conservation
or recovery programs for listed species covered by the permit; and
(vi) The applicant has shown capability for and commitment to implementing all of the terms of the Safe Harbor
Agreement.
(3) Permit conditions. In addition to any applicable general permit conditions set forth in part 13 of this subchapter,
every permit issued under this paragraph (c) is subject to the following special conditions:
(i) A requirement for the participating property owner to notify the Service of any transfer of lands subject to a Safe
Harbor Agreement;
(ii) When appropriate, a requirement for the permittee to give the Service reasonable advance notice (generally at
least 30 days) of when he or she expects to incidentally take any listed species covered under the permit. Such
notification will provide the Service with an opportunity to relocate affected individuals of the species, if possible
and appropriate; and
(iii) Any additional requirements or conditions the Director deems necessary or appropriate to carry out the
purposes of the permit and the Safe Harbor Agreement.
(4) Permit effective date. Permits issued under this paragraph (c) become effective the day of issuance for species
covered by the Safe Harbor Agreement.
(5) Assurances provided to permittee. (i) The assurances in subparagraph (ii) of this paragraph (c)(5) apply only to
Safe Harbor permits issued in accordance with paragraph (c)(2) of this section where the Safe Harbor Agreement
is being properly implemented, and apply only with respect to species covered by the Agreement and permit.
These assurances cannot be provided to Federal agencies. The assurances provided in this section apply only to
Safe Harbor permits issued after July 19, 1999.
(ii) The Director and the permittee may agree to revise or modify the management measures set forth in a Safe
Harbor Agreement if the Director determines that such revisions or modifications do not change the Director's prior
determination that the Safe Harbor Agreement is reasonably expected to provide a net conservation benefit to the
listed species. However, the Director may not require additional or different management activities to be
undertaken by a permittee without the consent of the permittee.
(6) Additional actions. Nothing in this rule will be construed to limit or constrain the Director, any Federal, State,
local or Tribal government agency, or a private entity, from taking additional actions at its own expense to protect
or conserve a species included in a Safe Harbor Agreement.
(7) Criteria for revocation. The Director may not revoke a permit issued under paragraph (c) of this section except
as provided in this paragraph. The Director may revoke a permit for any reason set forth in §13.28(a)(1) through
(4) of this subchapter. The Director may revoke a permit if continuation of the permitted activity would either
appreciably reduce the likelihood of survival and recovery in the wild of any listed species or directly or indirectly
alter designated critical habitat such that it appreciably diminishes the value of that critical habitat for both the
survival and recovery of a listed species. Before revoking a permit for either of the latter two reasons, the Director,
with the consent of the permittee, will pursue all appropriate options to avoid permit revocation. These options may
include, but are not limited to: extending or modifying the existing permit, capturing and relocating the species,
compensating the landowner to forgo the activity, purchasing an easement or fee simple interest in the property, or
arranging for a third-party acquisition of an interest in the property.
(8) Duration of permits. The duration of permits issued under this paragraph (c) must be sufficient to provide a net
conservation benefit to species covered in the enhancement of survival permit. In determining the duration of a
permit, the Director will consider the duration of the planned activities, as well as the positive and negative effects
associated with permits of the proposed duration on covered species, including the extent to which the
conservation activities included in the Safe Harbor Agreement will enhance the survival and contribute to the
recovery of listed species included in the permit.
(d)(1) Application requirements for permits for the enhancement of survival through Candidate Conservation
Agreements with Assurances (CCAAs). The applicant must submit an application for a permit under this paragraph
(d) to the appropriate Regional Director, U.S. Fish and Wildlife Service, for the Region where the applicant resides
or where the proposed activity is to occur (for appropriate addresses, see 50 CFR 10.22). When a species covered
by a CCAA is listed as threatened and the applicant wishes to engage in activities identified in the Agreement and
otherwise prohibited by §17.31, the applicant must apply for an enhancement of survival permit for species
covered by the Agreement. The permit will become valid if and when covered proposed, candidate or other
unlisted species is listed as a threatened species. The applicant must submit an official Service application form
(3-200.54) that includes the following information:
(i) The common and scientific names of the species for which the applicant requests incidental take authorization;
(ii) A description of the land use or water management activity for which the applicant requests incidental take
authorization; and
(iii) A CCAA that complies with the requirements of the Candidate Conservation Agreement with Assurances policy
available from the Service.
(iv) The Director must publish notice in the Federal Register of each application for a permit that is made under
this paragraph (d). Each notice must invite the submission from interested parties within 30 days after the date of
the notice of written data, views, or arguments with respect to the application. The procedures included in
§17.22(e) for permit objection apply to any notice published by the Director under this paragraph (d).
(2) Issuance criteria. Upon receiving an application completed in accordance with paragraph (d)(1) of this section,
the Director will decide whether or not to issue a permit. The Director shall consider the general issuance criteria in
§13.21(b) of this subchapter, except for §13.21(b)(4), and may issue the permit if he or she finds:
(i) The take will be incidental to an otherwise lawful activity and will be in accordance with the terms of the CCAA;
(ii) The implementation of the terms of the CCAA is reasonably expected to provide a net conservation benefit to
the affected covered species by contributing to the conservation of the species included in the permit, and the
CCAA otherwise complies with the Candidate Conservation Agreement with Assurances policy available from the
Service;
(iii) The probable direct and indirect effects of any authorized take will not appreciably reduce the likelihood of
survival and recovery in the wild of any species;
(iv) Implementation of the terms of the CCAA is consistent with applicable Federal, State, and Tribal laws and
regulations;
(v) Implementation of the terms of the CCAA will not be in conflict with any ongoing conservation programs for
species covered by the permit; and
(vi) The applicant has shown capability for and commitment to implementing all of the terms of the Candidate
Conservation Agreement.
(3) Permit conditions. In addition to any applicable general permit conditions set forth in part 13 of this subchapter,
every permit issued under this paragraph (d) is subject to the following special conditions:
(i) A requirement for the property owner to notify the Service of any transfer of lands subject to a CCAA;
(ii) When appropriate, a requirement for the permittee to give the Service reasonable advance notice (generally at
least 30 days) of when he or she expects to incidentally take any listed species covered under the permit. Such
notification will provide the Service with an opportunity to relocate affected individuals of the species, if possible
and appropriate; and
(iii) Any additional requirements or conditions the Director deems necessary or appropriate to carry out the
purposes of the permit and the CCAA.
(4) Permit effective date. Permits issued under this paragraph (d) become effective for a species covered by a
CCAA on the effective date of a final rule that lists a covered species as threatened.
(5) Assurances provided to permittee in case of changed or unforeseen circumstances. The assurances in this
paragraph (d)(5) apply only to permits issued in accordance with paragraph (d)(2) where the CCAA is being
properly implemented, and apply only with respect to species adequately covered by the CCAA. These
assurances cannot be provided to Federal agencies.
(i) Changed circumstances provided for in the Agreement. If the Director determines that additional conservation
measures are necessary to respond to changed circumstances and these measures were set forth in the
Agreement, the permittee will implement the measures specified in the Agreement.
(ii) Changed circumstances not provided for in the Agreement. If the Director determines that additional
conservation measures not provided for in the Agreement are necessary to respond to changed circumstances,
the Director will not require any conservation measures in addition to those provided for in the Agreement without
the consent of the permittee, provided the Agreement is being properly implemented.
(iii) Unforeseen circumstances. (A) In negotiating unforeseen circumstances, the Director will not require the
commitment of additional land, water, or financial compensation or additional restrictions on the use of land, water,
or other natural resources beyond the level otherwise agreed upon for the species covered by the Agreement
without the consent of the permittee.
(B) If the Director determines additional conservation measures are necessary to respond to unforeseen
circumstances, the Director may require additional measures of the permittee where the Agreement is being
properly implemented, but only if such measures maintain the original terms of the Agreement to the maximum
extent possible. Additional conservation measures will not involve the commitment of additional land, water, or
financial compensation or additional restrictions on the use of land, water, or other natural resources otherwise
available for development or use under the original terms of the Agreement without the consent of the permittee.
(C) The Director will have the burden of demonstrating that unforeseen circumstances exist, using the best
scientific and commercial data available. These findings must be clearly documented and based upon reliable
technical information regarding the status and habitat requirements of the affected species. The Director will
consider, but not be limited to, the following factors:
(1) Size of the current range of the affected species;
(2) Percentage of range adversely affected by the Agreement;
(3) Percentage of range conserved by the Agreement;
(4) Ecological significance of that portion of the range affected by the Agreement;
(5) Level of knowledge about the affected species and the degree of specificity of the species' conservation
program under the Agreement; and
(6) Whether failure to adopt additional conservation measures would appreciably reduce the likelihood of survival
and recovery of the affected species in the wild.
(6) Additional actions. Nothing in this rule will be construed to limit or constrain the Director, any Federal, State,
local or Tribal government agency, or a private entity, from taking additional actions at its own expense to protect
or conserve a species included in a CCAA.
(7) Criteria for revocation. The Director may not revoke a permit issued under paragraph (d) of this section except
as provided in this paragraph. The Director may revoke a permit for any reason set forth in §13.28(a)(1) through
(4) of this subchapter. The Director may revoke a permit if continuation of the permitted activity would either
appreciably reduce the likelihood of survival and recovery in the wild of any listed species or directly or indirectly
alter designated critical habitat such that it appreciably diminishes the value of that critical habitat for both the
survival and recovery of a listed species. Before revoking a permit for either of the latter two reasons, the Director,
with the consent of the permittee, will pursue all appropriate options to avoid permit revocation. These options may
include, but are not limited to: extending or modifying the existing permit, capturing and relocating the species,
compensating the landowner to forgo the activity, purchasing an easement or fee simple interest in the property, or
arranging for a third-party acquisition of an interest in the property.
(8) Duration. The duration of a CCAA covered by a permit issued under this paragraph (d) must be sufficient to
achieve a net conservation benefit to the species covered by the permit and the Agreement and otherwise comply
with the Candidate Conservation Agreement with Assurances policy available from the Service.
[50 FR 39689, Sept. 30, 1985, as amended at 63 FR 8871, Feb. 23, 1998; 63 FR 52635, Oct. 1, 1998; 64 FR
32714, June 17, 1999; 64 FR 52676, Sept. 30, 1999; 69 FR 24093, May 3, 2004; 69 FR 29670, May 25, 2004; 69
FR 71731, Dec. 10, 2004; 81 FR 95055, Dec. 27, 2016]
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§17.40 Special rules—mammals.
(a) Mazama pocket gophers (Olympia, Roy Prairie, Tenino, and Yelm) (Thomomys mazama pugetensis, glacialis,
tumuli, and yelmensis)—(1) Which populations of the Mazama pocket gopher are covered by this special
rule? This special rule covers the four Thurston/Pierce subspecies of the Mazama pocket gopher (Olympia, Roy
Prairie, Tenino, and Yelm) (Thomomys mazama pugetensis, glacialis, tumuli, and yelmensis) wherever they occur.
(2) What activities are prohibited? Except as noted in paragraphs (a)(3) through (7) of this section, all prohibitions
of §17.31 apply to the Olympia, Roy Prairie, Tenino, and Yelm pocket gophers.
(3) What activities are allowed on civilian airports? Incidental take of the Olympia, Roy Prairie, Tenino, and Yelm
pocket gophers will not be a violation of section 9 of the Act, if the incidental take results from non-Federal routine
maintenance activities in or adjacent to Mazama pocket gopher habitat and associated with airport operations on
civilian airports. Routine maintenance activities include the following:
(i) Routine management, repair, and maintenance of runways, roads, and taxiways (does not include upgrades, or
construction of new runways, roads, or taxiways, or new development at airports);
(ii) Hazing of hazardous wildlife;
(iii) Management of forage, water, and shelter to reduce the attractiveness of the area around airports for
hazardous wildlife; and
(iv) Control or other management of noxious weeds and invasive plants through mowing, discing, herbicide and
fungicide application, fumigation, or burning. Use of herbicides, fungicides, fumigation, and burning must occur in
such a way that nontarget plants are avoided to the maximum extent practicable.
(4) What agricultural activities are allowed on non-Federal lands? Incidental take of the Olympia, Roy Prairie,
Tenino, and Yelm pocket gophers will not be a violation of section 9 of the Act, if the incidental take results from
agricultural or horticultural (farming) practices implemented on such lands consistent with State laws on non-
Federal lands. For the purposes of this special rule, farm means any facility, including land, buildings,
watercourses, and appurtenances, used in the commercial production of crops, nursery or orchard stock, the
propagation and raising of nursery or orchard stock, livestock or poultry, or livestock or poultry products.
(i) For the purposes of this special rule, an agricultural (farming) practice means a mode of operation on a farm
that:
(A) Is or may be used on a farm of a similar nature;
(B) Is a generally accepted, reasonable, and prudent method for the operation of the farm to obtain a profit in
money;
(C) Is or may become a generally accepted, reasonable, and prudent method in conjunction with farm use;
(D) Complies with applicable State laws;
(E) Is done in a reasonable and prudent manner.
(ii) Accepted agricultural or horticultural (farming) practices include:
(A) Grazing;
(B) Routine installation, management, and maintenance of stock water facilities such as stock ponds, berms,
troughs, and tanks, pipelines and watering systems to maintain water supplies;
(C) Routine maintenance or construction of fencing;
(D) Planting, harvest, fertilization, harrowing, tilling, or rotation of crops (Disturbance to the soils shall not exceed a
12-inch (30.5-cm) depth. All activities that do not disturb the soil surface are also allowed, such as haying, baling,
some orchard and berry plant management activities, etc.);
(E) Maintenance of livestock management facilities such as corrals, sheds, and other ranch outbuildings;
(F) Repair and maintenance of unimproved agricultural roads (This exemption does not include improvement,
upgrade, or construction of new roads.);
(G) Placement of mineral supplements, plant nutrients, or soil amendments;
(H) Harvest, control, or other management of noxious weeds and invasive plants through mowing, discing,
herbicide and fungicide application, fumigation, or burning (Use of herbicides, fungicides, fumigation, and burning
must occur in such a way that nontarget plants are avoided to the maximum extent practicable.); and
(I) Deep tillage (usually at depths of 18-36 inches (45.7-91.4 cm), for compaction reduction purposes) occurring
between September 1 and February 28, no more often than once in 10 years.
(5) What noncommercial activities are allowed on single-family residential private land? Incidental take of the
Olympia, Roy Prairie, Tenino, and Yelm pocket gophers will not be a violation of section 9 of the Act, if the
incidental take results from noncommercial activities that occur in or adjacent to Mazama pocket gopher habitat on
existing single-family residential properties. These activities include the following:
(i) Harvest, control, or other management of noxious weeds and invasive plants through mowing, herbicide and
fungicide application, fumigation, or burning. Use of herbicides, fungicides, fumigation, and burning must occur in
such a way that nontarget plants are avoided to the maximum extent practicable;
(ii) Construction and placement of fencing, garden plots, or play equipment; and
(iii) Construction and placement of dog kennels, carports, or storage sheds less than 120 ft2 (11.15 m2) in size.
(6) What noxious weed and invasive plant control activities are allowed on non-Federal lands? Incidental take of
the Olympia, Roy Prairie, Tenino, and Yelm pocket gophers will not be a violation of section 9 of the Act, if the
incidental take results from routine removal or other management of noxious weeds and invasive plants. Routine
removal or other management of noxious weeds and invasive plants are limited to the following, and must be
conducted in a way that impacts to nontarget plants are avoided to the maximum extent practicable:
(i) Mowing;
(ii) Discing;
(iii) Herbicide and fungicide application;
(iv) Fumigation; and
(v) Burning.
(7) What roadside right-of-way maintenance activities are allowed on Federal and non-Federal lands? Incidental
take of the Olympia, Roy Prairie, Tenino, and Yelm pocket gophers will not be a violation of section 9 of the Act, if
the incidental take results from routine maintenance of roadside rights-of-way on Federal and non-Federal lands.
Routine maintenance activities of roadside rights-of-way of highways and roads are limited to the following, and
must be conducted in a way that impacts to nontarget plants are avoided to the maximum extent practicable:
(i) Mowing;
(ii) Mechanical removal of noxious weeds or invasive plants;
(iii) Selective application of herbicides for removal of noxious weeds or invasive plants; and
(iv) Repair or maintenance of fences.
(b) Grizzly bear (Ursus arctos horribilis)—(1) Prohibitions. The following prohibitions apply to the grizzly bear:
(i) Taking. (A) Except as provided in paragraphs (b)(1)(i)(B) through (F) of this section, no person shall take any
grizzly bear in the 48 conterminous states of the United States.
(B) Grizzly bears may be taken in self-defense or in defense of others, but such taking shall be reported by the
individual who has taken the bear or his designee within 5 days of occurrence to the Resident Agent in Charge,
Office of Law Enforcement, U.S. Fish and Wildlife Service, 2900 4th Avenue North, Suite 301, Billings, MT 59101
(406-247-7355), if occurring in Montana or Wyoming, or the Special Agent in Charge, Office of Law Enforcement,
U.S. Fish and Wildlife Service, P.O. Box 9, Sherwood, OR 97140 (503-521-5300), if occurring in Idaho or
Washington, and to appropriate State and Tribal authorities. Grizzly bears taken in self-defense or in defense of
others, including the parts of such bears, shall not be possessed, delivered, carried, transported, shipped,
exported, received, or sold, except by Federal, State, or Tribal authorities.
(C) Removal of nuisance bears. A grizzly bear consituting a demonstrable but non immediate threat to human
safety or committing significant depredations to lawfully present livestock, crops, or beehives may be taken, but
only if:
(1) It has not been reasonably possible to eliminate such threat or depredation by live-capturing and releasing
unharmed in a remote area the grizzly bear involved; and
(2) The taking is done in a humane manner by authorized Federal, State, or Tribal authorities, and in accordance
with current interagency guidelines covering the taking of such nuisance bears; and
(3) The taking is reported within 5 days of occurrence to the appropriate U.S. Fish and Wildlife Service law
enforcement office, as indicated in paragraph (b)(1)(i)(B) of this section, and to appropriate State and Tribal
authorities.
(D) Federal, State, or Tribal scientific or research activities. Federal, State, or Tribal authorities may take grizzly
bears for scientific or research purposes, but only if such taking does not result in death or permanent injury to the
bears involved. Such taking must be reported within 5 days of occurrence to the appropriate U.S. Fish and Wildlife
Service law enforcement office, as indicated in paragraph (b)(1)(i)(B) of this section, and to appropriate State and
Tribal authorities.
(E) [Reserved]
(F) National Parks. The regulations of the National Park Service shall govern all taking of grizzly bears in National
Parks.
(ii) Unlawfully taken grizzly bears. (A) Except as provided in paragraphs (b)(1)(ii)(B) and (iv) of this section, no
person shall possess, deliver, carry, transport, ship, export, receive, or sell any unlawfully taken grizzly bear. Any
unlawful taking of a grizzly bear shall be reported within 5 days of occurrence to the appropriate U.S. Fish and
Wildlife Service law enforcement office, as indicated in paragraph (b)(1)(i)(B) of this section, and to appropriate
State and Tribal authorities.
(B) Authorized Federal, State, or Tribal employees, when acting in the course of their official duties, may, for
scientific or research purposes, possess, deliver, carry, transport, ship, export, or receive unlawfully taken grizzly
bears.
(iii) Import or export. Except as provided in paragraphs (b)(1)(iii) (A) and (B) and (iv) of this section, no person shall
import any grizzly bear into the United States.
(A) Federal, State, or Tribal scientific or research activities. Federal, State, or Tribal authorities may import grizzly
bears into the United States for scientific or research purposes.
(B) Public zoological institution. Public zoological institutions (see 50 CFR 10.12) may import grizzly bears into the
United States.
(iv) Commercial transactions. (A) Except as provided in paragraph (b)(1)(iv)(B) of this section, no person shall, in
the course of commercial activity, deliver, receive, carry, transport, or ship in interstate or foreign commerce any
grizzly bear.
(B) A public zoological institution (see 50 CFR 10.12) dealing with other public zoological institutions may sell
grizzly bears or offer them for sale in interstate or foreign commerce, and may, in the course of commercial activity,
deliver, receive, carry, transport, or ship grizzly bears in interstate or foreign commerce.
(v) Other violations. No person shall attempt to commit, cause to be committed, or solicit another to commit any
act prohibited by paragraph (b)(1) of this section.
(2) Definitions. As used in paragraph (b) of this section:
Grizzly bear means any member of the species Ursus arctos horribilis of the 48 conterminous States of the United
States, including any part, offspring, dead body, part of a dead body, or product of such species.
Grizzly bear accompanied by young means any grizzly bear having offspring, including one or more cubs,
yearlings, or 2-year-olds, in its immediate vicinity.
Identified means permanently marked or documented so as to be identifiable by law enforcement officials at a
subsequent date.
State, Federal or Tribal authority means an employee of State, Federal, or Indian Tribal government who, as part
of his/her official duties, normally handles grizzly bears.
Young grizzly bear means a cub, yearling, or 2-year-old grizzly bear.
eCFR graphic ec01jn91.000.gif
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(c) Primates. (1) Except as noted in paragraph (c)(2) of this section, all provisions of §17.31 apply to the lesser
slow loris (Nycticebus pygmaeus); Philippine tarsier (Tarsius syrichta); white-footed tamarin (Saguinus leucopus);
black howler monkey (Alouatta pigra); stump-tailed macaque (Macaca arctoides); gelada baboon (Theropithecus
gelada);Formosan rock macaque (Macaca cyclopis); Japanese macaque (Macaca fuscata); Toque macaque
(Macaca sinica); long-tailed langur (Presbytis potenziani); and purple-faced langur (Presbytis senex).
(2) The prohibitions referred to above do not apply to any live member of such species held in captivity in the
United States on the effective date of the final rulemaking, or to the progeny of such animals, or to the progeny of
animals legally imported into the United States after the effective date of the final rulemaking, Provided, That the
person wishing to engage in any activity which would otherwise be prohibited must be able to show satisfactory
documentary or other evidence as to the captive status of the particular member of the species on the effective
date of this rulemaking or that the particular member of the species was born in captivity in the United States after
the effective date of this rulemaking. Identification of the particular member to a record in the International Species
Inventory System (ISIS), or to a Federal, State or local government permit, shall be deemed to be satisfactory
evidence. Records in the form of studbooks or inventories, kept in the normal course of business, shall be
acceptable as evidence, provided that a notarized statement is inserted in such record to the effect that:
(i) The records were kept in the normal course of business prior to November 18, 1976, and accurately identify (by
use of markers, tags, or other acceptable marking devices) individual animals; or
(ii) That the individual animal identified by the records was born in captivity on ____(Date).
The notarized statement in paragraph (c)(2)(i) of this section, shall be acceptable only if the notarization is dated
on or before January 3, 1977. The notarized statement in paragraph (c)(2)(ii), of this section, shall be acceptable
only if the notarization is dated within 15 days of the date of birth of the animal.
(d) Gray wolf (Canis lupus) in Minnesota.
(1) Zones. For purposes of these regulations, the State of Minnesota is divided into the following five zones:
(i) Zone 1—4,488 square miles. Beginning at the point of intersection of United States and Canadian boundaries in
Section 22, Township 71 North, Range 22 West, in Rainy Lake, then proceeding along the west side of Sections
22, 27, and 34 in said Township and Sections 3, 10, 15, 22, 27 and 34 in Township 70 North, Range 22 West and
Sections 3 and 10 in Township 69 North, Range 22 West; then east along the south boundaries of Sections 10, 11,
and 12 in said Township; then south along the Koochiching and St. Louis counties line to Highway 53; thence
southeasterly along State Highway 53 to the junction with County Route 765; thence easterly along County Route
765 to the junction with Kabetogama Lake in Ash River Bay; thence along the south boundary of Section 33 in
Township 69 North, Range 19 West, to the junction with the Moose River; thence southeasterly along the Moose
River to Moose Lake; thence along the western shore of Moose Lake to the river between Moose Lake and Long
Lake; thence along the said river to Long Lake; thence along the east shore of Long Lake to the drainage on the
southeast side of Long Lake in NE\1/4\, Section 18, Township 67 North, Range 18 West; thence along the said
drainage southeasterly and subsequently northeasterly to Marion Lake, the drainage being in Sections 17 and 18,
Township 67 North, Range 18 West; thence along the west shoreline of Marion Lake proceeding southeasterly to
the Moose Creek; thence along Moose Creek to Flap Creek; thence southeasterly along Flap Creek to the
Vermilion River; thence southerly along the Vermilion River to Vermilion Lake; thence along the Superior National
Forest boundary in a southeasterly direction through Vermilion Lake passing these points: Oak Narrows, Muskrat
Channel, South of Pine Island, to Hoodo Point and the junction with County Route 697; thence southeasterly on
County Route 697 to the junction with State Highway 169; thence easterly along State Highway 169 to the junction
with State Highway 1; thence easterly along State Highway 1 to the junction with the Erie Railroad tracks at
Murphy City; thence easterly along the Erie Railroad tracks to the junction with Lake Superior at Taconite Harbor;
thence northeasterly along the North Shore of Lake Superior to the Canadian Border; thence westerly along the
Canadian Border to the point of beginning in Rainy Lake.
(ii) Zone 2—1,856 square miles. Beginning at the intersection of the Erie Mining Co. Railroad and State Highway 1
(Murphy City); thence southeasterly on State Highway 1 to the junction with County Road 4; thence southwesterly
on County Road 4 to the State Snowmobile Trail (formerly the Alger-Smith Railroad); thence southwesterly to the
intersection of the Old Railroad Grade and Reserve Mining Co. Railroad in Section 33 of Township 56 North,
Range 9 West; thence northwesterly along the Railroad to Forest Road 107; thence westerly along Forest Road
107 to Forest Road 203; thence westerly along Forest Road 203 to the junction with County Route 2; thence in a
northerly direction on County Route 2 to the junction with Forest Road 122; thence in a westerly direction along
Forest Road 122 to the junction with the Duluth, Missable and Iron Range Railroad; thence in a southwesterly
direction along the said railroad tracks to the junction with County Route 14; thence in a northwesterly direction
along County Route 14 to the junction with County Route 55; thence in a westerly direction along County Route 55
to the junction with County Route 44; thence in a southerly direction along County Route 44 to the junction with
County Route 266; thence in a southeasterly direction along County Route 266 and subsequently in a westerly
direction to the junction with County Road 44; thence in a northerly direction on County Road 44 to the junction
with Township Road 2815; thence westerly along Township Road 2815 to Alden Lake; thence northwesterly across
Alden Lake to the inlet of the Cloquet River; thence northerly along the Cloquet River to the junction with Carrol
Trail-State Forestry Road; thence west along the Carrol Trail to the junction with County Route 4 and County
Route 49; thence west along County Route 49 to the junction with the Duluth, Winnipeg and Pacific Railroad;
thence in a northerly direction along said Railroad to the junction with the Whiteface River; thence in a
northeasterly direction along the Whiteface River to the Whiteface Reservoir; thence along the western shore of
the Whiteface Reservoir to the junction with County Route 340; thence north along County Route 340 to the
junction with County Route 16; thence east along County Route 16 to the junction with County Route 346; thence
in a northerly direction along County Route 346 to the junction with County Route 569; thence along County Route
569 to the junction with County Route 565; thence in a westerly direction along County Route 565 to the junction
with County Route 110; thence in a westerly direction along County Route 110 to the junction with County Route
100; thence in a north and subsequent west direction along County Route 100 to the junction with State Highway
135; thence in a northerly direction along State Highway 135 to the junction with State Highway 169 at Tower;
thence in an easterly direction along the southern boundary of Zone 1 to the point of beginning of Zone 2 at the
junction of the Erie Railroad Tracks and State Highway 1.
(iii) Zone 3—3,501 square miles. Beginning at the junction of State Highway 11 and State Highway 65; thence
southeasterly along State Highway 65 to the junction with State Highway 1; thence westerly along State Highway 1
to the junction with State Highway 72; thence north along State Highway 72 to the junction with an un-numbered
township road beginning in the northeast corner of Section 25, Township 155 North, Range 31 West; thence
westerly along the said road for approximately seven (7) miles to the junction with SFR 95: Thence westerly along
SFR 95 and continuing west through the southern boundary of Sections 36 through 31, Township 155 North,
Range 33 West, through Sections 36 through 31, Township 155 North, Range 34 West, through Sections 36
through 31, Township 155 North, Range 35 West, through Sections 36 and 35, Township 155 North, Range 36
West to the junction with State Highway 89, thence northwesterly along State Highway 89 to the junction with
County Route 44; thence northerly along County Route 44 to the junction with County Route 704; thence northerly
along County 704 to the junction with SFR 49; thence northerly along SFR 49 to the junction with SFR 57; thence
easterly along SFR 57 to the junction with SFR 63: Thence south along SFR 63 to the junction with SFR 70;
thence easterly along SFR 70 to the junction with County Route 87; thence easterly along County Route 87 to the
junction with County Route 1; thence south along County Route 1 to the junction with County Route 16; thence
easterly along County Route 16 to the junction with State Highway 72; thence south on State Highway 72 to the
junction with a gravel road (un-numbered County District Road) on the north side of Section 31, Township 158
North, Range 30 West; thence east on said District Road to the junction with SFR 62; thence easterly on SFR 62
to the junction with SFR 175; thence south on SFR 175 to the junction with County Route 101; thence easterly on
County Route 101 to the junction with County Route 11; thence easterly on County Route 11 to the junction with
State Highway 11; thence easterly on State Highway 11 to the junction with State Highway 65, the point of
beginning.
(iv) Zone 4—20,883 square miles. Excluding Zones 1, 2 and 3, all that part of Minnesota north and east of a line
beginning on State Trunk Highway 48 at the eastern boundary of the state; thence westerly along Highway 48 to
Interstate Highway 35; thence northerly on I-35 to State Highway 23, thence west one-half mile on Highway 23 to
State Trunk Highway 18; thence westerly along Highway 18 to State Trunk Highway 65, thence northerly on
Highway 65 to State Trunk Highway 210; thence westerly along Highway 210 to State Trunk Highway 6; thence
northerly on State Trunk Highway 6 to Emily; thence westerly along County State Aid Highway (CSAH) 1, Crow
Wing County, to CSAH 2, Cass County; thence westerly along CSAH 2 to Pine River; thence northwesterly along
State Trunk Highway 371 to Backus; thence westerly along State Trunk Highway 87 to U.S. Highway 71; thence
northerly along U.S. 71 to State Trunk Highway 200; thence northwesterly along Highway 200, to County State Aid
Highway (CSAH) 2, Clearwater County; thence northerly along CSAH 2 to Shevlin; thence along U.S. Highway 2
to Bagley; thence northerly along State Trunk Highway 92 to Gully; thence northerly along CSAH 2, Polk County,
to CSAH 27, Pennington County; thence along CSAH 27 to State Trunk Highway 1; thence easterly on Highway 1
to CSAH 28, Pennington County; thence northerly along CSAH 28 to CSAH 54, Marshall County, thence northerly
along CSAH 54 to Grygla; thence west and northerly along Highway 89 to Roseau; thence northerly along State
Truck Highway 310 to the Canadian border.
(v) Zone 5—54,603 square miles. All that part of Minnesota south and west of the line described as the south and
west border of Zone 4.
(vi) Map of regulatory zones follows:
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(2) Prohibitions. The following prohibitions apply to the gray wolf in Minnesota.
(i) Taking. Except as provided in this paragraph (d)(2)(i) of this section, no person may take a gray wolf in
Minnesota.
(A) Any person may take a gray wolf in Minnesota in defense of his own life or the lives of others.
(B) Any employee or agent of the Service, any other Federal land management agency, or the Minnesota
Department of Natural Resources, who is designated by his/her agency for such purposes, may, when acting in
the course of his or her official duties, take a gray wolf in Minnesota without a permit if such action is necessary to:
(1) Aid a sick, injured or orphaned specimen; or
(2) Dispose of a dead specimen; or
(3) Salvage a dead specimen which may be useful for scientific study.
(C) Designated employees or agents of the Service or the Minnesota Department of Natural Resources may take
a gray wolf without a permit in Minnesota, in zones 2, 3, 4, and 5, as delineated in paragraph (d)(l) of this section,
in response to depredations by a gray wolf on lawfully present domestic animals: Provided, that such taking must
occur within one-half mile of the place where such depredation occurred and must be performed in a humane
manner: And provided further, that any young of the year taken on or before August 1 of that year must be
released.
(D) Any taking pursuant to paragraph (d)(2)(i)(A), (d)(2)(i)(B), or (d)(2)(i)(C) of this section must be reported in
writing to the Twin Cities Ecological Service Field Office, 4101 American Boulevard East, Bloomington, Minnesota,
55425, or by facsimile (612) 725-3609 within 5 days. The specimen may only be retained, disposed of, or salvaged
in accordance with directions from the Service.
(E) Any employee or agent of the Service or the Minnesota Department of Natural Resources, when operating
under a Cooperative Agreement with the Service signed in accordance with section 6(c) of the Endangered
Species Act of 1973, who is designated by the Service or the Minnesota Department of Natural Resources for
such purposes, may, when acting in the course of his or her official duties, take a gray wolf in Minnesota to carry
out scientific research or conservation programs.
(ii) Export and commercial transactions. Except as may be authorized by a permit issued under §17.32, no person
may sell or offer for sale in interstate commerce, import or export, or in the course of a commercial activity
transport, ship, carry, deliver, or receive any Minnesota gray wolf.
(iii) Unlawfully taken wolves. No person may possess, sell, deliver, carry, transport, or ship, by any means
whatsoever, a gray wolf taken unlawfully in Minnesota, except that an employee or agent of the Service, or any
other Federal land management agency, or the Minnesota Department of Natural Resources, who is designated
by his/her agency for such purposes, may, when acting in the course of his official duties, possess, deliver, carry,
transport, or ship a gray wolf taken unlawfully in Minnesota.
(3) Permits. All permits available under §17.32 (General Permits—Threatened Wildlife) are available with regard to
the gray wolf in Minnesota. All the terms and provisions of §17.32 apply to such permits issued under the authority
of this paragraph (d)(3).
(e) African elephant (Loxodonta africana). This paragraph (e) applies to any specimen of the species Loxodonta
africana whether live or dead, including any part or product thereof. The African Elephant Conservation Act (16
U.S.C. 4201 et. seq.), and any moratorium under that act, also applies. Except as provided in paragraphs (e)(2)
through (9) of this section, all of the prohibitions and exceptions in §§17.31 and 17.32 apply to the African
elephant. Persons seeking to benefit from the exceptions provided in this paragraph (e) must demonstrate that
they meet the criteria to qualify for the exceptions.
(1) Definitions. In this paragraph (e), antique means any item that meets all four criteria under section 10(h) of the
Endangered Species Act (16 U.S.C. 1539(h)). Ivory means any African elephant tusk and any piece of an African
elephant tusk. Raw ivory means any African elephant tusk, and any piece thereof, the surface of which, polished
or unpolished, is unaltered or minimally carved. Worked ivory means any African elephant tusk, and any piece
thereof, that is not raw ivory.
(2) Live animals and parts and products other than ivory and sport-hunted trophies. Live African elephants and
African elephant parts and products other than ivory and sport-hunted trophies may be imported into or exported
from the United States; sold or offered for sale in interstate or foreign commerce; and delivered, received, carried,
transported, or shipped in interstate or foreign commerce in the course of a commercial activity without a
threatened species permit issued under §17.32, provided the requirements in 50 CFR parts 13, 14, and 23 have
been met.
(3) Interstate and foreign commerce of ivory. Except for antiques and certain manufactured or handcrafted items
containing de minimis quantities of ivory, sale or offer for sale of ivory in interstate or foreign commerce and
delivery, receipt, carrying, transport, or shipment of ivory in interstate or foreign commerce in the course of a
commercial activity is prohibited. Except as provided in paragraphs (e)(5)(iii) and (e)(6) through (8) of this section,
manufactured or handcrafted items containing de minimis quantities of ivory may be sold or offered for sale in
interstate or foreign commerce and delivered, received, carried, transported, or shipped in interstate or foreign
commerce in the course of a commercial activity without a threatened species permit issued under §17.32,
provided they meet all of the following criteria:
(i) If the item is located within the United States, the ivory was imported into the United States prior to January 18,
1990, or was imported into the United States under a Convention on International Trade in Endangered Species of
Wild Fauna and Flora (CITES) pre-Convention certificate with no limitation on its commercial use;
(ii) If the item is located outside the United States, the ivory was removed from the wild prior to February 26, 1976;
(iii) The ivory is a fixed or integral component or components of a larger manufactured or handcrafted item and is
not in its current form the primary source of the value of the item, that is, the ivory does not account for more than
50 percent of the value of the item;
(iv) The ivory is not raw;
(v) The manufactured or handcrafted item is not made wholly or primarily of ivory, that is, the ivory component or
components do not account for more than 50 percent of the item by volume;
(vi) The total weight of the ivory component or components is less than 200 grams; and
(vii) The item was manufactured or handcrafted before July 6, 2016.
(4) Import/export of raw ivory. Except as provided in paragraphs (e)(6) through (9) of this section, raw ivory may
not be imported into or exported from the United States.
(5) Import/export of worked ivory. Except as provided in paragraphs (e)(6) through (9) of this section, worked ivory
may not be imported into or exported from the United States unless it is contained in a musical instrument, or is
part of a traveling exhibition, household move, or inheritance, and meets the following criteria:
(i) Musical instrument. Musical instruments that contain worked ivory may be imported into and exported from the
United States without a threatened species permit issued under §17.32 of this part provided:
(A) The ivory was legally acquired prior to February 26, 1976;
(B) The instrument containing worked ivory is accompanied by a valid CITES musical instrument certificate or
equivalent CITES document;
(C) The instrument is securely marked or uniquely identified so that authorities can verify that the certificate
corresponds to the musical instrument in question; and
(D) The instrument is not sold, traded, or otherwise disposed of while outside the certificate holder's country of
usual residence.
(ii) Traveling exhibition. Worked ivory that is part of a traveling exhibition may be imported into and exported from
the United States without a threatened species permit issued under §17.32 provided:
(A) The ivory was legally acquired prior to February 26, 1976;
(B) The item containing worked ivory is accompanied by a valid CITES traveling exhibition certificate (see the
requirements for traveling exhibition certificates at 50 CFR 23.49) or equivalent CITES document;
(C) The item containing ivory is securely marked or uniquely identified so that authorities can verify that the
certificate corresponds to the item in question; and
(D) The item containing worked ivory is not sold, traded, or otherwise disposed of while outside the certificate
holder's country of usual residence.
(iii) Household move or inheritance. Worked ivory may be imported into or exported from the United States without
a threatened species permit issued under §17.32 for personal use as part of a household move or as part of an
inheritance if the ivory was legally acquired prior to February 26, 1976, and the item is accompanied by a valid
CITES pre-Convention certificate. It is unlawful to sell or offer for sale in interstate or foreign commerce or to
deliver, receive, carry, transport, or ship in interstate or foreign commerce and in the course of a commercial
activity any African elephant ivory imported into the United States as part of a household move or inheritance. The
exception in paragraph (e)(3) of this section regarding manufactured or handcrafted items containing de
minimisquantities of ivory does not apply to items imported or exported under this paragraph (e)(5)(iii) as part of a
household move or inheritance.
(6) Sport-hunted trophies. (i) African elephant sport-hunted trophies may be imported into the United States
provided:
(A) The trophy was legally taken in an African elephant range country that declared an ivory export quota to the
CITES Secretariat for the year in which the trophy animal was killed;
(B) A determination is made that the killing of the trophy animal will enhance the survival of the species and the
trophy is accompanied by a threatened species permit issued under §17.32;
(C) The trophy is legibly marked in accordance with 50 CFR part 23;
(D) The requirements in 50 CFR parts 13, 14, and 23 have been met; and
(E) No more than two African elephant sport-hunted trophies are imported by any hunter in a calendar year.
(ii) It is unlawful to sell or offer for sale in interstate or foreign commerce or to deliver, receive, carry, transport, or
ship in interstate or foreign commerce and in the course of a commercial activity any sport-hunted African elephant
trophy. The exception in paragraph (e)(3) of this section regarding manufactured or handcrafted items
containing de minimis quantities of ivory does not apply to ivory imported or exported under this paragraph (e)(6)
as part of a sport-hunted trophy.
(iii) Except as provided in paragraph (e)(9) of this section, raw ivory that was imported as part of a sport-hunted
trophy may not be exported from the United States. Except as provided in paragraphs (e)(5), (e)(7), (e)(8), and (e)
(9) of this section, worked ivory imported as a sport-hunted trophy may not be exported from the United States.
Parts of a sport-hunted trophy other than ivory may be exported from the United States without a threatened
species permit issued under §17.32, provided the requirements of 50 CFR parts 13, 14, and 23 have been met.
(7) Import/export of ivory for law enforcement purposes. Raw or worked ivory may be imported into and worked
ivory may be exported from the United States by an employee or agent of a Federal, State, or tribal government
agency for law enforcement purposes, without a threatened species permit issued under §17.32, provided the
requirements of 50 CFR parts 13, 14, and 23 have been met. It is unlawful to sell or offer for sale in interstate or
foreign commerce and to deliver, receive, carry, transport, or ship in interstate or foreign commerce and in the
course of a commercial activity any African elephant ivory that was imported into or exported from the United
States for law enforcement purposes. The exception in paragraph (e)(3) of this section regarding manufactured or
handcrafted items containing de minimis quantities of ivory does not apply to ivory imported or exported under this
paragraph (e)(7) for law enforcement purposes.
(8) Import/export of ivory for genuine scientific purposes. (i) Raw or worked ivory may be imported into and worked
ivory may be exported from the United States for genuine scientific purposes that will contribute to the
conservation of the African elephant, provided:
(A) It is accompanied by a threatened species permit issued under §17.32; and
(B) The requirements of 50 CFR parts 13, 14, and 23 have been met.
(ii) It is unlawful to sell or offer for sale in interstate or foreign commerce and to deliver, receive, carry, transport, or
ship in interstate or foreign commerce and in the course of a commercial activity any African elephant ivory that
was imported into or exported from the United States for genuine scientific purposes. The exception in paragraph
(e)(3) of this section regarding manufactured or handcrafted items containing de minimis quantities of ivory does
not apply to ivory imported or exported under this paragraph (e)(8) for genuine scientific purposes.
(9) Antique ivory. Antiques (as defined in paragraph (e)(1) of this section) are not subject to the provisions of this
rule. Antiques containing or consisting of ivory may, therefore, be imported into or exported from the United States
without a threatened species permit issued under §17.32, provided the requirements of 50 CFR parts 13, 14, and
23 have been met. Nevertheless, nothing in this rule interprets or changes any provisions or prohibitions that may
apply under the African Elephant Conservation Act (16 U.S.C. 4201 et seq.), regardless of the age of the item.
Antiques that consist of or contain raw or worked ivory may similarly be sold or offered for sale in interstate or
foreign commerce and delivered, received, carried, transported, or shipped in interstate or foreign commerce in the
course of a commercial activity without a threatened species permit issued under §17.32.
(f) Leopard (Panthera pardus) (1) Except as noted in paragraph (f)(2) of this section, all prohibitions of §17.31 of
this part and exemptions of §17.32 of this part shall apply to the leopard populations occurring in southern Africa to
the south of a line running along the borders of the following countries: Gabon/Rio Muni; Gabon/Cameroon;
Congo/Cameroon; Congo/Central African Republic; Zaire/Central African Republic; Zaire/Sudan; Uganda/Sudan;
Kenya/Sudan; Kenya/Ethiopia; Kenya/Somalia.
(2) A sport-hunted leopard trophy legally taken after the effective date of this rulemaking, from the area south of
the line delineated above, may be imported into the United States without a Threatened Species permit pursuant
to §17.32 of this part, provided that the applicable provisions of 50 CFR part 23 have been met.
(g) Utah prairie dog (Cynomys parvidens).
(1) Except as noted in paragraphs (g)(2) through (g)(6) of this section, all prohibitions of §17.31(a) and (b) and
exemptions of §17.32 apply to the Utah prairie dog.
(2) A Utah prairie dog may be directly or intentionally taken as described in paragraphs (g)(3) and (4) of this
section on agricultural lands, properties within 0.8 kilometers (km) (0.5 miles (mi)) of conservation lands, and areas
where prairie dogs create serious human safety hazards or disturb the sanctity of significant human cultural or
human burial sites.
(3) Agricultural lands and properties near conservation lands. When permitted by the Utah Division of Wildlife
Resources (UDWR), or other parties as authorized in writing by the Service, direct or intentional take is allowed on
private properties that are located within 0.8 km (0.5 mi) of conservation land, and on agricultural land. Records on
permitted take will be maintained by the State (or other parties as authorized in writing by the Service), and made
available to the Service upon request.
(i) Agricultural land. (A) Take may be permitted only on agricultural land being physically or economically affected
by Utah prairie dogs, and only when the spring count on the agricultural lands is seven or more individuals, and
only during the period of June 15 to December 31; and
(B) The land must:
(1) Meet the general classification of irrigated, dryland, grazing land, orchard, or meadow;
(2) Be capable of producing crops or forage;
(3) Be at least 2 contiguous hectares (5 contiguous acres) in area (smaller parcels may qualify where devoted to
agricultural use in conjunction with other eligible acreage under identical legal ownership);
(4) Be managed in such a way that there is a reasonable expectation of profit;
(5) Have been devoted to agricultural use for at least 2 successive years immediately preceding the year in which
application is made; and
(6) Meet State average annual (per-acre) production requirements.
(ii) Private property near conservation land. (A) Take may be permitted on private properties within 0.8 km (0.5 mi)
of Utah prairie dog conservation land during the period of June 15 to December 31.
(B) Conservation lands are defined as non-Federal areas set aside for the preservation of Utah prairie dogs and
are managed specifically or primarily toward that purpose. Conservation lands may include, but are not limited to,
properties set aside as conservation banks, fee-title purchased properties, properties under conservation
easements, and properties subject to a safe harbor agreement (see §17.22). Conservation lands do not include
Federal lands.
(iii) Amount of permitted take on agricultural lands and private property near conservation land. (A) The UDWR, or
other parties as authorized in writing by the Service, will ensure that permitted take on agricultural lands and
properties within 0.8 km (0.5 mi) of conservation lands does not exceed 10 percent of the estimated rangewide
population annually.
(B) On agricultural lands, the UDWR, or other parties as authorized in writing by the Service, will limit permitted
take to 7 percent of the estimated annual rangewide population and will limit within-colony take to one-half of a
colony's estimated annual production. The UDWR, or other parties as authorized in writing by the Service, will
spatially distribute the 7 percent allowed take on agricultural lands across the three Recovery Units, based on the
distribution of the total annual population estimate within each Recovery Unit.
(C) In setting take limits on properties within 0.8 km (0.5 mi) of conservation lands, the UDWR, or other parties as
authorized in writing by the Service, will consider the amount of take that occurs on agricultural lands. The State,
or other parties as authorized in writing by the Service, will restrict the remaining permitted take (the amount that
would bring the total take up to 10 percent of the estimated annual rangewide population) on properties within 0.8
km (0.5 mi) of conservation lands to animals in excess of the baseline population. The baseline population of these
lands is determined in accordance with paragraph (g)(3)(iii)(D) of this section.
(D) Take on properties within 0.8 km (0.5 mi) of conservation lands is restricted to prairie dogs in excess of the
baseline population. The baseline population is the highest estimated total (summer) population size on that
property during the 5 years prior to the establishment of the conservation property, except that if no UDWR
surveys to determine population size on a property were conducted during such 5-year period, the baseline
population is the estimated total (summer) population size on that property as determined in the first survey
conducted after the establishment of the conservation property. The baseline population will be established by the
UDWR, or other parties as authorized in writing by the Service.
(E) Translocated Utah prairie dogs will count toward the take limits in paragraphs (g)(3)(iii)(A) through (D) of this
section.
(iv) Methods of allowed direct take on agricultural lands and private properties near conservation land. Methods for
controlling Utah prairie dogs on agricultural lands and properties within 0.8 km (0.5 mi) of conservation lands are
limited to activities associated with translocation efforts by trained and permitted individuals complying with current
Service-approved guidance, trapping intended for lethal removal, and shooting. Actions intended to drown or
poison Utah prairie dogs and the use of gas cartridges, anticoagulants, and explosive devices are prohibited.
(4) Human safety hazards and significant human cultural or human burial sites. (i) Nonlethal take is allowed where
Utah prairie dogs create serious human safety hazards or disturb the sanctity of significant human cultural or
human burial sites, if approved in writing by the Service. To reduce hazards, prairie dog burrows may be filled with
dirt if they are directly creating human hazards or disturbing the sanctity of significant human cultural or human
burial sites. Utah prairie dogs also may be translocated from these sites to approved translocation sites by
properly trained personnel using Service-approved translocation protocols.
(ii) Direct or intentional lethal take is allowed where Utah prairie dogs create serious human safety hazards or
disturb the sanctity of significant human cultural or human burial sites, but only after all practicable measures to
resolve the conflict are implemented, and only as approved in writing by the Service. A permit is not required to
allow take under these conditions.
(A) All practicable measures means, with respect to these situations:
(1) Construction of prairie-dog-proof fence, above and below grade to specifications approved by the Service,
around the area in which there is concern.
(2) Translocation of Utah prairie dogs out of the fenced area in which there is a concern must be conducted prior to
allowing lethal take. Lethal take is allowed only to remove prairie dogs that remain in these areas after the
measures to fence and translocate are successfully carried out.
(3) Continued maintenance or modification of the fence as needed to preclude Utah prairie dogs from entering the
fenced sites.
(B) There are no restrictions on the amount, timing, or methods of lethal take allowed on lands where Utah prairie
dogs create serious human safety hazards or disturb the sanctity of significant human cultural or human burial
sites, as long as all qualifications in paragraphs (g)(4)(ii)(A)(1)through (3) of this section are met.
(C) The amount of take in areas where Utah prairie dogs create serious human safety hazards or disturb the
sanctity of significant human cultural or human burial sites does not contribute to the upper permitted take limits
described above for agricultural lands and private properties within 0.8 km (0.5 mi) of conservation lands.
(5) Incidental take associated with agriculture. Utah prairie dogs may be taken when take is incidental to
otherwise-legal activities associated with legal and standard agricultural practices on legitimately operating
agricultural lands. Acceptable practices include plowing to depths that do not exceed 46 cm (18 in.), discing,
harrowing, irrigating crops, mowing, harvesting, and bailing, as long as the activities are not intended to eradicate
Utah prairie dogs. There is no numeric limit established for incidental take associated with standard agricultural
practices. Incidental take is in addition to, and does not contribute to, the take limits described in paragraphs (g)(2)
through (4) of this section. A permit is not required for incidental take associated with agricultural practices.
(6) If the Service receives evidence that take pursuant to paragraphs (g)(2) through (5) of this section is having an
effect that is inconsistent with the conservation of the Utah prairie dog, the Service may immediately prohibit or
restrict such take as appropriate for the conservation of the species. The Service will notify the permitting entities
in writing if take restrictions are necessary.
(h) Mountain lion (Felis concolor). (1) Except as allowed in paragraphs (h)(2), (h)(3), and (h)(4) of this section, no
person shall take any free-living mountain lion (Felis concolor) in Florida.
(2) A mountain lion (Felis concolor) may be taken in this area under a valid threatened species permit issued
pursuant to 50 CFR 17.52.
(3) A mountain lion (Felis concolor) may be taken in Florida by an employee or designated agent of the Service or
the Florida Game and Fresh Water Fish Commission for taxonomic identification or other reasons consistent with
the conservation of the endangered Florida panther (Felis concolor coryi). When it has been established by the
Service, in consultation with the State, that an animal in question is not a Florida panther (Felis concolor coryi) or
an eastern cougar (Felis concolor couguar), such animals may be removed from the wild. The disposition of
animals so taken shall be at the discretion of the Florida Game and Fresh Water Fish Commission, with the
concurrence of the Fish and Wildlife Service.
(4) Take for reasons of human safety is allowed as specified under 50 CFR 17.21(c)(2) and 17.21(c)(3)(iv).
(5) Any take pursuant to paragraph (h)(4) of this section must be reported in writing to the U.S. Fish and Wildlife
Service, Office of Law Enforcement, 4401 N. Fairfax Drive, LE-3000, Arlington, VA 22203, within 5 days. The
specimen may only be retained, disposed of, or salvaged in accordance with directions from the Service.
(i) Columbian white-tailed deer (Odocoileus virginianus leucurus) (CWTD), the Columbia River distinct population
segment. (1) General requirements. Other than as expressly provided at paragraph (i)(3) of this section, the
provisions of §17.31(a) apply to the CWTD.
(2) Definitions. For the purposes of this entry:
(i) CWTD means the Columbia River distinct population segment (DPS) of Columbian white-tailed deer or
individual specimens of CWTD.
(ii) Intentional harassment means an intentional act which creates the likelihood of injury to wildlife by annoying it
to such an extent as to significantly disrupt normal behavior patterns which include, but are not limited to,
breeding, feeding, or sheltering. Intentional harassment may include prior purposeful actions to attract, track, wait
for, or search out CWTD, or purposeful actions to deter CWTD.
(iii) Problem CWTD means an individual specimen of CWTD that has been identified in writing by a State
conservation agency or the Service as meeting the following criteria:
(A) The CWTD is causing more than de minimus negative economic impact to a commercial crop;
(B) Previous efforts to alleviate the damage through nonlethal methods have been ineffective; and
(C) There is a reasonable certainty that additional property losses will occur in the near future if a lethal control
action is not implemented.
(iv) Commercial crop means commercially raised horticultural, agricultural, or forest products.
(v) State conservation agency means the State agency in Oregon or Washington operating a conservation
program for CWTD pursuant to the terms of a cooperative agreement with the Service in accordance with section
6(c) of the Endangered Species Act.
(3) Allowable forms of take of CWTD. Take of CWTD resulting from the following legally conducted activities is
allowed:
(i) Intentional harassment not likely to cause mortality. A State conservation agency may issue permits to
landowners or their agents to harass CWTD on lands they own, rent, or lease if the State conservation agency
determines in writing that such action is not likely to cause mortality of CWTD. The techniques employed in this
harassment must occur only as specifically directed or restricted by the State permit in order to avoid causing
CWTD mortality.
(ii) Take of problem CWTD resulting in mortality. Take of problem CWTD is authorized under the following
circumstances:
(A) Any employee or agent of the Service or the State conservation agency, who is designated by their agency for
such purposes, may, when acting in the course of their official duties, take problem CWTD. This take must occur in
compliance with all other applicable Federal, State, and local laws and regulations.
(B) The State conservation agency may issue a permit to landowners or their agents to take problem CWTD on
lands they own, rent, or lease. Such take must be implemented only as directed and allowed in the permit obtained
from the State conservation agency.
(iii) Accidental take of CWTD when carrying out State-permitted black-tailed deer damage control. Take of CWTD
in the course of carrying out black-tailed deer damage control will be a violation of this rule unless the taking was
accidental; reasonable care was practiced to avoid such taking; and the person causing the take was in
possession of a valid black-tailed deer damage control permit from a State conservation agency. When issuing
black-tailed deer damage control permits, the State conservation agency will provide education regarding
identification of target species. The exercise of reasonable care includes, but is not limited to, the review of the
educational material provided by the State conservation agency and identification of the target before shooting.
(iv) Accidental take of CWTD when carrying out State-permitted black-tailed deer hunting. Take of CWTD in the
course of hunting black-tailed deer will be a violation of this rule unless the take was accidental; the take was in
the course of hunting black-tailed deer under a lawful State permit; and reasonable due care was exercised to
avoid such taking. The State conservation agency will provide educational material to hunters regarding
identification of target species when issuing hunting permits. The exercise of reasonable care includes, but is not
limited to, the review of the educational materials provided by the State conservation agency and identification of
the target before shooting.
(4) Take limits. The amount of take of CWTD allowed for the activities in paragraphs (i)(3)(ii), (iii), and (iv) of this
section will not exceed 5 percent of the CWTD population during any calendar year, as determined by the Service.
By December 31 of each year, the Service will use the most current annual DPS population estimate to set the
maximum allowable take for these activities for the following calendar year. If take exceeds 2 percent of the DPS
population in a given calendar year, the Service will convene a meeting with the Oregon Department of Fish and
Wildlife and the Washington Department of Fish and Wildlife to discuss CWTD management and strategies to
minimize further take from these activities for the rest of the year. If take exceeds 5 percent of the CWTD
population in any given calendar year, no further take under paragraphs (i)(3)(ii), (iii), and (iv) will be allowed
during that year and any further take that does occur may be subject to prosecution under the Endangered
Species Act.
(5) Reporting and disposal requirements. Any injury or mortality of CWTD associated with the actions authorized
under paragraphs (i)(3), (6), and (7) of this section must be reported to the Service within 72 hours, and specimens
may be disposed of only in accordance with directions from the Service. Reports should be made to the Service's
Law Enforcement Office at (503) 231-6125, or the Service's Oregon Fish and Wildlife Office at (503) 231-6179.
The Service may allow additional reasonable time for reporting if access to these offices is limited due to closure.
(6) Additional taking authorizations for Tribal employees, State and local law enforcement officers, and Statelicensed wildlife rehabilitation facilities. (i) Tribal employees and State and local government law enforcement
officers. When acting in the course of their official duties, both Tribal employees designated by the Tribe for such
purposes, and State and local government law enforcement officers working in the States of Oregon or
Washington, may take CWTD for the following purposes:
(A) Aiding or euthanizing sick, injured, or orphaned CWTD;
(B) Disposing of a dead specimen; and
(C) Salvaging a dead specimen that may be used for scientific study.
(ii) Such take must be reported to the Service within 72 hours, and specimens may be disposed of only in
accordance with directions from the Service.
(7) Wildlife rehabilitation facilities licensed by the States of Oregon or Washington. When acting in the course of
their official duties, a State-licensed wildlife rehabilitation facility may take CWTD for the purpose of aiding or
euthanizing sick, injured, or orphaned CWTD. Such take must be reported to the Service within 72 hours as
required by paragraph (i)(5) of this section, and specimens may be retained and disposed of only in accordance
with directions from the Service.
(8) Take authorized by permits. Any person with a valid permit issued by the Service under §17.32 may take
CWTD, pursuant to the special terms and conditions of the permit.
(j) Argali (Ovis ammon) in Kyrgyzstan, Mongolia, and Tajikistan. (1) Except as noted in paragraph (j)(2) of this
section, all prohibitions of §17.31 of this part and exemptions of §17.32 of this part shall apply to this species in
Kyrgyzstan, Mongolia, and Tajikistan
(Note. In all other parts of its range the argali is classified as endangered and covered by §17.21).
(2) Upon receiving from the governments of Kyrgyzstan, Mongolia, and Tajikistan properly documented and
verifiable certification that (i) argali populations in those countries are sufficiently large to sustain sport hunting, (ii)
regulating authorities have the capacity to obtain sound data on these populations, (iii) regulating authorities
recognize these populations as a valuable resource and have the legal and practical capacity to manage them as
such, (iv) the habitat of these populations is secure, (v) regulating authorities can ensure that the involved trophies
have in fact been legally taken from the specified populations, and (vi) funds derived from the involved sport
hunting are applied primarily to argali conservation, the Director may, consistent with the purposes of the Act,
authorize by publication of a notice in the Federal Register the importation of personal sport-hunted argali trophies,
taken legally in Kyrgyzstan, Mongolia, and Tajikistan after the date of such notice, without a Threatened Species
permit pursuant to §17.32 of this part, provided that the applicable provisions of 50 CFR part 23 have been met.
(k) Canada lynx (Lynx canadensis). (1) What lynx does this special rule apply to? The regulations in this paragraph
(k) apply to all wild and captive lynx in the contiguous United States.
(2) What activities are prohibited for wild lynx? All prohibitions and provisions of 50 CFR 17.31 and 17.32 apply to
wild lynx found in the contiguous United States.
(3) What is considered a captive lynx? (i) For purposes of this paragraph (k), captive lynx means lynx, whether
alive or dead, and any part or product, if the specimen was in captivity at the time of the listing, born in captivity, or
lawfully imported or transported into the contiguous United States.
(ii) Lynx that were either born or held in captivity and then released into the wild are considered wild.
(4) What activities are allowed for captive lynx? (i) Take. You may take lawfully obtained captive lynx without a
permit.
(ii) Import and export. You may export captive live lynx, parts or products of captive lynx provided the specimens
are tagged with Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) export
tags and/or accompanied by a valid CITES export permit. You may import lawfully obtained lynx that originated
outside the United States when you follow the requirements of CITES.
(iii) Interstate commerce. You may deliver, receive, carry, transport, ship, sell, offer to sell, purchase, or offer to
purchase in interstate commerce captive lynx and captive lynx parts and products in accordance with State or
tribal laws and regulations. In addition, lynx pelts that are properly tagged with valid CITES export tags also qualify
for this exemption on interstate commerce.
(5) Are any activities not allowed or restricted for captive lynx? You must comply with all applicable State and tribal
laws and regulations. Violation of State or tribal law will also be a violation of the Act.
(l) Preble's meadow jumping mouse (Zapus hudsonius preblei). (1) What is the definition of take? To harass, harm,
pursue, hunt, shoot, wound, trap, kill, or collect; or attempt to engage in any such conduct. Incidental take is that
which occurs when it is incidental to and not the purpose of an otherwise lawful activity. Any take that is not
authorized by permit provided through section 7 or section 10 of the Act or that is not covered by the exemptions
described below is considered illegal take.
(2) When is take of Preble's meadow jumping mice allowed? Take of Preble's meadow jumping mice resulting from
the following legally conducted activities, in certain circumstances as described below, is allowed:
(i) Take under permits. Any person with a valid permit issued by the Service under §17.32 may take Preble's
meadow jumping mice pursuant to the terms of the permit.
(ii) Rodent control. Preble's meadow jumping mice may be taken incidental to rodent control undertaken within 10
feet of or inside any structure. “Rodent control” includes control of mice and rats by trapping, capturing, or
otherwise physically capturing or killing, or poisoning by any substance registered with the Environmental
Protection Agency as required by the Federal Insecticide, Fungicide, and Rodenticide Act (7 U.S.C. 136) and
applied consistent with its labeling. “Structure” includes but is not limited to any building, stable, grain silo, corral,
barn, shed, water or sewage treatment equipment or facility, enclosed parking structure, shelter, gazebo,
bandshell, or restroom complex.
(iii) Established, ongoing agricultural activities. Preble's meadow jumping mice may be taken incidental to
agricultural activities, including grazing, plowing, seeding, cultivating, minor drainage, burning, mowing, and
harvesting, as long as these activities are established, ongoing activities and do not increase impacts to or further
encroach upon the Preble's meadow jumping mouse or its habitat. New agricultural activities or those that expand
the footprint or intensity of the activity are not considered to be established, ongoing activities.
(iv) Maintenance and replacement of existing landscaping. Preble's meadow jumping mice may be taken incidental
to the maintenance and replacement of any landscaping and related structures and improvements, as long as they
are currently in place and no increase in impervious surfaces would result from their maintenance and
improvement. Construction of new structures or improvements or expansion of the landscaping in a manner that
increases impervious surfaces would not be considered maintenance and replacement of existing landscaping.
(v) Existing uses of water. Preble's meadow jumping mice may be taken incidentally as a result of existing uses of
water associated with the exercise of perfected water rights pursuant to State law and interstate compacts and
decrees. (A “perfected water right” is a right that has been put to beneficial use and has been permitted, decreed,
or adjudicated pursuant to State law.) Increasing the use or altering the location of use of an existing water right
would not be considered an existing use of water.
(vi) Noxious weed control. Preble's meadow jumping mice may be taken incidental to noxious weed control that is
conducted in accordance with:
(A) Federal law, including Environmental Protection Agency label restrictions;
(B) Applicable State laws for noxious weed control;
(C) Applicable county bulletins;
(D) Herbicide application guidelines as prescribed by herbicide manufacturers; and
(E) Any future revisions to the authorities listed in paragraphs (l)(2)(vi)(A) through (D) of this section that apply to
the herbicides proposed for use within the species' range.
(vii) Ditch maintenance activities. Preble's meadow jumping mice may be taken incidental to normal and customary
ditch maintenance activities only if the activities:
(A) Result in the annual loss of no more than 1⁄4 mile of riparian shrub habitat per linear mile of ditch, including
burning of ditches that results in the annual loss of no more than 1⁄4 mile of riparian shrub habitat per linear mile of
ditch.
(B) Are performed within the historic footprint of the surface disturbance associated with ditches and related
infrastructure, and
(C) Follow the Best Management Practices described in paragraphs (l)(2)(vii)(C)(1) through (3) of this section.
(1) Persons engaged in ditch maintenance activities shall avoid, to the maximum extent practicable, impacts to
shrub vegetation. For example, if accessing the ditch for maintenance or repair activities from an area containing
no shrubs is possible, then damage to adjacent shrub vegetation shall be avoided.
(2) Persons engaged in placement or sidecasting of silt and debris removed during ditch cleaning, vegetation or
mulch from mowing or cutting, and other material from ditch maintenance shall, to the maximum extent
practicable, avoid shrub habitat and at no time disturb more than 1⁄4 mile of riparian shrub habitat per linear mile of
ditch within any calendar year.
(3) To the maximum extent practicable, all ditch maintenance activities should be carried out during the Preble's
hibernation season, November through April.
(D) All ditch maintenance activities carried out during the Preble's active season, May through October, should be
conducted during daylight hours only.
(E) Ditch maintenance activities that would result in permanent or long-term loss of potential habitat that would not
be considered normal or customary include replacement of existing infrastructure with components of substantially
different materials and design, such as replacement of open ditches with pipeline or concrete-lined ditches,
replacement of an existing gravel access road with a permanently paved road, or replacement of an earthen
diversion structure with a rip-rap and concrete structure, and construction of new infrastructure or the movement of
existing infrastructure to new locations, such as realignment of a ditch, building a new access road, or installation
of new diversion works where none previously existed.
(3) When is take of Preble's not allowed? (i) Any manner of take not described under paragraph (l)(2) of this
section.
(ii) No person may import or export, ship in interstate commerce in the course of commercial activity, or sell or offer
for sale in interstate or foreign commerce any Preble's meadow jumping mice.
(iii) No person, except for an authorized person, may possess, sell, deliver, carry, transport, or ship any Preble's
meadow jumping mice that have been taken illegally.
(4) Where does this rule apply? The take exemptions provided by this rule are applicable within the entire range of
the Preble's meadow jumping mouse.
(m) Vicuña (Vicugna vicugna)— (1) What activities involving vicuña are prohibited by this rule? (i) Appendix I
populations. All provisions of §17.31 (a) and (b) and §17.32 apply to vicuña and vicuña parts and products
originating from populations currently listed in Appendix I of the Convention on International Trade in Endangered
Species of Wild Fauna and Flora (CITES).
(ii) Import, export, and re-export. Except as provided in paragraph (m)(2) of this section, it is unlawful to import,
export, or re-export, or present for export or re-export without valid permits as required under parts 17 and 23 of
this subchapter, any vicuña or vicuña parts and products. For import of embryos, blood, other tissue samples, or
live vicuña, permits required under §17.32 and part 23 will be issued only for bona fide scientific research
contributing to the conservation of the species in the wild.
(iii) Other activities. Except as provided in paragraph (m)(2) of this section, it is unlawful to sell or offer for sale,
deliver, receive, carry, transport, or ship in interstate or foreign commerce and in the course of a commercial
activity any vicuña or vicuña parts and products.
(iv) It is unlawful for any person subject to the jurisdiction of the United States to commit, attempt to commit, solicit
to commit, or cause to be committed any acts described in paragraphs (m)(1)(ii)-(iii) of this section.
(2) What activities involving vicuña are allowed by this rule? You may import, export, or re-export, or conduct
interstate or foreign commerce in raw wool sheared from live vicuñas, cloth made from such wool, or
manufactured or handicraft products and articles made from or consisting of such wool or cloth without a
threatened species permit issued according to §17.32 only when the following provisions have been met:
(i) The specimens originated from a population listed in CITES Appendix II.
(ii) The provisions in parts 13, 14, and 23 of this subchapter are met, including the specific labeling provisions in
part 23.
(iii) Personal and household effects. Under the provisions of this special rule, raw wool sheared from live vicuñas,
cloth made from such wool, or manufactured or handicraft products and articles made from or consisting of such
wool or cloth are not granted the personal or household effects exemption described in part 23 of this subchapter.
In addition to the provisions of this paragraph (m)(2), such specimens may only be imported, exported, or reexported when accompanied by a valid CITES document.
(iv) Labeling of wool sheared from live vicuñas. Any shipment of raw wool sheared from live vicuñas must be
sealed with a tamper-proof seal and have the following:
(A) An identification tag with a code identifying the country of origin of the raw vicuña wool and the CITES export
permit number; and
(B) The vicuña logotype as defined in 50 CFR part 23 and the words “VICUÑA—COUNTRY OF ORIGIN”, where
country of origin is the name of the country from which the raw vicuña wool was first exported.
(v) At the time of import, the country of origin and each country of re-export involved in the trade of a particular
shipment have not been identified by the CITES Conference of the Parties, the CITES Standing Committee, or in a
Notification from the CITES Secretariat as a country from which Parties should not accept permits.
(3) When and how will the Service inform the public of additional restrictions in trade of vicuña? Except in rare
cases involving extenuating circumstances that do not adversely affect the conservation of the species, we will
issue a public bulletin that identifies a restriction on trade in specimens of vicuña addressed in this paragraph (m) if
any of the following criteria are met:
(i) The country is identified in any action adopted by the Conference of the Parties to the Convention, the
Convention's Standing Committee, or in a Notification issued by the CITES Secretariat, whereby Parties are asked
not to accept shipments of specimens of any CITES-listed species from the country in question.
(ii) The Service's Division of Scientific Authority administratively determines that the conservation or management
status of threatened vicuña populations in a range country has changed, such that continued recovery of the
vicuña population in that country may be compromised, as a result of one or more of the following factors:
(A) A change in range country laws or regulations that lessens protection for vicuña;
(B) A change in range country management programs that lessens protection for vicuña;
(C) A documented decline in wild vicuña population numbers;
(D) A documented increase in poaching of vicuña;
(E) A documented decline in vicuña habitat quality or quantity; or
(F) Other natural or man-made factors affecting the species' recovery.
(4) What must vicuña range countries do in order to be authorized under the special rule to export to the United
States?—(i) Annual Report. Range country governments (Argentina, Bolivia, Chile, and Peru) wishing to export
specimens of vicuña to the United States will need to provide an annual report containing the most recent
information available on the status of the species, following the information guidelines specified below. The first
submission of a status report will be required as of July 1, 2003, and every year thereafter on the anniversary of
that date. For each range country, the following information should be provided in the annual report:
(A) A description of any revisions to the management program, especially any changes in management
approaches or emphasis;
(B) New information obtained in the last year on vicuña distribution, population status, or population trends, for the
country as a whole or for specific protected areas, and a detailed description of the methodology used to obtain
such information;
(C) Results of any research projects concluded in the last year on the biology of vicuña in the wild, particularly its
population biology, habitat use, and genetics, and a description of any new research projects undertaken on the
biology of vicuña in the wild, particularly its population biology, habitat use, and genetics;
(D) A description of any changes to national and/or provincial laws and programs relating to vicuña conservation,
in particular those laws and regulations related to harvest and use of the vicuña, and export of vicuña parts and
products;
(E) A description of any changes in the number or size of natural reserves or national parks that provide protected
habitat for the vicuña;
(F) A summary of law enforcement activities undertaken in the last year, and a description of any changes in
programs to prevent poaching, smuggling, and illegal commercialization of the vicuña;
(G) A description of the current management and harvest (or “sustainable use”) programs for wild populations of
the vicuña, including: any changes in the location and population size of wild populations being managed for
sustainable use; any changes in the harvest management practices being used for each population; any changes
in current harvest quotas for wild populations, if any; any changes in protocols for translocations undertaken as
part of the use program; a summary of the specific financial costs of and revenues generated by the sustainable
use program over the last year; and a summary of documented conservation benefits resulting from the
sustainable use program over the last year;
(H) A description of current management and harvest (or “sustainable use”) programs for captive and so-called
“semi-captive” populations of the vicuña, including: any changes in the number and location of all captive and
“semi-captive” populations; any changes in the size (ha) of each captive enclosure and the number of vicuña
maintained therein; any changes in protocols for translocations undertaken as part of the use program; a summary
of the financial costs of and revenues generated by the sustainable use program over the last year; and
documented conservation benefits resulting from the sustainable use program over the last year (information on
captive and “semi-captive” populations must be separate from that provided for wild populations); and
(I) Export data for the last year.
(ii) The Service's Division of Scientific Authority will conduct a review every 2 years, using information in the annual
reports, to determine whether range country management programs are effectively achieving conservation
benefits for the vicuña. Failure to submit an annual report could result in a restriction on trade in specimens of
vicuña as addressed in paragraph (m)(3) of this section. Based on information contained in the annual reports and
any other pertinent information it has available, the Service may restrict trade from a range country, as addressed
in paragraph (m)(3) of this section, if it determines that the conservation or management status of threatened
vicuña populations in a range country has changed, such that continued recovery of the vicuña population in that
country may be compromised. Trade restrictions may result from one or more of the following factors:
(A) A change in range country laws or regulations that lessens protection for vicuña;
(B) A change in range country management programs that lessens protection for vicuña;
(C) A documented decline in wild vicuña population numbers;
(D) A documented increase in poaching of vicuña;
(E) A documented decline in vicuña habitat quality or quantity; or
(F) Other natural or man-made factors affecting the species' recovery.
(n) Straight-horned markhor (Capra falconeri megaceros).
(1) General requirements. Except as noted in paragraph (n)(2) of this section, all prohibitions of §17.31 and
exemptions of §17.32 apply to this subspecies.
(2) What are the criteria under which a personal sport-hunted trophy may qualify for import without a permit under
§17.32? The Director may, consistent with the purposes of the Act, authorize by publication of a notice in
the Federal Register the importation, without a threatened species permit issued under §17.32, of personal sporthunted straight-horned markhor from an established conservation program that meets the following criteria:
(i) The markhor was taken legally from the established program after the date of the Federal Register notice;
(ii) The applicable provisions of 50 CFR parts 13, 14, 17, and 23 have been met; and
(iii) The Director has received the following information regarding the established conservation program for
straight-horned markhor:
(A) Populations of straight-horned markhor within the conservation program's areas can be shown to be sufficiently
large to sustain sport hunting and are stable or increasing.
(B) Regulatory authorities have the capacity to obtain sound data on populations.
(C) The conservation program can demonstrate a benefit to both the communities surrounding or within the area
managed by the conservation program and the species, and the funds derived from sport hunting are applied
toward benefits to the community and the species.
(D) Regulatory authorities have the legal and practical capacity to provide for the long-term survival of the
populations.
(E) Regulatory authorities can determine that the sport-hunted trophies have in fact been legally taken from the
populations under an established conservation program.
(o) Northern long-eared bat (Myotis septentrionalis). The provisions of this rule are based upon the occurrence of
white-nose syndrome (WNS), a disease affecting many U.S. bat populations. The term “WNS zone” identifies the
set of counties within the range of the northern long-eared bat within 150 miles of the boundaries of U.S. counties
or Canadian districts where the fungus Pseudogymnoascus destructans (Pd) or WNS has been detected. For
current information regarding the WNS zone, contact your local Service ecological services field office. Field office
contact information may be obtained from the Service regional offices, the addresses of which are listed in 50 CFR
2.2.
(1) Prohibitions. The following prohibitions apply to the northern long-eared bat:
(i) Purposeful take of northern long-eared bat, including capture, handling, or other activities.
(ii) Within the WNS zone:
(A) Actions that result in the incidental take of northern long-eared bats in known hibernacula.
(B) Actions that result in the incidental take of northern long-eared bats by altering a known hibernaculum's
entrance or interior environment if it impairs an essential behavioral pattern, including sheltering northern longeared bats.
(C) Tree-removal activities that result in the incidental take of northern long-eared bats when the activity:
(1) Occurs within 0.25 mile (0.4 kilometer) of a known hibernaculum; or
(2) Cuts or destroys known occupied maternity roost trees, or any other trees within a 150-foot (45-meter) radius
from the maternity roost tree, during the pup season (June 1 through July 31).
(iii) Possession and other acts with unlawfully taken northern long-eared bats. It is unlawful to possess, sell,
deliver, carry, transport, or ship, by any means whatsoever, any northern long-eared bat that was taken in violation
of this section or State laws.
(iv) Import and export.
(2) Exceptions from prohibitions. (i) Any person may take a northern long-eared bat in defense of his own life or
the lives of others, including for public health monitoring purposes.
(ii) Any person may take a northern long-eared bat that results from the removal of hazardous trees for the
protection of human life and property.
(iii) Any person may take a northern long-eared bat by removing it from human structures, but only if the actions
comply with all applicable State regulations.
(iv) Purposeful take that results from actions relating to capture, handling, and related activities for northern longeared bats by individuals permitted to conduct these same activities for other species of bat until May 3, 2016.
(v) All of the provisions of §17.32 apply to the northern long-eared bat.
(vi) Any employee or agent of the Service, of the National Marine Fisheries Service, or of a State conservation
agency that is operating a conservation program pursuant to the terms of a cooperative agreement with the
Service in accordance with section 6(c) of the Act, who is designated by his agency for such purposes, may, when
acting in the course of his official duties, take northern long-eared bats covered by an approved cooperative
agreement to carry out conservation programs.
(p) Northern sea otter (Enhydra lutris kenyoni). (1) To what population of sea otter does this special rule
apply? The regulations in paragraph (p) of this section apply to the southwest Alaska distinct population segment
(DPS) of the northern sea otter as set forth at §17.11(h) of this part.
(2) What provisions apply to this DPS? Except as noted in paragraph (p)(3) of this section, all prohibitions and
provisions of §§17.31 and 17.32 of this part apply to the southwest Alaska DPS of the northern sea otter.
(3) What additional activities are allowed for this DPS? In addition to the activities authorized under paragraph (p)
(2) of this section, you may conduct any activity authorized or exempted under the Marine Mammal Protection Act
(16 U.S.C. 1361 et seq.) with a part or product of a southwest Alaska DPS northern sea otter, provided that:
(i) The product qualifies as an authentic native article of handicrafts or clothing as defined in §17.3 of this part; and
(A) It was created by an Indian, Aleut, or Eskimo who is an Alaskan
Native, and
(B) It is not being exported or imported for commercial purposes; or
(ii) The part or product is owned by an Indian, Aleut, or Eskimo who is an Alaskan Native and resides in Alaska, or
by a Native inhabitant of Russia, Canada, or Greenland, and is part of a cultural exchange; or
(iii) The product is owned by a Native inhabitant of Russia, Canada, or Greenland, and is in conjunction with travel
for noncommercial purposes; or
(iv) The part or product has been received or acquired by a person registered as an agent or tannery under §18.23
of this subchapter.
(4) What other wildlife regulations may apply? All applicable provisions of 50 CFR parts 14, 18, and 23 must be
met.
(q) Polar bear (Ursus maritimus).
(1) Except as noted in paragraphs (q)(2) and (4) of this section, all prohibitions and provisions of §§17.31 and
17.32 of this part apply to the polar bear.
(2) None of the prohibitions in §17.31 of this part apply to any activity that is authorized or exempted under the
Marine Mammal Protection Act (MMPA) (16 U.S.C. 1361 et seq.), the Convention on International Trade in
Endangered Species of Wild Fauna and Flora (CITES) (27 U.S.T. 1087), or both, provided that the person carrying
out the activity has complied with all terms and conditions that apply to that activity under the provisions of the
MMPA and CITES and their implementing regulations.
(3) All applicable provisions of 50 CFR parts 14, 18, and 23 must be met.
(4) None of the prohibitions in §17.31of this part apply to any taking of polar bears that is incidental to, but not the
purpose of, carrying out an otherwise lawful activity within the United States, except for any incidental taking
caused by activities in areas subject to the jurisdiction or sovereign rights of the United States within the current
range of the polar bear.
(r) Lion (Panthera leo melanochaita).
(1) General requirements. All prohibitions and provisions of §§17.31 and 17.32 apply to this subspecies.
(2) The import exemption found in §17.8 for threatened wildlife listed in Appendix II of the Convention on
International Trade in Endangered Species of Wild Fauna and Flora (CITES) does not apply to this subspecies. A
threatened species import permit under §17.32 is required for the importation of all specimens of Panthera leo
melanochaita.
(3) All applicable provisions of 50 CFR parts 13, 14, 17, and 23 must be met.
[40 FR 44415, Sept. 26, 1975]
Editorial Note: For Federal Register citations affecting §17.40, see the List of CFR Sections Affected, which
appears in the Finding Aids section of the printed volume and at www.govinfo.gov.
return arrow Back to Top
§17.41 Special rules—birds.
(a) Streaked horned lark (Eremophila alpestris strigata). (1) Which populations of the streaked horned lark are
covered by this special rule? The components of this special rule that apply to airport management and noxious
weed control cover the rangewide distribution of this bird; the agricultural component applies only to the Willamette
Valley in Oregon.
(2) What activities are prohibited? Except as noted in paragraphs (a)(3), (4), and (5) of this section, all prohibitions
of §17.31 apply to the streaked horned lark.
(3) What activities are allowed on airports on non-Federal lands? (i) Incidental take of the streaked horned lark will
not be a violation of section 9 of the Act, if the incidental take results from routine management activities
associated with airport operations to minimize hazardous wildlife, consistent with regulations at 14 CFR 139.337.
(ii) Hazardous wildlife is defined by the Federal Aviation Administration as species of wildlife, including feral
animals and domesticated animals not under control, that are associated with aircraft strike problems, are capable
of causing structural damage to airport facilities, or act as attractants to other wildlife that pose a strike hazard.
Routine management activities include, but are not limited to, the following:
(A) Routine management, repair, and maintenance of roads and runways (does not include upgrades or
construction of new roads or runways);
(B) Control and management of vegetation (grass, weeds, shrubs, and trees) through mowing, discing, herbicide
application, or burning;
(C) Hazing of hazardous wildlife; and
(D) Habitat modification and management of sources of forage, water, and shelter to reduce the attractiveness of
the area around the airport for hazardous wildlife.
(iii) Incidental take of larks caused by accidental aircraft strikes at airports on non-Federal lands is also exempted
from the prohibitions of section 9 of the Act.
(4) What agricultural activities are allowed on non-Federal land in the Willamette Valley in Oregon? Incidental take
of streaked horned lark will not be a violation of section 9 of the Act, if the incidental take results from accepted
agricultural (farming) practices implemented on farms consistent with State laws on non-Federal lands.
(i) For the purposes of this special rule, farm means any facility, including land, buildings, watercourses and
appurtenances, used in the commercial production of crops, nursery stock, livestock, poultry, livestock products,
poultry products, vermiculture products, or the propagation and raising of nursery stock.
(ii) For the purposes of this special rule, an agricultural (farming) practice means a mode of operation on a farm
that:
(A) Is or may be used on a farm of a similar nature;
(B) Is a generally accepted, reasonable, and prudent method for the operation of the farm to obtain a profit in
money;
(C) Is or may become a generally accepted, reasonable, and prudent method in conjunction with farm use;
(D) Complies with applicable State laws; and
(E) Is done in a reasonable and prudent manner.
(iii) Accepted agricultural (farming) practices include, but are not limited to, the following activities:
(A) Planting, harvesting, rotation, mowing, tilling, discing, burning, and herbicide application to crops;
(B) Normal transportation activities, and repair and maintenance of unimproved farm roads (this exemption does
not include improvement or construction of new roads) and graveled margins of rural roads;
(C) Livestock grazing according to normally acceptable and established levels;
(D) Hazing of geese or predators; and
(E) Maintenance of irrigation and drainage systems.
(5) What noxious weed control activities are allowed on non-Federal lands? Incidental take of streaked horned lark
will not be a violation of section 9 of the Act, if the incidental take results from routine removal or other
management of noxious weeds. Routine removal or other management of noxious weeds are limited to the
following, and must be conducted in such a way that impacts to non-target plants are avoided to the maximum
extent practicable:
(i) Mowing;
(ii) Herbicide and fungicide application;
(iii) Fumigation; and
(iv) Burning.
(b) Coastal California gnatcatcher (Polioptila californica californica). (1) Except as noted in paragraphs (b)(2) and
(3) of this section, all prohibitions of §17.31(a) and (b) shall apply to the coastal California gnatcatcher.
(2) Incidental take of the coastal California gnatcatcher will not be considered a violation of section 9 of the
Endangered Species Act of 1973, as amended (Act), if it results from activities conducted pursuant to the State of
California's Natural Community Conservation Planning Act of 1991 (NCCP), and in accordance with a NCCP plan
for the protection of coastal sage scrub habitat, prepared consistent with the State's NCCP Conservation and
Process Guidelines, provided that:
(i) The NCCP plan has been prepared, approved, and implemented pursuant to California Fish and Game Code
sections 2800-2840; and
(ii) The Fish and Wildlife Service (Service) has issued written concurrence that the NCCP plan meets the
standards set forth in 50 CFR 17.32(b)(2). The Service shall issue its concurrence pursuant to the provisions of the
Memorandum of Understanding (MOU), dated December 4, 1991, between the California Department of Fish and
Game and the Service regarding coastal sage scrub natural community conservation planning in southern
California. (Copies of the State's NCCP Conservation and Process Guidelines and the MOU are available from the
U.S. Fish and Wildlife Service, Carlsbad Field Office, 2730 Loker Avenue West, Carlsbad, CA 92008.) The Service
shall monitor the implementation of the NCCP plan and may revoke its concurrence under this paragraph (b)(2)(ii)
if the NCCP plan, as implemented, fails to adhere to the standards set forth in 50 CFR 17.32(b)(2).
(3) During the period that a NCCP plan referred to in paragraph (b)(2) of this section is being prepared, incidental
take of the coastal California gnatcatcher will not be a violation of section 9 of the Act if such take occurs within an
area under the jurisdiction of a local government agency that is enrolled and actively engaged in the preparation of
such a plan and such take results from activities conducted in accordance with the NCCP Conservation Guidelines
and Process Guidelines.
(4) The Service will monitor the implementation of the NCCP Conservation and Process Guidelines as a whole,
and will conduct a review every 6 months to determine whether the guidelines, as implemented, are effective in
progressing toward or meeting regional and subregional conservation objectives during the interim planning
period. If the Service determines that the guidelines are not effecting adequate progress toward or meeting
regional and subregional conservation objectives, the Service will consult with the California Department of Fish
and Game pursuant to the MOU to seek appropriate modification of the guidelines or their application as defined
therein. If appropriate modification of the guidelines or their application as defined therein does not occur, the
Service may revoke the interim take provisions of this special rule on a subregional or subarea basis. The Service
will publish the findings for revocation in the Federal Register and provide for a 30-day public comment period prior
to the effective date for revoking the provisions of the special rule in a particular area. Revocation would result in
the reinstatement of the take prohibitions set forth under 50 CFR 17.31(a) and (b) in the affected NCCP area.
(c) The following species in the parrot family: Salmon-crested cockatoo (Cacatua moluccensis), yellow-billed
parrot (Amazona collaria), white cockatoo (Cacatua alba), hyacinth macaw (Anodorhynchus hyacinthinus), and
scarlet macaw (Ara macao macao and scarlet macaw subspecies crosses (Ara macao macao and Ara macao
cyanoptera)).
(1) Except as noted in paragraphs (c)(2) and (c)(3) of this section, all prohibitions and provisions of §§17.31 and
17.32 of this part apply to these species.
(2) Import and export. You may import or export a specimen without a permit issued under §17.32 of this part only
when the provisions of parts 13, 14, 15, and 23 of this chapter have been met and you meet the following
requirements:
(i) Captive-bred specimens: The source code on the Convention on International Trade in Endangered Species of
Wild Fauna and Flora (CITES) document accompanying the specimen must be “F” (captive born), “C” (bred in
captivity), or “D” (bred in captivity for commercial purposes) (see 50 CFR 23.24); or
(ii) Specimens held in captivity prior to certain dates: You must provide documentation to demonstrate that the
specimen was held in captivity prior to the dates specified in paragraph (c)(2)(ii)(A), (B), (C), (D), or (E) of this
section. Such documentation may include copies of receipts, accession or veterinary records, CITES documents,
or wildlife declaration forms, which must be dated prior to the specified dates.
(A) For salmon-crested cockatoos: January 18, 1990 (the date this species was transferred to CITES Appendix I).
(B) For yellow-billed parrots: April 11, 2013 (the date this species was listed under the Endangered Species Act of
1973, as amended (Act) (16 U.S.C. 1531 et seq.)).
(C) For white cockatoos: July 24, 2014 (the date this species was listed under the Endangered Species Act of
1973, as amended (Act) (16 U.S.C. 1531 et seq.)).
(D) For hyacinth macaws: September 12, 2018 (the date this species was listed under the Endangered Species
Act of 1973, as amended (Act) (16 U.S.C. 1531 et seq.)).
(E) For scarlet macaws: March 28, 2019 (the date this species was listed under the Endangered Species Act of
1973, as amended (Act) (16 U.S.C. 1531 et seq.)).
(3) Interstate commerce. Except where use after import is restricted under §23.55 of this chapter, you may deliver,
receive, carry, transport, or ship in interstate commerce and in the course of a commercial activity, or sell or offer to
sell, in interstate commerce the species listed in this paragraph (c) without a permit under the Act.
(d) Hawaiian goose (Branta sandvicensis) (nene). (1) Definitions. For the purposes of this paragraph (d):
(i) Nene means the Hawaiian goose (Branta sandvicensis).
(ii) Intentional harassment means an intentional act that creates the likelihood of injury to wildlife by annoying it to
such an extent as to significantly disrupt normal behavior patterns, which include, but are not limited to, breeding,
feeding, or sheltering. Intentional harassment may include prior purposeful actions to attract, track, wait for, or
search out nene, or purposeful actions to deter nene.
(iii) Person means a person as defined by section 3(13) of the Act.
(iv) Qualified biologist means an individual with a combination of academic training in the area of wildlife biology or
related discipline and demonstrated field experience in the identification and life history of nene.
(2) Prohibitions. The following prohibitions apply to the nene except as provided under paragraph (d)(3) of this
section and §§17.4 through 17.6:
(i) Import or export as provided in §17.21(b).
(ii) Take as provided in §17.21(c)(1).
(iii) Possession and other acts with unlawfully taken specimens as provided in §17.21(d)(1).
(iv) Interstate or foreign commerce in the course of commercial activity as provided in §17.21(e).
(v) Sale or offer for sale as provided in §17.21(f).
(vi) Attempt to commit, solicit another to commit, or to cause to be committed, any of the acts described in
paragraphs (d)(2)(i) through (v) of this section.
(3) Exceptions from prohibitions. The following exceptions from prohibitions apply to the nene:
(i) Authorization provided under §17.32.
(ii) Take as provided in §17.21(c)(2) through (7). However, §17.21(c)(5)(i) through (iv) does not apply.
(iii) Take incidental to an otherwise lawful activity caused by:
(A) Intentional harassment of nene that is not likely to cause direct injury or mortality. A person may harass nene
on lands they own, rent, or lease, if the action is not likely to cause direct injury or mortality of nene. Techniques for
such harassment may include the use of predator effigies (including raptor kites, predator replicas, etc.),
commercial chemical bird repellents, ultrasonic repellers, audio deterrents (noisemakers, pyrotechnics, etc.),
herding or harassing with trained or tethered dogs, or access control (including netting, fencing, etc.). Nene may
also be harassed in the course of surveys that benefit and further the recovery of nene. Such harassment
techniques must avoid causing direct injury or mortality to nene. Before implementation of any such intentional
harassment activities during the nene breeding season (September through April), a qualified biologist
knowledgeable about the nesting behavior of nene must survey in and around the area to determine whether a
nest or goslings are present. If a nest is discovered, the Service and authorized State wildlife officials must be
notified within 72 hours (see paragraph (d)(4) of this section for contact information) and the following measures
implemented to avoid disturbance of nests and broods:
(1) No disruptive activities may occur within a 100-foot (30-meter) buffer around all active nests and broods until
the goslings have fledged;
(2) Brooding adults (i.e., adults with an active nest or goslings) or adults in molt may not be subject to intentional
harassment at any time; and
(3) The landowner must arrange follow-up surveys of the property by qualified biologists to assess the status of
birds present.
(B) Nonnative predator control or habitat management activities. A person may incidentally take nene in the course
of carrying out nonnative predator control or habitat management activities for nene conservation purposes if
reasonable care is practiced to minimize effects to the nene.
(1) Nonnative predator control activities for the conservation of nene include use of fencing, trapping, shooting,
and toxicants to control predators, and related activities such as performing efficacy surveys, trap checks, and
maintenance duties. Reasonable care for predator control activities may include, but is not limited to, procuring
and implementing technical assistance from a qualified biologist on predator control methods and protocols prior to
application of methods; compliance with all State and Federal regulations and guidelines for application of predator
control methods; and judicious use of methods and tool adaptations to reduce the likelihood of nene ingesting bait,
interacting with mechanical devices, or being injured or dying from interaction with mechanical devices.
(2) Habitat management activities for the conservation of nene include: Mowing, weeding, fertilizing, herbicide
application, and irrigating existing pasture areas for conservation purposes; planting native food resources;
providing watering areas, such as water units or ponds or catchments, designed to be safe for goslings and
flightless/molting adults; providing temporary supplemental feeding and watering stations when appropriate, such
as under poor quality forage or extreme conditions (e.g., drought or fire); if mechanical mowing of pastures for
conservation management purposes is not feasible, alternate methods of keeping grass short, such as grazing;
and large-scale restoration of native habitat (e.g., feral ungulate control, fencing). Reasonable care for habitat
management may include, but is not limited to, procuring and implementing technical assistance from a qualified
biologist on habitat management activities, and best efforts to minimize nene exposure to hazards (e.g., predation,
habituation to feeding, entanglement, and vehicle collisions).
(C) Actions carried out by law enforcement officers in the course of official law enforcement duties. When acting in
the course of their official duties, State and local government law enforcement officers, working in conjunction with
authorized wildlife biologists and wildlife rehabilitators in the State of Hawaii, may take nene for the following
purposes:
(1) Aiding or euthanizing sick, injured, or orphaned nene;
(2) Disposing of a dead specimen; or
(3) Salvaging a dead specimen that may be used for scientific study; or
(4) Possession and other acts with unlawfully taken specimens as provided in §17.21(d)(2) through (4)).
(4) Reporting and disposal requirements. Any injury or mortality of nene associated with the actions excepted
under paragraphs (d)(3)(iii)(A) through (C) of this section must be reported to the Service and authorized State
wildlife officials within 72 hours, and specimens may be disposed of only in accordance with directions from the
Service. Reports should be made to the Service's Office of Law Enforcement at (808) 861-8525, or the Service's
Pacific Islands Fish and Wildlife Office at (808) 792-9400. The State of Hawaii Department of Land and Natural
Resources, Division of Forestry and Wildlife may be contacted at (808) 587-0166. The Service may allow
additional reasonable time for reporting if access to these offices is limited due to closure.
(e) Elfin-woods warbler (Setophaga angelae). (1) Prohibitions. Except as noted in paragraph (e)(2) of this section,
all prohibitions and provisions of 50 CFR 17.31 and 17.32 apply to the elfin-woods warbler.
(2) Exemptions from prohibitions. Incidental take of the elfin-woods warbler will not be considered a violation of
section 9 of the Act if the take results from any of the following when conducted within habitats currently occupied
by the elfin-woods warbler provided these activities abide by the conservation measures set forth in this paragraph
(e) and are conducted in accordance with applicable State, Federal, and local laws and regulations:
(i) The conversion of sun-grown coffee to shade-grown coffee plantations by the restoration and maintenance
(i.e.,removal of invasive, exotic, and feral species; shade and coffee tree seasonal pruning; shade and coffee tree
planting and replacement; coffee bean harvest by hands-on methods; and the use of standard pest control
methods and fertilizers within the plantations) of shade-grown coffee plantations and native forests associated with
this type of crop. To minimize disturbance to the elfin-woods warbler, shade and coffee tree seasonal pruning must
be conducted between September 1 and February 28, which is the time period outside the peak of the elfin-woods
warbler's breeding season. The Service considers the use of pest control methods (e.g., pesticides, herbicides)
and fertilizers “standard” when it is used only twice a year during the establishment period of shade and coffee
trees (i.e., the first 2 years). Once the shade-grown coffee system reaches its functionality and structure (i.e., 3 to
4 years), little or no chemical fertilizers, herbicides, or pesticides may be used.
(ii) Riparian buffer establishment though the planting of native vegetation and selective removal of exotic species.
(iii) Reforestation and forested habitat enhancement projects within secondary forests (i.e., young and mature) that
promote the establishment or improvement of habitat conditions for the species by the planting of native trees,
selective removal of native and exotic trees, seasonal pruning of native and exotic trees, or a combination of
these.
[43 FR 6233, Feb. 14, 1978, as amended at 58 FR 65095, Dec. 10, 1993; 60 FR 36010, July 12, 1995; 72 FR
37372, July 9, 2007; 73 FR 23970, May 1, 2008; 76 FR 30780, May 26, 2011; 76 FR 54713, Sept. 2, 2011; 78 FR
15641, Mar. 12, 2013; 78 FR 61502, Oct. 3, 2013; 79 FR 20084, Apr. 10, 2014; 79 FR 35900, June 24, 2014; 81
FR 47048, July 20, 2016; 81 FR 40547, June 22, 2016; 83 FR 39916, Aug. 13, 2018; 84 FR 6311, Feb. 26, 2019;
84 FR 69946, Dec. 19, 2019]
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§17.42 Special rules—reptiles.
(a) American alligator (Alligator mississippiensis)—(1) Definitions. For purposes of this paragraph (a) the following
definitions apply:
(i) American alligator means any specimen of the species Alligator mississippiensis, whether alive or dead,
including any skin, part, product, egg, or offspring thereof held in captivity or from the wild.
(ii) The definitions of crocodilian skins and crocodilian parts in §23.70(b) of this subchapter apply to this paragraph
(a).
(2) Taking. No person may take any American alligator, except:
(i) Any employee or agent of the Service, any other Federal land management agency, or a State conservation
agency, who is designated by the agency for such purposes, may, when acting in the course of official duties, take
an American alligator.
(ii) Any person may take an American alligator in the wild, or one which was born in captivity or lawfully placed in
captivity, and may deliver, receive, carry, transport, ship, sell, offer to sell, purchase, or offer to purchase such
alligator in interstate or foreign commerce, by any means whatsoever and in the course of a commercial activity in
accordance with the laws and regulations of the State of taking subject to the following conditions:
(A) Any skin of an American alligator may be sold or otherwise transferred only if the State or Tribe of taking
requires skins to be tagged by State or tribal officials or under State or tribal supervision with a Service-approved
tag in accordance with the requirements in part 23 of this subchapter; and
(B) Any American alligator specimen may be sold or otherwise transferred only in accordance with the laws and
regulations of the State or Tribe in which the taking occurs and the State or Tribe in which the sale or transfer
occurs.
(3) Import and export. Any person may import or export an American alligator specimen provided that it is in
accordance with part 23 of this subchapter.
(4) Recordkeeping. (i) Any person not holding an import/export license issued by the Service under part 14 of this
subchapter and who imports, exports, or obtains permits under part 23 of this subchapter for the import or export
of American alligator shall keep such records as are otherwise required to be maintained by all import/export
licensees under part 14 of this subchapter. Such records shall be maintained as in the normal course of business,
reproducible in the English language, and retained for 5 years from the date of each transaction.
(ii) Subject to applicable limitations of law, duly authorized officers at all reasonable times shall, upon notice, be
afforded access to examine such records required to be kept under paragraph (a)(4)(i) of this section, and an
opportunity to copy such records.
(b) Green sea turtle (Chelonia mydas), loggerhead sea turtle (Caretta caretta), olive ridley sea turtle (Lepidochelys
olivacea) (these do not include the populations listed as endangered in §17.11).
(1) Prohibitions. Subject to the permits allowable under the following paragraph (b)(2) of this section, all of the
provisions set forth in §17.31 (which incorporate portions of §17.21) shall apply to this wildlife with the following
exceptions:
(i) Section 17.21(c)(2) (self-defense) is not applicable.
(ii) In §17.21(c)(3)(i), the word “orphaned” is replaced by the word “stranded.”
(iii) Delete §17.21(c)(3)(iv) (Wildlife threatening human safety).
(iv) [Reserved]
(v) The prohibition against taking shall not apply to incidental catches, as specified in 50 CFR 227.72(e).
(vi) The prohibition against taking within the United States or the territorial sea of the United States shall not apply
to subsistence taking, as specified in 50 CFR 227.72(f).
(2) Permits. (i) For those activities which come under the jurisdiction of the Service, only permits for scientific
purposes, enhancement of propagation or survival, zoological exhibition or educational purposes, are available
under §17.32. Procedures for issuance of permits are found in §17.32 and, for those activities which come under
the jurisdiction of the National Marine Fisheries Service, subpart E of part 220. All the provisions of §17.32 apply to
permits issued by the Service.
(c) Threatened crocodilians—(1) What are the definitions of terms used in this paragraph (c)?
(i) Threatened crocodilian means any live or dead specimen of the following species:
(A) Broad-snouted caiman (Caiman latirostris) originating in Argentina;
(B) Brown caiman (Caiman crocodilus fuscus, including Caiman crocodilus chiapasius);
(C) Common caiman (Caiman crocodilus crocodilus);
(D) Yacare caiman (Caiman yacare);
(E) Nile crocodile (Crocodylus niloticus); and
(F) Saltwater crocodile (Crocodylus porosus) originating in Australia (also referred to as Australian saltwater
crocodile).
(ii) The definitions of crocodilian skins and crocodilian parts in §23.70(b) and re-export in §23.5 of this subchapter
apply to this paragraph (c).
(2) What activities involving threatened crocodilians are prohibited by this rule? (i) All provisions of §§17.31 and
17.32 apply to live specimens, including viable eggs, of all threatened crocodilians and to any specimen of the
Appendix-I Nile crocodile.
(ii) Except as provided in paragraph (c)(2)(i) of this section, the following prohibitions apply to threatened
crocodilians.
(A) Import, export, and re-export. Except as provided in paragraph (c)(3) of this section, it is unlawful to import,
export, or re-export, or attempt to import, export, or re-export without valid permits as required under parts 17 and
23 of this subchapter any threatened crocodilians, including their skins, parts, and products.
(B) Commercial activity. Except as provided in paragraph (c)(3) of this section, it is unlawful, in the course of a
commercial activity, to sell or offer for sale, deliver, receive, carry, transport, or ship in interstate or foreign
commerce any threatened crocodilians, including their skins, parts, and products.
(C) It is unlawful for any person subject to the jurisdiction of the United States to commit, attempt to commit, solicit
to commit, or cause to be committed any acts described in paragraphs (c)(2)(i) and (c)(2)(ii)(A) and (B) of this
section.
(3) What activities involving threatened crocodilians are allowed by this rule? Except as provided in (c)(2)(i), you
may import, export, or re-export, or sell or offer for sale, deliver, receive, carry, transport, or ship in interstate or
foreign commerce and in the course of a commercial activity, threatened crocodilian skins, parts, and products
without a threatened species permit otherwise required under §17.32 provided the requirements of parts 13, 14,
and 23 of this subchapter and the requirements of paragraphs (c)(3) and (4) of this section have been met.
(i) Skins and parts. Except as provided in (c)(3)(ii) of this section, the import, export, or re-export of threatened
crocodilian skins and crocodilian parts is allowed provided the following conditions are met:
(A) Each crocodilian skin and crocodilian part imported, exported, or re-exported must be tagged or labeled in
accordance with §23.70 of this subchapter.
(B) Any countries re-exporting crocodilian skins or parts must have implemented an administrative system for the
effective matching of imports and re-exports.
(C) If a shipment contains more than 25 percent replacement tags, the U.S. Management Authority will consult
with the Management Authority of the re-exporting country before clearing the shipment. Such shipments may be
seized if we determine that the requirements of the Convention have not been met.
(D) The country of origin and any intermediary country(s) must be effectively implementing the Convention. If we
receive persuasive information from the CITES Secretariat or other reliable sources that a specific country is not
effectively implementing the Convention, we will prohibit or restrict imports from such country(s) as appropriate for
the conservation of the species.
(ii) Meat, skulls, scientific specimens, products, and noncommercial personal or household effects. The tagging
requirements in paragraph (c)(3)(i) of this section for skins and parts do not apply to the import, export, or reexport of threatened crocodilian meat, skulls, scientific specimens, or products or to the noncommercial import,
export, or re-export of personal effects in accompanying baggage or household effects.
(4) When and how will the Service inform the public of additional restrictions in trade of threatened crocodilians?
Except in rare cases involving extenuating circumstances that do not adversely affect the conservation of the
species, the Service will issue an information bulletin (posted on our
websites, http://www.fws.gov/le and http://www.fws.gov/international) announcing additional restrictions on trade of
specimens of threatened crocodilians if any of the following criteria are met:
(i) The country is listed in a Notification to the Parties by the CITES Secretariat as not having designated
Management and Scientific Authorities.
(ii) The country is identified in any action adopted by the Conference of the Parties to the Convention, the Standing
Committee, or in a Notification issued by the CITES Secretariat, whereby Parties are asked not to accept
shipments of specimens of any CITES species from the country in question or of any crocodilian species listed in
the CITES Appendices.
(iii) We determine, based on information from the CITES Secretariat or other reliable sources, that the country is
not effectively implementing the provisions of the Convention.
(5) Reporting requirements for yacare caiman range countries—(i) Biennial reports. Range countries (Argentina,
Bolivia, Brazil, and Paraguay) wishing to export specimens of yacare caiman to the United States for commercial
purposes must provide a biennial report containing the most recent information available on the status of the
species. The first submission of a status report will be required as of December 31, 2001, and every 2 years
thereafter on the anniversary of that date. For each range country, all of the following information must be included
in the report.
(A) Recent distribution and population data, and a description of the methodology used to obtain such estimates.
(B) Description of research projects currently being conducted related to the biology of the species in the wild,
particularly reproductive biology (for example, age or size when animals become sexually mature, number of
clutches per season, number of eggs per clutch, survival of eggs, survival of hatchlings).
(C) Description of laws and programs regulating harvest, including approximate acreage of land set aside as
natural reserves or national parks that provide protected habitat for yacare caiman.
(D) Description of current sustainable harvest programs, including ranching (captive rearing of specimens
collected from the wild as eggs or juveniles) and farming (captive-breeding) programs.
(E) Current harvest quotas for wild populations.
(F) Export data for the last 2 years. Information should be organized according to the source of specimens such as
wild-caught, captive-reared, or captive-bred.
(ii) Review and restrictions. The U.S. Scientific Authority will conduct a review every 2 years, using information in
the biennial reports and other available information, to determine whether range country management programs
are effectively achieving conservation benefits for the yacare caiman. Based on the best available information, we
may restrict trade from a range country if we determine that the conservation or management status of threatened
yacare caiman populations has changed, such that continued recovery of the population in that country may be
compromised. Trade restrictions, as addressed in paragraph (c)(4) of this section, may be implemented based on
one or more of the following factors:
(A) Failure to submit the reports described above, or failure to respond to requests for additional information.
(B) A change in range country laws or regulations that lessens protection for yacare caiman.
(C) A change in range country management programs that lessens protection for the species.
(D) A documented decline in wild population numbers.
(E) A documented increase in poaching.
(F) A documented decline in habitat quality or quantity.
(G) Other natural or manmade factors affecting the species' recovery.
(d) Blue-tailed mole skink (Eumeces egregius lividus) and sand skink (Neoseps reynoldsi). (1) No person shall
take these species, except in accordance with applicable State fish and wildlife conservation laws and regulations
for educational purposes, scientific purposes, the enhancement or survival of the species, zoological exhibition,
and other conservation purposes consistent with the Act.
(2) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to taking of
these species is also a violation of the Endangered Species Act.
(3) No person shall possess, sell, deliver, carry, transport, ship, import, or export, by any means whatever, any
such species taken in violation of applicable State fish and wildlife conservation laws or regulations.
(4) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraph (c) (1) through (3) of this section.
(5) Taking of these species for purposes other than those described in paragraph (c)(1) of this section, including
taking incidental to carrying out otherwise lawful activities, is prohibited except when permitted under §§17.23 and
17.32.
(e) Desert tortoise (Gopherus agassizii)—(1) Definition. For the purposes of this paragraph (e) “desert tortoise”
shall mean any member of the species Gopherus agassizii, whether alive or dead, and any part, product, egg, or
offspring thereof, found outside of Arizona (south and east of the Colorado River) and Mexico, regardless of natal
origin or place of removal from the wild.
(2) Applicable provisions. The provisions of §17.31-17.32 shall apply to any desert tortoise subject to this
paragraph (e).
(f) Bog turtle (Clemmys muhlenbergii), southern population—(1) Definitions of terms. For the purposes of this
paragraph (f): Bog turtle of the southern population means any member of the species Clemmys
muhlenbergii,within Georgia, North Carolina, South Carolina, Tennessee and Virginia, regardless of whether in the
wild or captivity, and also applies to the progeny of any such turtle.
(2) Prohibitions. Except as provided in paragraph (f)(3) of this section, the provisions of Sec. 17.31 (a) and (b) of
this part applies to bog turtles of the southern population (see also 50 CFR part 23).
(3) Take. Incidental take, that is, take that results from, but is not the purpose of, carrying out an otherwise lawful
activity, does not apply to bog turtles of the southern population.
(g) Northern Mexican gartersnake (Thamnophis eques megalops)—(1) Prohibitions. Except as noted in paragraph
(g)(2) of this section, all prohibitions and provisions of §§17.31 and 17.32 apply to the northern Mexican
gartersnake.
(2) Exemptions from prohibitions. Incidental take of the northern Mexican gartersnake will not be considered a
violation of section 9 of the Act if the take occurs on non-Federal land and is incidental to activities pertaining to
construction, continued use, and maintenance of stock tanks. A stock tank is an existing or future impoundment in
an ephemeral drainage or upland site constructed primarily as a watering site for livestock.
(h) Black pinesnake (Pituophis melanoleucus lodingi).
(1) Prohibitions. Except as noted in paragraph (h)(2) of this section, all prohibitions and provisions of §§17.31 and
17.32 apply to the black pinesnake.
(2) Exemptions from prohibitions. Incidental take of the black pinesnake will not be considered a violation of
section 9 of the Act if the take results from:
(i) Prescribed burning, including all fire break establishment and maintenance actions, as well as actions taken to
control wildfires.
(ii) Herbicide application for invasive plant species control, site-preparation, and mid-story and understory woody
vegetation control. All exempted herbicide applications must be conducted in a manner consistent with Federal
law, including Environmental Protection Agency label restrictions; applicable State laws; and herbicide application
guidelines as prescribed by herbicide manufacturers.
(iii) All forest management activities that maintain lands in a forested condition, except for:
(A) Conversion of longleaf-pine-dominated forests (>51 percent longleaf in the overstory) to other forest cover
types or land uses; and
(B) Those activities causing significant subsurface disturbance, including, but not limited to, shearing, wind-rowing,
stumping, disking (except during fire break creation or maintenance), root-raking, and bedding.
[42 FR 2076, Jan. 10, 1977, as amended at 43 FR 32809, July 28, 1978; 44 FR 59084, Oct. 12, 1979; 45 FR
17589, Mar. 19, 1980; 45 FR 78154, Nov. 25, 1980; 48 FR 46336, Oct. 12, 1983; 50 FR 25678, June 20, 1985; 50
FR 45409, Oct. 31, 1985; 52 FR 21063, June 4, 1987; 52 FR 42662, Nov. 6, 1987; 55 FR 12191, Apr. 2, 1990; 61
FR 32366, June 24, 1996; 62 FR 59622, Nov. 4, 1997; 65 FR 25879, May 4, 2000; 72 FR 48446, Aug. 23, 2007;
78 FR 38190, June 25, 2013; 79 FR 38746, July 8, 2014; 80 FR 60489, Oct. 6, 2015]
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§17.43 Special rules—amphibians.
(a) San Marcos salamander (Eurycea nana). (1) All provisions of §17.31 apply to this species, except that it may
be taken in accordance with applicable State law.
(2) Any violation of State law will also be a violation of the Act.
(b) Chiricahua leopard frog (Lithobates chiricahuensis).
(1) What activities are prohibited? Except as noted in paragraph (b)(2) of this section, all prohibitions of §17.31 will
apply to the Chiricahua leopard frog.
(2) What activities are allowed on private, State, or Tribal land? Incidental take of the Chiricahua leopard frog will
not be considered a violation of section 9 of the Act, if the take results from livestock use at or maintenance
activities of livestock tanks located on private, State, or Tribal lands. A livestock tank is defined as an existing or
future impoundment in an ephemeral drainage or upland site constructed primarily as a watering site for livestock.
(c) California tiger salamander (Ambystoma californiense).
(1) Which populations of the California tiger salamander are covered by this special rule? This rule covers the
California tiger salamander (Ambystoma californiense) rangewide.
(2) What activities are prohibited? Except as noted in paragraph (c)(3) of this section, all prohibitions of §17.31 will
apply to the California tiger salamander.
(3) What activities are allowed on private or Tribal land? Incidental take of the California tiger salamander will not
be a violation of section 9 of the Act, if the incidental take results from routine ranching activities located on private
or Tribal lands. Routine ranching activities include, but are not limited to, the following:
(i) Livestock grazing according to normally acceptable and established levels of intensity in terms of the number of
head of livestock per acre of rangeland;
(ii) Control of ground-burrowing rodents using poisonous grain according to the labeled directions and local, State,
and Federal regulations and guidelines (The use of toxic or suffocating gases is not exempt from the prohibitions
due to their nontarget-specific mode of action.);
(iii) Control and management of burrow complexes using discing and grading to destroy burrows and fill openings;
(iv) Routine management and maintenance of stock ponds and berms to maintain livestock water supplies (This
exemption does not include the intentional introduction of species into a stock pond that may prey on California
tiger salamander adults, larvae, or eggs.);
(v) Routine maintenance or construction of fences for grazing management;
(vi) Planting, harvest, or rotation of unirrigated forage crops as part of a rangeland livestock operation;
(vii) Maintenance and construction of livestock management facilities such as corrals, sheds, and other ranch
outbuildings;
(viii) Repair and maintenance of unimproved ranch roads (This exemption does not include improvement, upgrade,
or construction of new roads.);
(ix) Discing of fencelines or perimeter areas for fire prevention control;
(x) Placement of mineral supplements; and
(xi) Control and management of noxious weeds.
(d) California red-legged frog (Rana aurora draytonii)—(1) Which populations of the California red-legged frog are
covered by this special rule? This rule covers the California red-legged frog (Rana aurora draytonii) rangewide.
(2) What activities are prohibited? Except as noted in paragraph (d)(3) of this section, all prohibitions of §17.31 will
apply to the California red-legged frog.
(3) What activities are allowed on private or Tribal land? Incidental take of the California red-legged frog will not be
a violation of section 9 of the Act, if the incidental take results from routine ranching activities located on private or
Tribal lands. Routine ranching activities include, but are not limited to, the following:
(i) Livestock grazing according to normally acceptable and established levels of intensity in terms of the number of
head of livestock per acre of rangeland;
(ii) Control of ground-burrowing rodents using poisonous grain according to the labeled directions and local, State,
and Federal regulations and guidelines (In areas where California red-legged frogs and California tiger
salamanders coexist, the use of toxic or suffocating gases is not exempt from the prohibitions due to their
nontarget-specific mode of action.);
(iii) Control and management of burrow complexes using discing and grading to destroy burrows and fill openings
(This exemption does not apply to areas within 0.7 mi (1.2 km) of known or potential California red-legged frog
breeding ponds.);
(iv) Routine management and maintenance of stock ponds and berms to maintain livestock water supplies (This
exemption does not include the intentional introduction of species into a stock pond (including non-native fish and
bullfrogs) that may prey on California red-legged frog adults, larvae, or eggs.);
(v) Routine maintenance or construction of fences for grazing management;
(vi) Planting, harvest, or rotation of unirrigated forage crops as part of a rangeland livestock operation;
(vii) Maintenance and construction of livestock management facilities such as corrals, sheds, and other ranch
outbuildings;
(viii) Repair and maintenance of unimproved ranch roads (This exemption does not include improvement, upgrade,
or construction of new roads.);
(ix) Discing of fencelines or perimeter areas for fire prevention control;
(x) Placement of mineral supplements; and
(xi) Control and management of noxious weeds.
(e) Georgetown salamander (Eurycea naufragia.)
(1) Prohibitions. Except as noted in paragraph (e)(2) of this section, all prohibitions and provisions of §§17.31 and
17.32 apply to the Georgetown salamander.
(2) Exemptions from prohibitions. Incidental take of the Georgetown salamander will not be considered a violation
of section 9 of the Act if the take occurs on non-Federal land from regulated activities that are conducted
consistent with the water quality protection measures contained in chapter 11.07 and Appendix A of the City of
Georgetown (Texas) Unified Development Code (UDC), as endorsed by the U.S. Fish and Wildlife Service.
[40 FR 44415, Sept. 26, 1975, as amended at 45 FR 47363, July 14, 1980; 67 FR 40811, June 13, 2002; 69 FR
47248, Aug. 4, 2004; 71 FR 19293, Apr. 13, 2006; 77 FR 16375, Mar. 20, 2012; 80 FR 47428, Aug. 7, 2015]
return arrow Back to Top
§17.44 Special rules—fishes.
(a) Lahontan cutthroat trout, Paiute cutthroat trout, and Arizona trout (Salmo clarki henshawi, Salmo clarki
seleniris,and Salmo apache). (1) All the provisions of §17.31 apply to these species, except that they may be
taken in accordance with applicable State law.
(2) Violation of State law will also be a violation of the Act.
(b) Bayou darter (Etheostoma rubrum). (1) All the provisions of §17.31 apply to this species, except that they may
be taken in accordance with applicable State law.
(2) Any violation of State law will also be a violation of the Act.
(c) Slender chub (Hybopsis cahni), spotfin chub (Erimonax monachus), slackwater darter (Etheostoma boschungi),
and yellowfin madtom (Noturus flavipinnis). (1) All the provisions of §17.31 apply to these species, except that they
may be taken in accordance with applicable State law.
(2) Any violation of State law will also be a violation of the Act.
(d) Leopard darter (Percina pantherina). (1) All provisions of §17.31 apply to this species, except that it may be
taken in accordance with applicable State law.
(2) Any violation of State law will also be a violation of the Act.
(e) Little Kern golden trout (Salmo aguabonita whitei). (1) All provisions of §17.31 apply to this species, except that
it may be taken in accordance with applicable State law.
(2) Any violation of State law will also be a violation of the Act.
(f) Greenback cutthroat trout (Salmo clarki stomias). (1) All provisions of §17.31 apply to this species, except that it
may be taken in accordance with applicable State law.
(2) Any violation of State law will also be a violation of the Act.
(g) Chihuahua chub (Gila nigrescens). (1) All provisions of §17.31 apply to this species, except that it may be
taken in accordance with applicable State law.
(2) Any violation of State law will also be a violation of the Endangered Species Act.
(h) Yaqui catfish (Ictalurus pricei) and beautiful shiner (Notropis formosus). (1) All provisions of §17.31 apply to
these species, except that they may be taken for educational, scientific, or conservation purposes in accordance
with applicable Arizona State laws and regulations.
(2) Any violation of State law will also be a violation of the Endangered Species Act.
(i) Big Spring spinedace (Lepidomeda mollispinis pratensis). (1) All the provisions of §17.31 apply to this species,
except that it may be taken in accordance with applicable State fish and wildlife conservation laws and regulations
in the following instances: educational purposes, scientific purposes, the enhancement of propagation or survival
of the species, zoological exhibition, and other conservation purposes consistent with the Act.
(2) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to this species
will also be a violation of the Endangered Species Act.
(j) Hutton tui chub (Gila bicolor subspecies). (1) No person shall take this species, except in accordance with
applicable State fish and wildlife conservation laws and regulations in the following instances: for educational
purposes, scientific purposes, the enhancement of propagation or survival of the species, zoological exhibition,
and other conservation purposes consistent with the Act.
(2) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to the taking of
this species will also be a violation of the Endangered Species Act.
(3) No person shall possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever, any
such species taken in violation of these regulations or in violation of applicable State fish and wildlife conservation
laws or regulations.
(4) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (j) (1) through (3) of this section.
(k) Niangua darter, Etheostoma nianguae. (1) No person shall take the species, except in accordance with
applicable State fish and wildlife conservation laws and regulations in the following instances: educational
purposes, scientific purposes, the enhancement of propagation or survival of the species, zoological exhibition,
and other conservation purposes consistent with the Act.
(2) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to the taking of
this species will also be a violation of the Endangered Species Act.
(3) No person shall possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever, any
such species taken in violation of these regulations or in violation of applicable State fish and wildlife conservation
laws or regulations.
(4) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (k) (1) through (3) of this section.
(l) Warner sucker (Catostomus warnerensis). (1) No person shall take the species, except in accordance with
applicable State fish and wildlife conservation laws and regulations in the following instances:
(i) For educational purposes, scientific purposes, the enhancement of propagation or survival of the species,
zoological exhibition, and other conservation purposes consistent with the Act;
(ii) Incidental to State-permitted recreational fishing activities, provided that the individual fish taken is immediately
returned to its habitat.
(2) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to the taking of
this species will also be a violation of the Endangered Species Act.
(3) No person shall possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever, any
such species taken in violation of these regulations or in violation of applicable State fish and wildlife laws or
regulations.
(4) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (l) (1) through (3) of this section.
(m) Desert dace (Eremichthys acros). (1) No person shall take the species, except in accordance with applicable
State fish and wildlife conservation laws and regulations in the following instances: For educational purposes,
scientific purposes, the enhancement of propagation or survival of the species, zoological exhibition, and other
conservation purposes consistent with the Act.
(2) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to the taking of
this species will also be a violation of the Endangered Species Act.
(3) No person shall possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever, any
such species taken in violation of applicable State fish and wildlife conservation laws or regulations.
(4) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (m) (1) through (3) of this section.
(n) Railroad Valley springfish (Crenichthys nevadae). (1) No person shall take the species, except in accordance
with applicable State fish and wildlife conservation laws and regulations in the following instances: for educational
purposes, scientific purposes, the enhancement of propagation or survival of the species, zoological exhibition,
and other conservation purposes consistent with the Act.
(2) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to the taking of
this species will also be a violation of the Endangered Species Act.
(3) No person shall possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever, any
such species taken in violation of these regulations or in violation of applicable State fish and wildlife conservation
laws or regulations.
(4) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (n) (1) through (3) of this section.
(o) Sonora chub (Gila ditaenia). (1) No person shall take the species, except in accordance with applicable State
fish and wildlife conservation laws and regulations in the following instances:
(i) For educational purposes, scientific purposes, the enhancement of propagation or survival of the species,
zoological exhibition, and other conservation purposes consistent with the Act; or,
(ii) Incidental to State-permitted recreational fishing activities, provided that the individual fish taken is immediately
returned to its habitat.
(2) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to the taking of
this species will also be a violation of the Endangered Species Act.
(3) No person shall possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever, any
such species taken in violation of these regulations or in violation of applicable State fish and wildlife conservation
laws or regulations.
(4) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (o) (1) through (3) of this section.
(p) Kentucky arrow darter (Etheostoma spilotum).
(1) Prohibitions. Except as noted in paragraph (p)(2) of this section, all prohibitions and provisions of 50 CFR
17.31 and 17.32 apply to the Kentucky arrow darter.
(2) Exceptions from prohibitions.
(i) All of the activities listed in paragraph (p)(2)(ii) of this section must be conducted in a manner that:
(A) Maintains connectivity of suitable Kentucky arrow darter habitats, allowing for dispersal between streams;
(B) Minimizes instream disturbance by occurring during low-flow periods when possible; and
(C) Maximizes the amount of instream cover that is available for the species.
(ii) Incidental take of the Kentucky arrow darter will not be considered a violation of section 9 of the Act if the take
results from any of the following when conducted within habitats currently occupied by the Kentucky arrow darter:
(A) Channel reconfiguration or restoration projects that create natural, physically stable, ecologically functioning
streams (or stream and wetland systems) that are reconnected with their groundwater aquifers. These projects
can be accomplished using a variety of methods, but the desired outcome is a natural, sinuous channel with low
shear stress (force of water moving against the channel); low bank heights and reconnection to the floodplain; a
reconnection of surface and groundwater systems, resulting in perennial flows in the channel; riffles and pools
composed of existing soil, rock, and wood instead of large imported materials; low compaction of soils within
adjacent riparian areas; and inclusion of riparian wetlands. First- to third-order headwater streams reconstructed in
this way would offer suitable habitats for the Kentucky arrow darter and contain stable channel features, such as
pools, glides, runs, and riffles, which could be used by the species for spawning, rearing, growth, feeding,
migration, and other normal behaviors.
(B) Bank stabilization projects that use State-approved bioengineering methods (specified by the Kentucky Energy
and Environment Cabinet and the Kentucky Transportation Cabinet) to replace preexisting, bare, eroding stream
banks with vegetated, stable stream banks, thereby reducing bank erosion and instream sedimentation and
improving habitat conditions for the species. Following these methods, stream banks may be stabilized using live
stakes (live, vegetative cuttings inserted or tamped into the ground in a manner that allows the stake to take root
and grow), live fascines (live branch cuttings, usually willows, bound together into long, cigar-shaped bundles), or
brush layering (cuttings or branches of easily rooted tree species layered between successive lifts of soil fill).
These methods would not include the sole use of quarried rock (rip-rap) or the use of rock baskets or gabion
structures.
(C) Bridge and culvert replacement/removal projects that remove migration barriers (e.g., collapsing, blocked, or
perched culverts) or generally allow for improved upstream and downstream movements of Kentucky arrow
darters while maintaining normal stream flows, preventing bed and bank erosion, and improving habitat conditions
for the species.
(D) Repair and maintenance of U.S. Forest Service concrete plank stream crossings on the Daniel Boone National
Forest (DBNF) that allow for safe vehicle passage while maintaining instream habitats, reducing bank and stream
bed erosion and instream sedimentation, and improving habitat conditions for the species. These concrete plank
crossings have been an effective stream crossing structure on the DBNF and have been used for decades. Over
time, the planks can be buried by sediment, undercut during storm events, or simply break down and decay. If
these situations occur, the DBNF must make repairs or replace the affected plank.
(q) [Reserved]
(r) Pecos bluntnose shiner (Notropis simus pecosensis). (1) No person shall take the species, except in
accordance with applicable State fish and wildlife conservation laws and regulations in the following instances:
(i) For educational purposes, scientific purposes, the enhancement of propagation or survival of the species,
zoological exhibition, and other conservation purposes consistent with the Act; or,
(ii) Incidental to State permitted recreational fishing activities, provided that the individual fish taken is immediately
returned to its habitat.
(2) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to taking of this
species will also be a violation of the Endangered Species Act.
(3) No person shall possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever any
such species taken in violation of these regulations or in violation of applicable State fish and wildlife conservation
laws or regulations.
(4) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (r) (1) through (3) of this section.
(s) Waccamaw Silverside (Menidia extensa). (1) No person shall take the species, except in accordance with
applicable State fish and wildlife conservation laws and regulations.
(2) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to the taking of
this species will also be a violation of the Endangered Species Act.
(3) No person shall possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever, any
such species taken in violation of these regulations or in violation of applicable State fish and wildlife conservation
laws or regulations.
(4) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (s) (1) through (3) of this section.
(t) Little Colorado spinedace (Lepidomeda vittata). (1) No person shall take this species, except in accordance with
applicable State Fish and Wildlife conservation laws and regulations in the following instances: for educational
purposes, scientific purposes, the enhancement of propagation or survival of the species, zoological exhibition,
and other conservation purposes consistent with the Act.
(2) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to the taking of
this species is also a violation of the Endangered Species Act.
(3) No person shall possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever, any
such species taken in violation of these regulations or in violation of applicable State fish and wildlife conservation
laws or regulations.
(4) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (t) (1) through (3) of this section.
(u) Pygmy sculpin (Cottus pygmaeus). The City of Anniston Water Works and Sewer Board will continue to use
Coldwater Spring as a municipal water supply. Pumpage may remove all spring flow in excess of 3 cubic feet per
second (1,938,000 gallons per day).
(v) Gulf sturgeon (Acipenser oxyrhynchus desotoi). (1) No person shall take this species, except in accordance
with applicable State fish and wildlife conservation laws and regulations for educational purposes, scientific
purposes, the enhancement of propagation or survival of the species, zoological exhibition, or other conservation
purposes consistent with the Act.
(2) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to taking of this
species is also a violation of the Endangered Species Act.
(3) No person shall possess, sell, deliver, carry, transport, ship, import, or export, by any means whatever, any of
this species taken in violation of applicable State fish and wildlife conservation laws or regulations.
(4) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (v)(1) through (3) of this section.
(5) Taking of this species for purposes other than those described in paragraph (v)(1) of this section, including
taking incidental to otherwise lawful activities, is prohibited except when permitted under 50 CFR 17.32.
(w) What species are covered by this special rule? Bull trout (Salvelinus confluentus), wherever found in the
coterminous lower 48 States, except in the Jarbidge River Basin in Nevada and Idaho (see 50 CFR 17.44(x)).
(1) What activities do we prohibit? Except as noted in paragraph (w)(2) of this section, all prohibitions of 50 CFR
17.31 and exemptions of 50 CFR 17.32 shall apply to the bull trout in the coterminous United States as defined in
paragraph (w) of this section.
(i) No person may possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever, any
such species taken in violation of this section or in violation of applicable State, National Park Service, and Native
American Tribal fish and conservation laws and regulations.
(ii) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense listed in this special rule.
(2) What activities do we allow? In the following instances you may take this species in accordance with applicable
State, National Park Service, and Native American Tribal fish and wildlife conservation laws and regulations, as
constituted in all respects relevant to protection of bull trout in effect on November 1, 1999:
(i) Educational purposes, scientific purposes, the enhancement of propagation or survival of the species,
zoological exhibition, and other conservation purposes consistent with the Act; or
(ii) Fishing activities authorized under State, National Park Service, or Native American Tribal laws and
regulations;
(3) How does this rule relate to State protective regulations? Any violation of applicable State, National Park
Service, or Native American Tribal fish and wildlife conservation laws or regulations with respect to the taking of
this species is also a violation of the Endangered Species Act.
(x) Bull trout (Salvelinus confluentus), Jarbidge River population segment. (1) Prohibitions. Except as noted in
paragraph (x)(2) of this section, all prohibitions of 50 CFR 17.31 and exemptions of 50 CFR 17.32 apply to the bull
trout in the Jarbidge River population segment within the United States.
(2) Exceptions. No person may take this species, except in the following instances in accordance with applicable
State fish and wildlife conservation laws and regulations relevant to protection of bull trout in effect on April 8,
1999.
(i) For educational purposes, scientific purposes, the enhancement of propagation or survival of the species,
zoological exhibition, and other conservation purposes consistent with the Act;
(ii) Incidental to State-permitted recreational fishing activities, provided that any bull trout caught are immediately
returned to the stream.
(iii) The exceptions in paragraphs (x)(2) (i) and (ii) of this section will be in effect until April 9, 2001. At that time, all
take prohibitions of the Act will be reinstated for the Jarbidge River population segment unless exceptions to take
prohibitions are otherwise provided through a subsequent special rule.
(3) Any violation of applicable State fish and wildlife conservation laws or regulations with respect to the taking of
this species is also a violation of the Endangered Species Act.
(4) No person may possess, sell, deliver, carry, transport, ship, import, or export, any means whatsoever, any such
species taken in violation of this section or in violation of applicable State fish and conservation laws and
regulations.
(5) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (x)(2) through (4) of this section.
(y) Beluga sturgeon (Huso huso)
(1) How are various terms defined in this special rule? In addition to the definitions specified in §10.12 of
subchapter B of this chapter, we define certain terms that specifically apply to beluga sturgeon trade and this
special rule as follows:
Aquacultured beluga sturgeon products. Eggs, larvae, fingerlings, or other products derived from Huso
husocaptive-bred or grown in captivity for commercial purposes starting at least at the F1 generation in captivity
(i.e., captive-bred for at least one generation).
Beluga caviar. Processed unfertilized eggs from female Huso huso intended for human consumption, including
products containing such eggs (e.g., cosmetics).
Beluga meat. Excised muscle tissue of Huso huso destined for human consumption.
Black Sea. The contiguous waters of the Black Sea and the Sea of Azov.
CITES. The Convention on International Trade in Endangered Species of Wild Fauna and Flora.
Export. The transport of a beluga sturgeon specimen out of its country of origin.
Hatchery-origin beluga sturgeon. Specimens of Huso huso captive-bred solely in the littoral states, primarily for
reintroduction and stock enhancement purposes. Such specimens can occur in the natural marine environment of
the littoral states.
Live or living beluga sturgeon. Any living specimen of Huso huso, including viable unfertilized or fertilized eggs,
larvae, fingerlings, juveniles, and adults.
Littoral states. Azerbaijan, Bulgaria, Georgia, Islamic Republic of Iran, Kazakhstan, Romania, Russian Federation,
Serbia and Montenegro, Turkey, Turkmenistan, and Ukraine.
Re-export. Export of beluga sturgeon specimens that were previously imported.
Wild beluga sturgeon. Specimens of Huso huso born and reared in the natural marine environment within the
current or former geographic range of the species.
(2) What activities involving beluga sturgeon are affected by this rule? (i) International trade in beluga
sturgeon.Except as provided in paragraphs (y)(3) and (y)(5) of this section, all prohibitions and provisions of
§§17.31(a) and 17.32 apply to the international trade in beluga sturgeon, including its parts and derivatives. Live
beluga sturgeon remain subject to all the prohibitions and provisions of §§17.31(a) and 17.32.
(ii) Trade without CITES documents. Except as provided in paragraph (y)(3) of this section, you may not import,
export, or re-export, or present for export or re-export, beluga sturgeon or beluga sturgeon products without valid
CITES permits and other permits and licenses issued under parts 13, 17, and 23 of this chapter.
(iii) Commercial activity. Except as provided in paragraphs (y)(3) and (5) of this section and §17.32, you may not
sell or offer for sale, deliver, receive, carry, transport, or ship in interstate or foreign commerce in the course of a
commercial activity any beluga sturgeon or beluga sturgeon products.
(iv) It is unlawful for any person subject to the jurisdiction of the United States to commit, attempt to commit, solicit
to commit, or cause to be committed any acts described in paragraphs (y)(2)(ii) and (iii) of this section.
(3) What activities are exempted from threatened species permits by this rule? (i) Import, export or re-export, and
interstate and foreign commerce involving certain caviar and meat obtained from beluga sturgeon. You may
import, export or re-export, or conduct interstate or foreign commerce in beluga sturgeon caviar and meat without
a threatened species permit issued according to §17.32 only if the caviar and meat are derived from wild or
hatchery-origin beluga sturgeon that were caught and processed in the littoral states, or the caviar and meat are
exempt from permits because they originate from qualifying aquaculture facilities outside of littoral states
(see paragraph (y)(5) of this section). Also, the provisions in parts 13, 14, and 23 of this chapter and the following
requirements must be met:
(A) Beluga sturgeon caviar, including beluga sturgeon caviar in interstate commerce in the United States, must be
labeled in accordance with the CITES labeling requirements in 50 CFR part 23.
(B) The shipment must be accompanied by a valid CITES permit or certificate upon import, export, or re-export.
(C) For each shipment covered by this exemption, the country of origin and each country of re-export, and the
country of import involved in the trade of a particular shipment, must have designated both a CITES Management
Authority and Scientific Authority, and have not been identified by the CITES Conference of the Parties, the CITES
Standing Committee, or in a Notification from the CITES Secretariat as a country from which Parties should not
accept permits for beluga sturgeon or all CITES-listed species in general.
(D) The littoral state from which the beluga sturgeon caviar or meat originated has complied with all of the
requirements shown in paragraph (y)(4) of this section, and none of the exporting, importing, or re-exporting
countries involved in the commercial activity has been subject to an administrative trade restriction or suspension
as outlined in paragraphs (y)(6) and (7) of this section.
(E) Any relevant aquaculture facility located outside of a littoral state has complied with all of the requirements
shown in paragraph (y)(5) of this section.
(ii) Personal and household effects. You may import, export, or re-export, or conduct interstate or foreign
commerce in beluga sturgeon specimens that qualify as personal or household effects under 50 CFR part 23
without a threatened species permit otherwise required under §17.32. Trade suspensions or trade restrictions
administratively imposed by the Service under paragraphs (y)(6) or (y)(7) of this section may also apply to
personal and household effects of beluga sturgeon caviar.
(4) What must beluga sturgeon littoral states do to be authorized under the special rule to export to the United
States? The following requirements apply to the littoral states wishing to export beluga caviar or beluga meat to
the United States without the need for a threatened species permit issued under §17.32. These requirements
apply to all shipments of beluga caviar and beluga meat that originate in the littoral states, even if the shipments
are re-exported to the United States via an intermediary country. (See paragraph (y)(7) of this section for more
information on the Service's biennial reviews under the special rule.)
(i) Basin-wide beluga sturgeon management plans. By September 6, 2005, each littoral state wishing to export
beluga caviar or beluga meat to the United States without the need for a threatened species permit issued under
§17.32 must submit to the Service's Division of Scientific Authority a copy of a cooperative management plan for
its respective basin (i.e., Black Sea or Caspian Sea) that addresses Huso huso conservation. Each of these two
basin-wide management plans must be agreed to by all of the littoral states (not just exporting nations) in the Black
Sea or the Caspian Sea, as appropriate. Upon receipt, the Division of Scientific Authority will review these basinwide management plans within 90 days for completeness and clarity. If any elements of the management plans
are missing or unclear, we will ask the appropriate littoral states to provide additional information within 60 days of
the date we contact them. If the littoral states fail to respond or fail to submit basin-wide management plans by the
specified deadline, or if we are unable to confirm that all littoral states are signatories to those plans, we will
immediately suspend trade with all littoral states in the given basin (Caspian Sea or Black Sea) until we are
satisfied that such management plans exist. Submission of documents in English may help expedite the Service's
review. These cooperative management plans must contain the following elements:
(A) A clear statement of the recovery and management objectives of the plan, including a specification of the
stock(s) concerned, a definition of what constitutes over-fishing for that stock, and a rebuilding objective and
schedule for that stock;
(B) A statement of standard regulations and habitat improvement strategies (e.g., size limits, target harvest rates,
quotas, seasons, fishing gear, effort caps, fish passage improvement, water quality controls) to be utilized by the
nations involved;
(C) A complete statement of the specific regulatory, monitoring, and research requirements that each cooperating
nation must implement to be in compliance with the management plan;
(D) A complete description of how stock survey data and fisheries data are used to establish annual catch and
export quotas, including a full explanation of any models used and the assumptions underlying those models;
(E) Procedures under which the nations may implement and enforce alternative management measures that
achieve the same conservation benefits for beluga sturgeon as the standards mentioned in paragraph (y)(4)(i)(B)
of this section; and
(F) A complete schedule by which nations must take particular actions to be in compliance with the plan.
(ii) National regulations. By September 6, 2005, each littoral state wishing to export beluga caviar or beluga meat
to the United States under this special rule must provide the Service's Division of Scientific Authority with copies of
national legislation and regulations that implement the basin-wide cooperative management plan described in
paragraph (y)(4)(i) of this section, including regulations pertaining to the harvest, trade, aquaculture, restocking,
and processing of beluga sturgeon. Upon receipt, the Division of Scientific Authority will review these national laws
and regulations within 90 days for completeness and clarity. If any elements of the national legislation or national
fishery regulations are missing or unclear, we will ask the appropriate littoral states to provide additional
information within 60 days of the date we contact them. If the littoral states fail to respond or fail to submit copies of
national laws and regulations by the specified deadline, we will immediately suspend trade with the given littoral
states until we are satisfied that such laws and regulations are in effect. Submission of documents in English may
help expedite the Service's review.
(iii) CITES compliance. Trade in beluga sturgeon specimens must comply with CITES requirements in 50 CFR part
23. Except for specimens that qualify as personal or household effects under 50 CFR part 23, all beluga sturgeon
specimens, including those exempted from threatened species permits under this special rule, must be
accompanied by valid CITES documents upon import, export, or re-export. Beluga sturgeon caviar, including
beluga sturgeon caviar in interstate commerce in the United States, must be labeled in accordance with the CITES
labeling requirements in 50 CFR part 23.
(iv) Initial reporting period. Until September 6, 2005, no threatened species permits will be required for the import,
export, re-export, or interstate or foreign commerce of beluga sturgeon caviar and meat that originated in the
littoral states, in order to provide the littoral states time to submit the required documentation. After this 6-month
period, the exemption from threatened species permits will continue only while the Service reviews littoral state
compliance with paragraphs (y)(4)(i) through (iv) of this section. If this review demonstrates that the provisions of
this special rule are not met, the Service will announce and institute trade restrictions or suspensions in beluga
sturgeon caviar or meat with one or more littoral states as per paragraph (y)(7) of this section.
(v) Biennial reports. Littoral state governments wishing to export specimens of beluga sturgeon caviar or meat to
the United States under this special rule must provide to the Service's Division of Scientific Authority reports
containing the most recent information available on the status of the species, following the information guidelines
specified below. The Service must receive the first report no later than December 1, 2005, and every 2 years
thereafter on the anniversary of that date. Starting in December 2005, and thereafter on a biennial basis, the
Service will review the national reports within 90 days of receiving them and any other pertinent information on wild
beluga sturgeon conservation. If any elements of the biennial reports are missing or unclear, the Service will ask
the appropriate littoral states to provide additional information within 60 days of the date we contact them. If the
littoral states fail to respond or fail to submit biennial reports by the specified deadline, we will immediately
suspend trade with the given littoral states (see paragraph (y)(7) of this section for details on how such a
suspension would be instituted and announced). Submission of documents in English may help expedite the
Service's review. We propose to use these reviews to determine whether littoral state management programs are
leading to recovery of wild beluga sturgeon stocks. For each littoral state, the following information must be
provided in the biennial reports:
(A) A description of the specific fishery regulations that affect the harvest of Huso huso in the respective littoral
state, with any changes from the previous report highlighted;
(B) A description of any revisions to the cooperative management program mentioned in paragraph (y)(4)(i) of this
section, including any new models, assumptions, or equations used to set harvest and export quotas;
(C) New information obtained in the last 2 years on beluga sturgeon distribution, stock size, models used for
quota-setting, spawning activity, habitat use, hatchery programs and results, or other relevant subjects;
(D) A summary of law enforcement activities undertaken in the last 2 years, and a description of any changes in
programs to prevent poaching and smuggling, including indicators of their effectiveness;
(E) A summary of the revenues generated by the commercial exploitation of beluga sturgeon in the respective
littoral state, and a summary of any documented conservation benefits resulting from the commercial harvest
program in that country (e.g., revenues allocated to hatchery and restocking programs or research programs); and
(F) Export data for the previous two calendar years.
(5) Can aquacultured beluga sturgeon products be exempt from threatened species permits if the products
originate outside the littoral states? We will consider exemptions from threatened species permits for beluga caviar
and meat obtained from aquaculture facilities outside the littoral states. These exemptions will be for individual
facilities, and would allow aquacultured beluga caviar and meat originating from these facilities to be imported,
exported, re-exported, or traded in interstate and foreign commerce without threatened species permits issued
under Section 10 of the Act. Aquaculture facilities within the United States could also be exempt from prohibitions
against take for purposes of harvesting caviar or meat (i.e., killing of beluga sturgeon), or for conducting activities
involving research to enhance the survival or propagation of the species. Facilities outside the littoral states
wishing to obtain such exemptions must submit a written request to the Division of Management Authority at the
address provided at 50 CFR 2.1(b) and provide information that shows, at a minimum, all of the following:
(i) The facility in question is using best management practices to prevent the escape of beluga sturgeon and
disease pathogens into local ecosystems, as certified by the relevant regulatory agency. In the case of the United
States, the relevant regulatory authority will be the state agency with jurisdiction over aquaculture. In the case of
foreign aquaculture facilities outside the littoral states, the relevant regulatory agency will be the designated CITES
Management Authority with jurisdiction over sturgeon. Best management practices that affect the applicant's
facility must be part of the application and available for Service review.
(ii) The facility in question has entered into a formal agreement with one or more littoral states to study, protect, or
otherwise enhance the survival of wild beluga sturgeon. Copies of such agreements must be provided.
(iii) The facility in question does not rely on wild beluga sturgeon for broodstock. Proof of broodstock origin,
including relevant CITES permits that accompanied broodstock specimens upon import into the United States,
must be part of the application.
(iv) Exemptions granted under paragraph (y)(5) of this section shall not apply to trade (import, export, re-export, or
interstate and foreign commerce) in live beluga sturgeon, and may be revoked at any time if the Service
determines that any of the criteria shown in paragraphs (y)(5)(i) through (iii) of this section are not met by the
facility. Applicants will be required to submit biennial reports on their compliance with paragraphs (y)(5)(i) through
(iii) of this section, starting on the second anniversary of any programmatic exemption granted to the applicants.
These biennial reports must show that exempted facilities have actively cooperated with one or more littoral states
in a meaningful way to support beluga sturgeon conservation. Any beluga caviar originating from aquaculture
facilities outside the littoral states must comply with CITES caviar-labeling requirements, even in interstate
commerce within the United States. We will publish an information notice if the Service grants a programmatic
exemption to any aquaculture facility outside the littoral states, and announce such actions through our website
and posting notices at our wildlife ports of entry. We will follow the provisions of paragraph (y)(7) of this section to
announce restrictions or revocations of such programmatic exemptions, based on our review of facilities' biennial
reports.
(6) How will the Service inform the public of CITES restrictions on trade in beluga sturgeon? We will issue a public
bulletin that identifies a restriction or suspension of trade in specimens of beluga sturgeon and post it on our
websites (http://le.fws.gov and http://international.fws.gov) and at our staffed wildlife ports of entry if any criterion in
paragraphs (y)(6)(i) or (ii) of this section is met:
(i) The country is lacking a designated Management Authority or Scientific Authority for the issuance of valid
CITES documents or their equivalent for beluga sturgeon.
(ii) The country is identified in any action adopted by the CITES Conference of the Parties, the CITES Standing
Committee, or in a Notification to the Parties issued by the CITES Secretariat as a country from which Parties are
asked not to accept shipments of specimens of beluga sturgeon or all CITES-listed species.
Note to paragraph (y)(6): A listing of all countries that have not designated either a Management Authority or
Scientific Authority, or that have been identified as countries from which Parties should not accept permits, is
available by writing to the Division of Management Authority at the address provided at 50 CFR 2.1(b).
(7) How will the Service set trade restrictions or prohibitions under the special rule? The Service's Division of
Scientific Authority will conduct a biennial review of beluga sturgeon conservation based on information in the
cooperative basin-wide management plans, national regulations and laws, and biennial reports (submitted as per
paragraph (y)(4) of this section, and, for aquaculture facilities, as per paragraph (y)(5)(iv) of this section). We will
combine that review with a review of other relevant information (e.g., scientific literature, law enforcement data,
government-to-government consultations) to determine whether littoral state management programs and
aquaculture operations are effectively achieving conservation benefits for beluga sturgeon. Based on this
information, or the failure to obtain it, the Service may restrict or prohibit trade from a littoral state, a re-exporting
intermediary country, or an entire basin (i.e., the Caspian Sea or Black Sea) or a specific aquaculture facility
outside the littoral states if we determine that the conservation or management status of beluga sturgeon has been
adversely affected and the continued recovery of beluga sturgeon may be compromised. The decision to restrict or
prohibit trade in beluga sturgeon products on a national, basin, or region-wide scale will depend on the scope of
the problem observed, the magnitude of the threat to wild beluga sturgeon, and whether remedial action is
necessary at a national, basin, or region-wide scale.
(i) Trade restrictions or suspensions will result basin-wide, for specific littoral states, or for non-littoral state
aquaculture facilities under one or more of the following scenarios:
(A) Failure to submit any of the reports, legislation, and management plans described in paragraph (y)(4) of this
section, or failure to respond to requests for additional information;
(B) A change in regional cooperative management that threatens the recovery of wild beluga sturgeon;
(C) A change in littoral state laws or regulations that compromises beluga sturgeon recovery or survival in the wild;
(D) Adoption of scientifically unsound hatchery practices or restocking programs for beluga sturgeon;
(E) A decline in wild Huso huso populations, as documented in national reports outlined above or the scientific
literature, that goes unaddressed by regional or national management programs;
(F) Failure to address poaching or smuggling in beluga sturgeon, their parts, or products in the littoral states or reexporting countries, as documented in national reports described above or other law enforcement sources;
(G) Failure of the littoral states to address the loss of beluga sturgeon habitat quality or quantity;
(H) Failure of the littoral states or re-exporting countries to follow the caviar-labeling recommendations of the
CITES Parties (currently embodied in Resolution Conf. 12.7);
(I) Recommendations from the CITES Standing Committee to suspend trade in beluga sturgeon from one or more
countries; or
(J) An aquaculture facility outside the littoral states has been issued a programmatic exemption from threatened
species permits under paragraph (y)(5) of this section, but is not abiding by the provisions of paragraphs (y)(5)(i)
through (iii) of this section, or, based on the biennial reports required under paragraph (y)(5) of this section, has
not actively cooperated with one or more littoral states in a meaningful way to support beluga sturgeon
conservation.
(K) Any other natural or human-induced phenomenon that threatens the survival or recovery of beluga sturgeon.
(ii) We will publish an information notice in the Federal Register, as well as on our Web site and at our wildlife ports
of entry, if the Service's Division of Scientific Authority administratively suspends or restricts trade in beluga
sturgeon products after determining that wild beluga sturgeon stock status worsens or threats to the species
increase. This information notice will provide:
(A) The problem(s) identified in the biennial reports or other salient documents.
(B) The scope of the problem and the number of nations involved.
(C) The scope of the trade restriction or suspension we are imposing, including products covered, duration of the
restriction or suspension, and criteria for lifting it and reinstating any exemption to threatened species permits.
(D) How the public can provide input, make comments, and recommend remedial action to withdraw the trade
measures imposed.
(z) Gila trout (Oncorhynchus gilae). (1) Except as noted in paragraph (z)(2) of this section, all prohibitions of 50
CFR 17.31 and exemptions of 50 CFR 17.32 apply to the Gila trout.
(i) No person may possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever, any
such species taken in violation of this section or in violation of applicable fish and conservation laws and
regulations promulgated by the States of New Mexico or Arizona.
(ii) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed any
offense listed in paragraph (z)(1)(i) of this section.
(2) In the following instances you may take Gila trout in accordance with applicable State fish and wildlife
conservation laws and regulations to protect this species in the States of New Mexico or Arizona:
(i) Fishing activities authorized under New Mexico or Arizona laws and regulations; and
(ii) Educational purposes, scientific purposes, the enhancement of propagation or survival of the species,
zoological exhibition, and other conservation purposes consistent with the Endangered Species Act.
(3) The four relict populations of Gila trout (Main Diamond Creek, South Diamond Creek, Spruce Creek, and
Whiskey Creek) will not be opened to fishing.
(4) Any changes to State recreational fishing regulations will be made by the States in collaboration with the
Service.
(5) Any violation of State applicable fish and wildlife conservation laws or regulations with respect to the taking of
this species is also a violation of the Endangered Species Act of 1973, as amended.
(aa) Shovelnose sturgeon (Scaphirhynchus platorynchus). (1) Within the geographic areas set forth in paragraph
(aa)(2) of this section, except as expressly noted in this paragraph, take of any shovelnose sturgeon, shovelnosepallid sturgeon hybrids, or their roe associated with or related to a commercial fishing activity is prohibited. Capture
of shovelnose sturgeon or shovelnose-pallid sturgeon hybrids in commercial fishing gear is not prohibited if it is
accidental or incidental to otherwise legal commercial fishing activities, such as commercial fishing targeting
nonsturgeon species, provided the animal is released immediately upon discovery, with all roe intact, at the point
of capture.
(2) The shovelnose and shovelnose-pallid sturgeon hybrid populations covered by this special rule occur in
portions of Arkansas, Iowa, Illinois, Kansas, Kentucky, Louisiana, Missouri, Mississippi, Montana, North Dakota,
Nebraska, South Dakota, and Tennessee. The specific areas are:
(i) The portion of the Missouri River in Iowa, Kansas, Missouri, Montana, North Dakota, Nebraska, and South
Dakota;
(ii) The portion of the Mississippi River downstream from the Melvin Price Locks and Dam (Lock and Dam 26) in
Arkansas, Illinois, Kentucky, Louisiana, Missouri, Mississippi, and Tennessee;
(iii) The Platte River downstream of the Elkhorn River confluence in Nebraska;
(iv) The portion of the Kansas River downstream from the Bowersock Dam in Kansas;
(v) The Yellowstone River downstream of the Bighorn River confluence in North Dakota and Montana; and
(vi) The Atchafalaya River in Louisiana.
(3) A map showing the area covered by this special rule (the area of shared habitat between shovelnose and pallid
sturgeon) follows:
eCFR graphic er01se10.000.gif
View or download PDF
(bb) Okaloosa darter (Etheostoma okaloosae).
(1) Except as noted in paragraphs (bb)(2) and (bb)(3) of this section, all prohibitions of 50 CFR 17.31 and
exemptions of 50 CFR 17.32 apply to the Okaloosa darter.
(i) No person may possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever, any
Okaloosa darters taken in violation of this section or in violation of applicable State fish and wildlife conservation
laws or regulations.
(ii) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense listed in this special rule.
(2) The following activities, which may result in incidental take of the Okaloosa darter, are allowed on Eglin Air
Force Base (AFB), provided that the activities occur in accordance with applicable Federal, State, and local laws,
and are consistent with a Service-approved Integrated Natural Resources Management Plan by Eglin AFB and
with Eglin AFB's Threatened and Endangered Species Component Plan:
(i) Prescribed fire for land management to promote a healthy ecosystem;
(ii) Instream habitat restoration;
(iii) Unpaved range road stabilization; and
(iv) Removal or replacement of culverts for the purpose of road decommissioning, improving fish passage, or
enhancing stream habitat.
(3) Scientific research and monitoring activities that may result in incidental take of the Okaloosa darter are
allowed, provided these activities are consistent with a Service-approved Okaloosa darter recovery plan, or
otherwise approved by the Service, whether those activities occur on or off of Eglin AFB.
(4) Take caused by any activities not listed in paragraph (bb)(2) and (bb)(3) of this section is prohibited.
[40 FR 44415, Sept. 26, 1975]
Editorial Note: For Federal Register citations affecting §17.44, see the List of CFR Sections Affected, which
appears in the Finding Aids section of the printed volume and at www.govinfo.gov.
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§17.45 Special rules—snails and clams.
[Reserved]
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§17.46 Special rules—crustaceans.
(a) Madison Cave isopod (Antrolana lira). (1) All provisions of §17.31 (a) and (b) apply to this species except that it
may be taken for scientific purposes without Federal permits issued pursuant to these regulations: Provided, that
all other Federal, State, or local laws, regulations, ordinances or other restrictions or limitations have been
complied with.
(b) [Reserved]
[47 FR 43701, Oct. 4, 1982]
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§17.47 Special rules—insects.
(a) Cassius blue butterfly (Leptotes cassius theonus), Ceraunus blue butterfly (Hemiargus ceraunus antibubastus),
and Nickerbean blue butterfly (Cyclargus ammon).
(1) The provisions of §17.31(c) apply to these species (cassius blue butterfly, ceraunus blue butterfly, nickerbean
blue butterfly), regardless of whether in the wild or in captivity, and also apply to the progeny of any such butterfly.
(2) Any violation of State law will also be a violation of the Act.
(3) Incidental take, that is, take that results from, but is not the purpose of, carrying out an otherwise lawful activity,
will not apply to the cassius blue butterfly, ceraunus blue butterfly, and nickerbean blue butterfly.
(4) Collection of the cassius blue butterfly, ceraunus blue butterfly, and nickerbean blue butterfly is prohibited in
coastal counties south of Interstate 4 and extending to the boundaries of the State of Florida at the endpoints of
Interstate 4 at Tampa and Daytona Beach. Specifically, such activities are prohibited in the following counties:
Brevard, Broward, Charlotte, Collier, De Soto, Hillsborough, Indian River, Lee, Manatee, Pinellas, Sarasota, St.
Lucie, Martin, Miami-Dade, Monroe, Palm Beach, and Volusia.
(b) Dakota skipper (Hesperia dacotae). (1) Which populations of the Dakota skipper are covered by this special
rule? This rule covers the distribution of Dakota skipper in the United States.
(2) Prohibitions. Except as noted in paragraph (b)(3) of this section, all prohibitions and provisions of §§17.31 and
17.32 apply to the Dakota skipper.
(3) Exemptions from prohibitions. Incidental take of Dakota skipper will not be a violation of section 9 of the Act if it
occurs as a result of the following activities (except where explicitly stated otherwise, these activities must be
associated with livestock ranching):
(i) Fence construction and maintenance.
(ii) Livestock gathering and management. The installation and maintenance of corrals, loading chutes, and other
livestock working facilities must be carefully sited with respect to the location and distribution of important Dakota
skipper habitat.
(iii) Development and maintenance of livestock watering facilities.
(iv) Noxious weed control. Incidental take of Dakota skipper that results from spraying of herbicides is not a
violation of section 9 of the Act, except such take that results from broadcast spraying, which is the application of
herbicides evenly across the entire application area. Incidental take that results from mowing to control one or
more noxious weed species would also not be a violation of section 9 of the Act.
(v) Haying. For the purposes of this rule, native haylands do not include lands that had previously been plowed
and were then replanted to native or nonnative vegetation, but native haylands do include areas within
transportation (e.g., road, highway, railroad) rights-of-ways and corridors where native grasses are mowed for hay.
Haying of native haylands no earlier than July 16 (after July 15) would not be a violation of section 9 of the Act.
Mowing of replanted grasslands (grasslands replanted on formerly plowed or cultivated lands) or tame haylands or
grasslands (planted hayland or grassland comprising primarily nonnative grass species, such as smooth brome
(Bromus inermis inermis)) would also not be a violation of section 9 of the Act at any time of the year.
(vi) Mowing section line rights-of-way and recreational trails. Mowing of section line rights-of-way (typically
disturbed soil that has been contoured for a roadway) would not be a violation of section 9 of the Act. Mowing of
recreational trails (travelways established either through construction or use that are intended for and passable by
foot traffic, bicycles, in-line skates, wheelchairs, or cross-country skis) would not be a violation of section 9 of the
Act, regardless of whether the trails are associated with livestock ranching.
(vii) Livestock (cattle, bison, or horse) grazing on private, State, or tribal land.
(c) Western glacier stonefly (Zapada glacier) and meltwater lednian stonefly (Lednia tumana)—
(1) Prohibitions. The following prohibitions that apply to endangered wildlife also apply to western glacier stonefly
and meltwater lednian stonefly except as provided under paragraph (c)(2) of this section and §§17.4 and 17.5. It is
unlawful for any person subject to the jurisdiction of the United States to commit, to attempt to commit, to solicit
another to commit, or cause to be committed, any of the following acts in regard to these species:
(i) Import or export, as set forth at §17.21(b).
(ii) Take, as set forth at §17.21(c)(1).
(iii) Possession and other acts with unlawfully taken specimens, as set forth at §17.21(d)(1).
(iv) Interstate or foreign commerce in the course of commercial activity, as set forth at §17.21(e).
(v) Sale or offer for sale, as set forth at §17.21(f).
(2) Exceptions from prohibitions. In regard to this species, you may:
(i) Conduct activities as authorized by a permit under §17.32.
(ii) Take, as set forth at §17.21(c)(3) and (4) for endangered wildlife.
(iii) Possess and engage in other acts, as set forth at §17.21(d)(2) for endangered wildlife.
(iv) In addition to any other provisions of this part, any employee or agent of the Service, of the National Marine
Fisheries Service, or of a State conservation agency that is operating a conservation program pursuant to the
terms of a cooperative agreement with the Service in accordance with section 6(c) of the Act, who is designated by
that agency for such purposes, may, when acting in the course of official duties, take those threatened species of
wildlife that are covered by an approved cooperative agreement to carry out conservation programs.
[77 FR 20986, Apr. 6, 2012, as amended at 79 FR 67348, Oct. 24, 2014; 84 FR 64227, Nov. 21, 2019]
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§17.48 Special rules—common sponges and other
forms. [Reserved]
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Subpart E—Similarity of Appearance
Source: 42 FR 32377, June 24, 1977, unless otherwise noted.
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§17.50 General.
(a) Whenever a species which is not Endangered or Threatened closely resembles an Endangered or Threatened
species, such species may be treated as either Endangered or Threatened if the director makes such
determination in accordance with section 4(e) of the Act and the criteria of paragraph (b) of this section. After the
Director has made such determination in accordance with the notification procedures specified in the Act, such
species shall appear in the list in §17.11 (Wildlife) or §17.12 (Plants) with the notation “(S/A)” (similarity of
appearance) in the “Status” column, following either a letter “E” or a letter “T” to indicate whether the species is
being treated as Endangered or Threatened.
(b) In determining whether to treat a species as Endangered or Threatened due to similarity of appearance, the
Director shall consider the criteria in section 4(e) of the Act, as indicated below:
(1) The degree of difficulty enforcement personnel would have in distinguishing the species, at the point in
question, from an Endangered or Threatened species (including those cases where the criteria for recognition of a
species are based on geographical boundaries);
(2) The additional threat posed to the Endangered or Threatened species by the loss of control occasioned
because of the similarity of appearance; and
(3) The probability that so designating a similar species will substantially facilitate enforcement and further the
purposes and policy of the Act.
[42 FR 32377, June 24, 1977, as amended at 81 FR 51605, Aug. 4, 2016]
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§17.51 Treatment as endangered or threatened.
(a) Any species listed in §17.11 or §17.12, pursuant to §17.50, shall be treated as Endangered or Threatened, as
indicated in the “Status” column.
(b) All of the provisions of subparts C (Endangered Wildlife), D (Threatened Wildlife), F (Endangered Plants) or G
(Threatened Plants), as appropriate, shall apply to any such species.
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§17.52 Permits—similarity of appearance.
Upon receipt of a complete application and unless otherwise indicated in a rule found at §§17.40 through 17.48,
§§17.73 through 17.78, or §§17.84 through 17.86, the Director may issue permits for any activity otherwise
prohibited with a species designated as endangered or threatened due to its similarity of appearance. Such a
permit may authorize a single transaction, a series of transactions, or a number of activities over a specified period
of time.
(a) Application requirements. An application for a permit under this section must be submitted to the Director by
the person who wishes to engage in the prohibited activity. The permit for activities involving interstate commerce
of plants must be obtained by the seller; in the case of wildlife, the permit must be obtained by the buyer. The
application must be submitted on an official application form (Form 3-200) provided by the Service, or must contain
the general information and certification required by §13.12(a) of this subchapter. It must include, as an
attachment, all of the following information: Documentary evidence, sworn affidavits, or other information to show
species identification and the origin of the wildlife or plant in question. This information may be in the form of
hunting licenses, hide seals, official stamps, export documents, bills of sales, certification, expert opinion, or other
appropriate information.
(b) Issuance criteria. Upon receiving an application completed in accordance with paragraph (a) of this section, the
Director will decide whether or not a permit should be issued. In making his decision, the Director shall consider, in
addition to the general criteria, in §13.21(b) of this subchapter, the following factors:
(1) Whether the information submitted by the applicant appears reliable;
(2) Whether the information submitted by the applicant adequately identifies the wildlife or plant in question so as
to distinguish it from any Endangered or Threatened wildlife or plant.
(c) Permit conditions. In addition to the general conditions set forth in part 13 of this subchapter, every permit
issued under this section shall be subject to the following special conditions:
(1) If indicated in the permit, a special mark, to be specified in the permit, must be applied to the wildlife or plant,
and remain for the time designated in the permit;
(2) A copy of the permit or an identification label, which includes the scientific name and the permit number, must
accompany the wildlife or plant or its container during the course of any activity subject to these regulations.
(d) Duration of permits. The duration of a permit issued under this section shall be designated on the face of the
permit.
[42 FR 32377, June 24, 1977, as amended at 81 FR 51605, Aug. 4, 2016]
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Subpart F—Endangered Plants
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§17.61 Prohibitions.
(a) Except as provided in a permit issued pursuant to §17.62 or §17.63, it is unlawful for any person subject to the
jurisdiction of the United States to commit, to attempt to commit, to solicit another to commit, or to cause to be
committed, any of the acts described in paragraphs (b) through (e) of this section in regard to any Endangered
plant.
(b) Import or export. It is unlawful to import or to export any Endangered plant. Any shipment in transit through the
United States is an importation and an exportation, whether or not it has entered the country for customs
purposes.
(c) Remove and reduce to possession. (1) It is unlawful to remove and reduce to possession any endangered
plant from an area under Federal jurisdiction.
(2) Notwithstanding paragraph (c)(1) of this section, any employee or agent of the Service, any other Federal land
management agency, or a State conservation agency, who is designated by that agency for such purposes, may,
when acting in the course of official duties, remove and reduce to possession endangered plants from areas under
Federal jurisdiction without a permit if such action is necessary to:
(i) Care for a damaged or diseased specimen;
(ii) Dispose of a dead specimen; or
(iii) Salvage a dead specimen which may be useful for scientific study.
(3) Any removal and reduction to possession pursuant to paragraph (c)(2) of this section must be reported in
writing to the U.S. Fish and Wildlife Service, Division of Law Enforcement, P.O. Box 28006, Washington, DC
20005, within 5 days. The specimen may only be retained, disposed of, or salvaged in accordance with written
directions from the Service.
(4) Notwithstanding paragraph (c)(1) of this section, any qualified employee or agent of a State conservation
agency which is a party to a Cooperative Agreement with the Service in accordance with section 6(c) of the Act,
who is designated by that agency for such purposes, may, when acting in the course of official duties, remove and
reduce to possession from areas under Federal jurisdiction those endangered plants which are covered by an
approved cooperative agreement for conservation programs in accordance with the Cooperative Agreement,
provided that such removal is not reasonably anticipated to result in:
(i) The death or permanent damage of the specimens;
(ii) The removal of the specimen from the State where the removal occurred; or
(iii) The introduction of the specimen so removed, or of any propagules derived from such a specimen, into an
area beyond the historical range of the species.
(d) Interstate or foreign commerce. It is unlawful to deliver, receive, carry, transport, or ship in interstate or foreign
commerce, by any means whatsoever, and in the course of a commercial activity, an endangered plant.
(e) Sale or offer for sale. (1) It is unlawful to sell or to offer for sale in interstate or foreign commerce any
endangered plant.
(2) An advertisement for the sale of any endangered plant which carries a warning to the effect that no sale may
be consummated until a permit has been obtained from the Service, shall not be considered an offer for sale within
the meaning of this paragraph.
[44 FR 54060, Sept. 18, 1979, as amended at 50 FR 39690, Sept. 30, 1985]
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§17.62 Permits for scientific purposes or for the
enhancement of propagation or survival.
Upon receipt of a complete application the Director may issue a permit authorizing any activity otherwise
prohibited by §17.61, in accordance with the issuance criteria of this section, for scientific purposes or for
enhancing the propagation or survival of endangered plants. (See §17.72 for permits for threatened plants.) Such
a permit may authorize a single transaction, a series of transactions, or a number of activities over a specified
period of time.
(a) Application requirements. A person wishing to get a permit for an activity prohibited by §17.61 submits an
application to conduct activities under this paragraph. For interstate commerce activities the seller gets the permit
for plants coming from cultivated stock and the buyer gets the permit if the plants are taken from the wild. The
Service provides application Form 3-200, or you may submit the general information and certification required by
§13.12(a) of this subchapter. Application requirements differ for permits issued for plants taken from the wild
(excluding seeds), seeds and cultivated plants, or herbarium specimens. You must attach the following information
and any other information requested by the Director.
(1) For activities involving plants obtained from the wild (excluding seeds), provide the following information:
(i) The scientific names of the plants sought to be covered by the permit;
(ii) The estimated number of specimens sought to be covered by the permit;
(iii) The year, country, and approximate place where taking occurred or will occur;
(iv) If the activities would involve removal and reduction to possession of a plant from an area under Federal
jurisdiction, the year, State, county, or any other description such as place name, township, and range designation
that will precisely place the location where the proposed removal and reduction to possession will occur, the name
of the Federal entity having jurisdiction over the area, and the name, title, address, and phone number of the
person in charge of the area.
(v) The name and address of the institution or other facility where the plant sought to be covered by the permit will
be used or maintained;
(vi) A brief description of the applicant's expertise and facilities as related to the proposed activity;
(vii) A statement of the applicant's willingness to participate in a cooperative propagation program, and to maintain
or contribute data relating to such efforts; and
(viii) A statement of the reasons why the applicant is justified in obtaining the permit, including:
(A) The activities sought to be authorized by the permit and the relationship of such activities to scientific purposes
or enhancing the propagation or survival of the species; and
(B) The planned disposition of such plant upon termination of the activities sought to be authorized.
(2) For activities involving seeds and cultivated plants, provide the following information:
(i) The scientific names of the plants sought to be covered by the permit;
(ii) A statement of the applicant's willingness to participate in a cooperative propagation program, and to maintain
or contribute data relating to the success of such efforts;
(iii) A justification of the activities sought to be authorized by the permit and the relationship of such activities to
scientific purposes or enhancing the propagation or survival of the species; and
(iv) If the activities would involve seeds obtained from the wild, additional information to evaluate the effects of
such taking upon the reproductive potential of the species where the taking will occur.
(v) If the activities would involve removal and reduction to possession of seeds from an area under Federal
jurisdiction, the year, State, county or any other description such as place name, township, and range designation
that will precisely place the location where the proposed removal and reduction to possession will occur, the name
of the Federal entity having jurisdiction over the area and the name, title, address, and phone number of the
person in charge of the area.
(3) For importation or exportation involving the non-commercial loan, exchange, or donation of herbarium or other
preserved, dried, or embedded museum specimens of any endangered species between scientists or scientific
institutions, provide the following information:
(i) The name and address of the institution or other facility where the plants sought to be covered by the permit will
be used or maintained; and
(ii) A justification of the activities sought to be authorized by the permit and the relationship of such activities to
scientific purposes or enhancing the propagation or survival of the species.
(4) When the activity applied for involves a species also regulated by the Convention on International Trade in
Endangered Species of Wild Fauna and Flora, additional requirements in part 23 of this subchapter must be met.
(b) Issuance criteria. Upon receiving an application completed in accordance with paragraph (a) of this section, the
Director will decide whether or not a permit should be issued. In making his decision, the Director shall consider, in
addition to the general criteria in §13.21(b) of this subchapter, the following factors:
(1) Whether the purpose for which the permit is requested will enhance the survival of the species in the wild;
(2) Whether the purpose for which the permit is requested will enhance the propagation of the species;
(3) The opinions or views of scientists or other persons or organizations having expertise concerning the plant or
other matters germane to the application; and
(4) Whether the expertise, facilities, or other resources available to the applicant appear adequate to successfully
accomplish the objectives stated in the application.
(c) Permit conditions. In addition to the general conditions set forth in part 13 of this subchapter, every permit
issued under this section shall be subject to the following special conditions:
(1) If requested, the permittee shall submit to the Director a written report of the activities authorized by the permit.
Such report must be postmarked by the date specified in the permit or otherwise requested by the Director.
(2) A copy of the permit or an identification label, which includes the scientific name, the permit number, and a
statement that the plant is of “wild origin” or “cultivated origin” must accompany the plant or its container during the
course of any activity subject to these regulations, unless the specimens meet the special conditions referred to in
paragraph (c)(3) of this section.
(3) In the case of plants that are herbarium specimens, or other preserved, dried or embedded museum
specimens to be imported or exported as a noncommercial loan, exchange or donation between scientists or
scientific institutions, the names and addresses of the consignor and consignee must be on each package or
container. A description such as “herbarium specimens” and the code letters assigned by the Service to the
scientists or scientific institution must be entered on the Customs declaration form affixed to each package or
container. If the specimens are of taxa also regulated by the Convention on International Trade in Endangered
Species of Wild Fauna and Flora, specific information must be entered on the Customs declaration label affixed to
the outside of each shipping container or package. See part 23 of this subchapter for requirements for trade in
CITES specimens between registered scientific institutions.
(d) Duration of permit. The duration of a permit issued under this section shall be designated on the face of the
permit.
[44 FR 54060, Sept. 18, 1979, as amended at 50 FR 39690, Sept. 30, 1985; 63 FR 52635, Oct. 1, 1998; 79 FR
30419, May 27, 2014]
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§17.63 Economic hardship permits.
Upon receipt of a complete application, the Director may issue a permit authorizing any activity otherwise
prohibited by §17.61, in accordance with Section 10(b) of the Act and the issuance criteria of this section, in order
to prevent undue economic hardship. No such exemption may be granted for the importation or exportation of a
species also listed in Appendix I of the Convention on International Trade in endangered Species of Wild Fauna
and Flora, if the specimen would be used in a commercial activity.
(a) Application requirements. An application for a permit under this section must be submitted to the Director by
the person allegedly suffering undue economic hardship because his desired activity is prohibited. The application
must be submitted on an official application form (Form 3-200) provided by the Service, or must contain the
general information and certification required by §13.12(a) of this subchapter. It must include, as an attachment, all
of the information required in §17.62 plus the following additional information.
(1) The possible legal or economic alternatives to the activity sought to be authorized by the permit.
(2) A full statement, accompanied by copies of all relevant correspondence, showing the applicant's involvement
with the plant sought to be covered by the permit (as well as his involvement with similar plants). The applicant
should include information on that portion of his income derived from activities involving such plants in relation to
the balance of his income during the calendar year immediately preceding either the Federal Register notice of
review of the status of the species or proposed rulemaking to list the species as Endangered, whichever is earlier.
(3) Where applicable, proof of a contract or other binding legal obligation which:
(i) Deals specifically with the plant sought to be covered by the permit;
(ii) Became binding prior to the date of the Federal Register notice of review of the status of the species or
proposed rulemaking to list the species as endangered, whichever is earlier; and
(iii) Will cause monetary loss of a given dollar amount if the permit sought under this section is not granted.
(b) Issuance criteria. Upon receiving an application completed in accordance with paragraph (a) of this section, the
Director will decide whether or not a permit should be issued for economic hardship, as defined in section 10(b) of
the Act. In making his decision, the Director shall consider, in addition to the general criteria in §13.21(b) of this
subchapter, the following factors:
(1) Whether the purpose for which the permit is requested will significantly affect the survival of the species in the
wild;
(2) The economic, legal, or other alternatives or relief available to the applicant;
(3) The amount of evidence that the applicant was in fact party to a contract or other binding legal obligation which:
(i) Deals specifically with the plant sought to be covered by the permit; and
(ii) Became binding prior to the date of the Federal Register notice of review of the status of the species or
proposed rulemaking to list the species as endangered, whichever is earlier;
(4) The severity of economic hardship which the contract or other binding legal obligation referred to in paragraph
(b)(3) of this section would cause if the permit were denied;
(5) Where applicable, the portion of the applicant's income which would be lost if the permit were denied, and the
relationship of that portion to the balance of his income.
(c) Permit conditions. In addition to the general conditions set forth in part 13 of this subchapter, every permit
issued under this section may be subject to any of the following special conditions:
(1) If requested, the permittee shall submit to the Director a written report of the activities authorized by the permit.
Such report must be postmarked by the date specified in the permit or otherwise requested by the Director.
(2) If requested, the permittee shall report to the Service's office designated in the permit the death, destruction or
loss of all living plants covered by the permit. Such report must be postmarked by the date specified in the permit
or otherwise requested by the Director.
(d) Duration of permit. The duration of a permit issued under this section shall be designated on the face of the
permit. No permit issued under this section shall be valid for more than one year from the date of a Federal
Register notice of review of the status of the species or proposed rulemaking to list the species as endangered,
whichever is earlier.
[44 FR 54060, Sept. 18, 1979]
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Subpart G—Threatened Plants
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§17.71 Prohibitions.
(a) Except as provided in a permit issued under this subpart, all of the provisions of §17.61 shall apply to
threatened species of plants that were added to the List of Endangered and Threatened Plants in §17.12(h) on or
prior to September 26, 2019, with the following exception: Seeds of cultivated specimens of species treated as
threatened shall be exempt from all the provisions of §17.61, provided that a statement that the seeds are of
“cultivated origin” accompanies the seeds or their container during the course of any activity otherwise subject to
the regulations in this subpart.
(b) In addition to any provisions of this part, any employee or agent of the Service or of a State conservation
agency that is operating a conservation program pursuant to the terms of a cooperative agreement with the
Service in accordance with section 6(c) of the Act, who is designated by that agency for such purposes, may,
when acting in the course of official duties, remove and reduce to possession from areas under Federal jurisdiction
those threatened species of plants that are covered by an approved cooperative agreement to carry out
conservation programs.
(c) Whenever a species-specific rule in §§17.73 through 17.78 applies to a threatened species, the speciesspecific rule will contain all the applicable prohibitions and exceptions.
[84 FR 44760, Aug. 27, 2019]
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§17.72 Permits—general.
Upon receipt of a complete application, the Director may issue a permit authorizing any activity otherwise
prohibited with regard to threatened plants. The permit shall be governed by the provisions of this section unless a
special rule applicable to the plant is provided in §§17.73 to 17.78. A permit issued under this section must be for
one of the following: scientific purposes, the enhancement of the propagation or survival of threatened species,
economic hardship, botanical or horticultural exhibition, educational purposes, or other activities consistent with
the purposes and policy of the Act. Such a permit may authorize a single transaction, a series of transactions, or a
number of activities over a specified period of time.
(a) Application requirements. A person wishing to get a permit for an activity prohibited by §17.71 submits an
application to conduct activities under this paragraph. For interstate commerce activities the seller gets the permit
for plants coming from cultivated stock and the buyer gets the permit if the plants are taken from the wild. The
Service provides Form 3-200 for the application or you may submit the general information and certification
required by §13.12(a) of this subchapter. Application requirements differ for permits issued for plants taken from
the wild (excluding seeds), seeds and cultivated plants, or herbarium specimens. You must attach the following
information and any other information requested by the Director.
(1) For activities involving plants obtained from the wild (excluding seeds), provide the following information:
(i) The scientific names of the plants sought to be covered by the permit;
(ii) The estimated number of specimens sought to be covered by the permit;
(iii) The year, country, and approximate place where taking occurred or will occur;
(iv) If the activities would involve removal and reduction to possession of a plant from an area under Federal
jurisdiction, the year, State, county or any other description such as place name, township, and range designation
that will precisely place the location where the proposed removal and reduction to possession will occur, the name
of the Federal entity having jurisdiction over the area and the name, title, address, and phone number of the
person in charge of the area.
(v) A brief description of the applicant's expertise and facilities as related to the proposed activity;
(vi) A justification of the activities sought to be authorized by the permit and the relationship of such activities to
scientific purposes, enhancing the propagation or survival of the species, or other objectives consistent with the
purposes and policy of the Act; and
(vii) A statement of the applicant's willingness to participate in a cooperative propagation program, and to maintain
or contribute data relating to such efforts.
(2) For activities involving seeds obtained from the wild and cultivated plants, provide the following information:
(i) The scientific names of the plants sought to be covered by the permit;
(ii) A statement of the applicant's willingness to participate in a cooperative propagation program, and to maintain
or contribute data relating to the success of such efforts; and
(iii) A justification of the activities sought to be authorized by the permit and the relationship of such activities to
scientific purposes, enhancing the propagation or survival of the species, or other objectives consistent with the
purposes and policy of the Act.
(iv) If the activities would involve removal and reduction to possession of seeds from an area under Federal
jurisdiction, the year, State, county, or any other description such as place name, township, and range designation
that will precisely place the location where the proposed removal and reduction to possession will occur, the name
of the Federal entity having jurisdiction over the area and the name, title, address, and phone number of the
person in charge of the area.
(3) For importation or exportation involving the non-commercial loan, exchange or donation of herbarium or other
preserved, dried or embedded museum specimens of all threatened species between scientists or scientific
institutions, provide the following information:
(i) The name and address of the institution or other facility where the plants sought to be covered by the permit will
be used or maintained; and
(ii) A justification of the activities sought to be authorized by the permit and the relationship of such activities to
scientific purposes, enhancing the propagation or survival of the species, or other objectives consistent with the
purposes and policy of the Act.
(4) When the activity applied for involves a species also regulated by the Convention on International Trade in
Endangered Species of Wild Fauna and Flora, additional requirements in part 23 of this subchapter must be met.
(b) Issuance criteria. Upon receiving an application completed in accordance with paragraph (a) of this section, the
Director will decide whether or not a permit should be issued. In making his decision, the Director shall consider, in
addition to the general criteria in §13.21(b) of this subchapter, the following factors:
(1) Whether the purpose for which the permit is requested will enhance the survival of the species in the wild;
(2) Whether the purpose for which the permit is requested will enhance the propagation of the species;
(3) The opinions or views of scientists or other persons or organizations having expertise concerning the plant or
other matters germane to the application; and
(4) Whether the expertise, facilities, or other resources available to the applicant appear adequate to successfully
accomplish the objectives stated in the application.
(c) Permit conditions. In addition to the general conditions set forth in part 13 of this subchapter, every permit
issued under this section shall be subject to the following special conditions:
(1) If requested, the permittee shall submit to the Director a written report of the activities authorized by the permit.
Such report must be postmarked by the date specified in the permit or otherwise requested by the Director.
(2) A copy of the permit or an identification label, which includes the scientific name, the permit number, and a
statement that the plant is of “wild orgin” or “cultivated origin” must accompany the plant or its container during the
course of any activity subject to these regulations, unless the specimens meet the special conditions referred to in
paragraph (c)(3) of this section.
(3) In the case of plants that are herbarium specimens, or other preserved, dried, or embedded museum
specimens to be imported or exported as a noncommercial loan exchange or donation between scientists or
scientific institutions, the names and addresses of the consignor and consignee must be on each package or
container. A description such as “herbarium specimens” and the code letters assigned by the Service to the
scientist or scientific institution must be entered on the Customs declaration form affixed to each package or
container. If the specimens are of taxa also regulated by the Convention on International Trade in Endangered
Species of Wild Fauna and Flora, specific information must be entered on the Customs declaration label affixed to
the outside of each shipping container or package. See part 23 of this subchapter for requirements for trade in
CITES specimens between registered scientific institutions.
(d) Duration of permit. The duration of a permit issued under this section shall be designated on the face of the
permit.
[42 FR 32380, June 24, 1977, as amended at 50 FR 39691, Sept. 30, 1985; 63 FR 52636, Oct. 1, 1998; 79 FR
30419, May 27, 2014]
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§§17.73-17.78 [Reserved]
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Subpart H—Experimental Populations
Source: 49 FR 33893, Aug. 27, 1984, unless otherwise noted.
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§17.80 Definitions.
(a) The term experimental population means an introduced and/or designated population (including any off-spring
arising solely therefrom) that has been so designated in accordance with the procedures of this subpart but only
when, and at such times as the population is wholly separate geographically from nonexperimental populations of
the same species. Where part of an experimental population overlaps with natural populations of the same species
on a particular occasion, but is wholly separate at other times, specimens of the experimental population will not
be recognized as such while in the area of overlap. That is, experimental status will only be recognized outside the
areas of overlap. Thus, such a population shall be treated as experimental only when the times of geographic
separation are reasonably predictable; e.g., fixed migration patterns, natural or man-made barriers. A population is
not treated as experimental if total separation will occur solely as a result of random and unpredictable events.
(b) The term essential experimental population means an experimental population whose loss would be likely to
appreciably reduce the likelihood of the survival of the species in the wild. All other experimental populations are to
be classified as nonessential.
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§17.81 Listing.
(a) The Secretary may designate as an experimental population a population of endangered or threatened species
that has been or will be released into suitable natural habitat outside the species' current natural range (but within
its probable historic range, absent a finding by the Director in the extreme case that the primary habitat of the
species has been unsuitably and irreversibly altered or destroyed), subject to the further conditions specified in this
section; provided, that all designations of experimental populations must proceed by regulation adopted in
accordance with 5 U.S.C. 553 and the requirements of this subpart.
(b) Before authorizing the release as an experimental population of any population (including eggs, propagules, or
individuals) of an endangered or threatened species, and before authorizing any necessary transportation to
conduct the release, the Secretary must find by regulation that such release will further the conservation of the
species. In making such a finding the Secretary shall utilize the best scientific and commercial data available to
consider:
(1) Any possible adverse effects on extant populations of a species as a result of removal of individuals, eggs, or
propagules for introduction elsewhere;
(2) The likelihood that any such experimental population will become established and survive in the foreseeable
future;
(3) The relative effects that establishment of an experimental population will have on the recovery of the species;
and
(4) The extent to which the introduced population may be affected by existing or anticipated Federal or State
actions or private activities within or adjacent to the experimental population area.
The Secretary may issue a permit under section 10(a)(1)(A) of the Act, if appropriate under the standards set out
in subsections 10(d) and (j) of the Act, to allow acts necessary for the establishment and maintenance of an
experimental population.
(c) Any regulation promulgated under paragraph (a) of this section shall provide:
(1) Appropriate means to identify the experimental population, including, but not limited to, its actual or proposed
location, actual or anticipated migration, number of specimens released or to be released, and other criteria
appropriate to identify the experimental population(s);
(2) A finding, based solely on the best scientific and commercial data available, and the supporting factual basis,
on whether the experimental population is, or is not, essential to the continued existence of the species in the wild;
(3) Management restrictions, protective measures, or other special management concerns of that population,
which may include but are not limited to, measures to isolate and/or contain the experimental population
designated in the regulation from natural populations; and
(4) A process for periodic review and evaluation of the success or failure of the release and the effect of the
release on the conservation and recovery of the species.
(d) The Fish and Wildlife Service shall consult with appropriate State fish and wildlife agencies, local governmental
entities, affected Federal agencies, and affected private landowners in developing and implementing experimental
population rules. When appropriate, a public meeting will be conducted with interested members of the public. Any
regulation promulgated pursuant to this section shall, to the maximum extent practicable, represent an agreement
between the Fish and Wildlife Service, the affected State and Federal agencies and persons holding any interest
in land which may be affected by the establishment of an experimental population.
(e) Any population of an endangered species or a threatened species determined by the Secretary to be an
experimental population in accordance with this subpart shall be identified by special rule in §§17.84-17.86 as
appropriate and separately listed in §17.11(h) (wildlife) or §17.12(h) (plants) as appropriate.
(f) The Secretary may designate critical habitat as defined in section (3)(5)(A) of the Act for an essential
experimental population as determined pursuant to paragraph (c)(2) of this section. Any designation of critical
habitat for an essential experimental population will be made in accordance with section 4 of the Act. No
designation of critical habitat will be made for nonessential populations. In those situations where a portion or all of
an essential experimental population overlaps with a natural population of the species during certain periods of the
year, no critical habitat shall be designated for the area of overlap unless implemented as a revision to critical
habitat of the natural population for reasons unrelated to the overlap itself.
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§17.82 Prohibitions.
Any population determined by the Secretary to be an experimental population shall be treated as if it were listed as
a threatened species for purposes of establishing protective regulations under section 4(d) of the Act with respect
to such population. The Special rules (protective regulations) adopted for an experimental population under §17.81
will contain applicable prohibitions, as appropriate, and exceptions for that population.
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§17.83 Interagency cooperation.
(a) Any experimental population designated for a listed species (1) determined pursuant to §17.81(c)(2) of this
subpart not to be essential to the survival of that species and (2) not occurring within the National Park System or
the National Wildlife Refuge System, shall be treated for purposes of section 7 (other than subsection (a)(1)
thereof) as a species proposed to be listed under the Act as a threatened species.
(b) Any experimental population designated for a listed species that either (1) has been determined pursuant to
§17.81(c)(2) of this subpart to be essential to the survival of that species, of (2) occurs within the National Park
System or the National Wildlife Refuge System as now or hereafter constituted, shall be treated for purposes of
section 7 of the Act as a threatened species. Notwithstanding the foregoing, any biological opinion prepared
pursuant to section 7(b) of the Act and any agency determination made pursuant to section 7(a) of the Act shall
consider any experimental and nonexperimental populations to constitute a single listed species for the purposes
of conducting the analyses under such sections.
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§17.84 Special rules—vertebrates.
(a) [Reserved]
(b) Colorado squawfish (Ptychocheilus lucius) and woundfin (Plagopterus argentissimus). (1) The Colorado
squawfish and woundfin populations identified in paragraph (b)(6) of this section, are experimental, nonessential
populations.
(2) No person shall take the species, except in accordance with applicable State or Tribal fish and wildlife
conservation laws and regulations in the following instances:
(i) For educational purposes, scientific purposes, the enhancement of propagation or survival of the species,
zoological exhibition, and other conservation purposes consistent with the Act; or
(ii) Incidental to otherwise lawful activities, provided that the individual fish taken, if still alive, is immediately
returned to its habitat.
(3) Any violation of applicable State or Tribal fish and wildlife conservation laws or regulations with respect to the
taking of this species (other than incidental taking as described in paragraph (b)(2)(ii) of this section) will also be a
violation of the Endangered Species Act.
(4) No person shall possess, sell, deliver, carry, transport, ship, import, or export, by any means whatsoever, any
such species taken in violation of these regulations or in violation of applicable State or Tribal fish and wildlife laws
or regulations.
(5) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (b) (2) through (4) of this section.
(6) All of the sites for reintroduction of Colorado squawfish and woundfin are totally isolated from existing
populations of these species. The nearest population of Colorado squawfish is above Lake Powell in the Green
and Colorado Rivers, an upstream distance of at least 800 miles including 6 mainstream dams, and 200 miles of
dry riverbed. Woundfin are similarly isolated (450 miles distant, 200 miles of dry streambed and 5 mainstream
dams). All reintroduction sites are within the probable historic range of these species and are as follows:
Colorado Squawfish
(i) Arizona: Gila County. Salt River from Roosevelt Dam upstream to U.S Highway 60 bridge.
(ii) Arizona: Gila and Yavapai Counties. Verde River from Horseshoe Dam upstream to Perkinsville.
The lower segments of large streams which flow into these two sections of river may, from time to time, be
inhabited by Colorado squawfish. Downstream movement of squawfish in these areas will be restricted by dams
and upstream movement is limited by lack of suitable habitat.
Woundfin
(i) Arizona: Gila and Yavapai Counties. Verde River from backwaters of Horseshoe Reservoir upstream to
Perkinsville.
(ii) Arizona: Graham and Greenlee Counties. Gila River from backwaters of San Carlos Reservoir upstream to
Arizona/New Mexico State line.
(iii) Arizona: Greenlee County. San Francisco River from its junction with the Gila River upstream to the
Arizona/New Mexico State line.
(iv) Arizona: Gila County. Tonto Creek, from Punkin Center upstream to Gisela.
(v) Arizona: Yavapai County. Hassayampa River, from Red Cliff upstream to Wagoner.
The movement of woundfin beyond these areas will be limited to the lower portion of larger tributaries where
suitable habitat exists. Downstream movement is limited by dams, reservoirs, and dry streambed. Upstream
movement from these areas is restricted due to the absence of habitat. Upstream areas are too cold and the
gradient is too steep to support populations of woundfin.
(7) The reintroduced populations will be checked annually to determine their condition. A seining survey will be
used to determine population expansion or contraction, reproduction success, and general health condition of the
fish.
(c) Red wolf (Canis rufus). (1) The red wolf populations identified in paragraphs (c)(9)(i) and (c)(9)(ii) of this section
are nonessential experimental populations.
(2) No person may take this species, except as provided in paragraphs (c)(3) through (5) and (10) of this section.
(3) Any person with a valid permit issued by the Service under §17.32 may take red wolves for educational
purposes, scientific purposes, the enhancement of propagation or survival of the species, zoological exhibition,
and other conservation purposes consistent with the Act and in accordance with applicable State fish and wildlife
conservation laws and regulations;
(4)(i) Any person may take red wolves found on private land in the areas defined in paragraphs (c)(9) (i) and (ii) of
this section, Provided that such taking is not intentional or willful, or is in defense of that person's own life or the
lives of others; and that such taking is reported within 24 hours to the refuge manager (for the red wolf population
defined in paragraph (c)(9)(i) of this section), the Park superintendent (for the red wolf population defined in
paragraph (c)(9)(ii) of this section), or the State wildlife enforcement officer for investigation.
(ii) Any person may take red wolves found on lands owned or managed by Federal, State, or local government
agencies in the areas defined in paragraphs (c)(9) (i) and (ii) of this section, Provided that such taking is incidental
to lawful activities, is unavoidable, unintentional, and not exhibiting a lack of reasonable due care, or is in defense
of that person's own life or the lives of others, and that such taking is reported within 24 hours to the refuge
manager (for the red wolf population defined in paragraph (c)(9)(i) of this section), the Park superintendent (for the
red wolf population defined in paragraph (c)(9)(ii) of this section), or the State wildlife enforcement officer for
investigation.
(iii) Any private landowner, or any other individual having his or her permission, may take red wolves found on his
or her property in the areas defined in paragraphs (c)(9) (i) and (ii) of this section when the wolves are in the act of
killing livestock or pets, Provided that freshly wounded or killed livestock or pets are evident and that all such
taking shall be reported within 24 hours to the refuge manager (for the red wolf population defined in paragraph (c)
(9)(i) of this section), the Park superintendent (for the red wolf population defined in paragraph (c)(9)(ii) of this
section), or the State wildlife enforcement officer for investigation.
(iv) Any private landowner, or any other individual having his or her permission, may harass red wolves found on
his or her property in the areas defined in paragraphs (c)(9) (i) and (ii) of this section, Provided that all such
harassment is by methods that are not lethal or physically injurious to the red wolf and is reported within 24 hours
to the refuge manager (for the red wolf population defined in paragraph (c)(9)(i) of this section), the Park
superintendent (for the red wolf population defined in paragraph (c)(9)(ii) of this section), or the State wildlife
enforcement officer, as noted in paragraph (c)(6) of this section for investigation.
(v) Any private landowner may take red wolves found on his or her property in the areas defined in paragraphs (c)
(9) (i) and (ii) of this section after efforts by project personnel to capture such animals have been
abandoned, Provided that the Service project leader or biologist has approved such actions in writing and all such
taking shall be reported within 24 hours to the Service project leader or biologist, the refuge manager (for the red
wolf population defined in paragraph (c)(9)(i) of this section), the Park superintendent (for the red wolf population
defined in paragraph (c)(9)(ii) of this section), or the State wildlife enforcement officer for investigation.
(vi) The provisions of paragraphs (4) (i) through (v) of this section apply to red wolves found in areas outside the
areas defined in paragraphs (c)(9) (i) and (ii) of this section, with the exception that reporting of taking or
harassment to the refuge manager, Park superintendent, or State wildlife enforcement officer, while encouraged, is
not required.
(5) Any employee or agent of the Service or State conservation agency who is designated for such purposes,
when acting in the course of official duties, may take a red wolf if such action is necessary to:
(i) Aid a sick, injured, or orphaned specimen;
(ii) Dispose of a dead specimen, or salvage a dead specimen which may be useful for scientific study;
(iii) Take an animal that constitutes a demonstrable but non-immediate threat to human safety or that is
responsible for depredations to lawfully present domestic animals or other personal property, if it has not been
possible to otherwise eliminate such depredation or loss of personal property, Provided That such taking must be
done in a humane manner, and may involve killing or injuring the animal only if it has not been possible to
eliminate such threat by live capturing and releasing the specimen unharmed on the refuge or Park;
(iv) Move an animal for genetic purposes.
(6) Any taking pursuant to paragraphs (c) (3) through (5) of this section must be immediately reported to either the
Refuge Manager, Alligator River National Wildlife Refuge, Manteo, North Carolina, telephone 919/473-1131, or the
Superintendent, Great Smoky Mountains National Park, Gatlinburg, Tennessee, telephone 615/436-1294. Either of
these persons will determine disposition of any live or dead specimens.
(7) No person shall possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever, any
such species taken in violation of these regulations or in violation of applicable State fish and wildlife laws or
regulations or the Endangered Species Act.
(8) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (c) (2) through (7) of this section.
(9)(i) The Alligator River reintroduction site is within the historic range of the species in North Carolina, in Dare,
Hyde, Tyrrell, and Washington Counties; because of its proximity and potential conservation value, Beaufort
County is also included in the experimental population designation.
(ii) The red wolf also historically occurred on lands that now comprise the Great Smoky Mountains National Park.
The Park encompasses properties within Haywood and Swain Counties in North Carolina, and Blount, Cocke, and
Sevier Counties in Tennessee. Graham, Jackson, and Madison Counties in North Carolina, and Monroe County in
Tennessee, are also included in the experimental designation because of the close proximity of these counties to
the Park boundary.
(iii) Except for the three island propagation projects and these small reintroduced populations, the red wolf is
extirpated from the wild. Therefore, there are no other extant populations with which the refuge or Park
experimental populations could come into contact.
(10) The reintroduced populations will be monitored closely for the duration of the project, generally using radio
telemetry as appropriate. All animals released or captured will be vaccinated against diseases prevalent in canids
prior to release. Any animal that is determined to be in need of special care or that moves onto lands where the
landowner requests their removal will be recaptured, if possible, by Service and/or Park Service and/or designated
State wildlife agency personnel and will be given appropriate care. Such animals will be released back into the wild
as soon as possible, unless physical or behavioral problems make it necessary to return the animals to a captivebreeding facility.
(11) The status of the Alligator River National Wildlife Refuge project will be reevaluated by October 1, 1992, to
determine future management status and needs. This review will take into account the reproductive success of the
mated pairs, movement patterns of individual animals, food habits, and overall health of the population. The
duration of the first phase of the Park project is estimated to be 10 to 12 months. After that period, an assessment
of the reintroduction potential of the Park for red wolves will be made. If a second phase of reintroduction is
attempted, the duration of that phase will be better defined during the assessment. However, it is presently thought
that a second phase would last for 3 years, after which time the red wolf would be treated as a resident species
within the Park. Throughout these periods, the experimental and nonessential designation of the animals will
remain in effect.
(d) Topeka shiner (Notropis topeka).
(1) Where is the Topeka shiner designated as a nonessential experimental population (NEP)? (i) The NEP area for
the Topeka shiner is within the species' historical range and includes those waters within the Missouri counties of
Adair, Gentry, Harrison, Putnam, Sullivan, and Worth identified below in paragraph (d)(5) of this section.
(ii) The Topeka shiner is not known to currently exist in Adair, Gentry, Putnam, Sullivan, and Worth Counties in
Missouri, or in those portions of Harrison County, Missouri, where the NEP is being designated. Based on its
habitat requirements and potential predation by other fish predators, we do not expect this species to become
established outside this NEP area, although there is a remote chance it may.
(iii) We will not change the NEP designations to “essential experimental,” “threatened,” or “endangered” within the
NEP area without a public rulemaking. Additionally, we will not designate critical habitat for this NEP, as provided
by 16 U.S.C. 1539(j)(2)(C)(ii).
(2) What activities are not allowed in the NEP area? (i) Except as expressly allowed in paragraph (d)(3) of this
section, all the prohibitions of §17.21 apply to the Topeka shiner NEP.
(ii) Any manner of take not described under paragraph (d)(3) of this section is prohibited in the NEP area.
(iii) You may not possess, sell, deliver, carry, transport, ship, import, or export by any means, Topeka shiners, or
parts thereof, that are taken or possessed in violation of paragraph (d)(3) of this section or in violation of the
applicable State fish and wildlife laws or regulations or the Act.
(iv) You may not attempt to commit, solicit another to commit, or cause to be committed any offense defined in
paragraph (d)(2)(iii) of this section.
(3) What take is allowed in the NEP area? Take of this species that is incidental to an otherwise legal activity, such
as agriculture, forestry and wildlife management, land development, recreation, and other activities, is allowed
provided that the activity is not in violation of any applicable State fish and wildlife laws or regulations.
(4) How will the effectiveness of these reintroductions be monitored? We will monitor reintroduction efforts to
assess changes in distribution within each watershed by sampling ponds and streams where releases occur for 10
years after reintroduction. Streams will be sampled annually, and ponds will be sampled annually for the first 3
years and biennially thereafter.
(5) Note: Map of the NEP areas [Big Muddy Creek (Gentry, Harrison, and Worth Counties), Little Creek (Harrison
County), and Spring Creek (Adair, Putnam, and Sullivan Counties)] for the Topeka shiner, follows:
eCFR graphic er17jy13.000.gif
View or download PDF
(6) Note: Map of the NEP area for the Topeka shiner in Little Creek watershed, Harrison County, follows:
eCFR graphic er17jy13.001.gif
View or download PDF
(7) Note: Map of the NEP area for the Topeka shiner in Big Muddy Creek watershed, Gentry, Harrison, and Worth
Counties, follows:
eCFR graphic er17jy13.002.gif
View or download PDF
(8) Note: Map of the NEP area for the Topeka shiner in Spring Creek watershed, Adair, Putnam, and Sullivan
Counties, follows:
eCFR graphic er17jy13.003.gif
View or download PDF
(e) Yellowfin madtom (Noturus flavipinnis). (1) Where is the yellowfin madtom designated as a nonessential
experimental population (NEP)? We have designated three populations of this species as NEPs: the North Fork
Holston River Watershed NEP, the Tellico River NEP, and the French Broad River and Holston River NEP.
(i) The North Fork Holston River Watershed NEP area is within the species' historic range and is defined as
follows: The North Fork Holston River watershed, Washington, Smyth, and Scott Counties, Virginia; South Fork
Holston River watershed upstream to Ft. Patrick Henry Dam, Sullivan County, Tennessee; and the Holston River
from the confluence of the North and South Forks downstream to the John Sevier Detention Lake Dam, Hawkins
County, Tennessee. This site is totally isolated from existing populations of this species by large Tennessee River
tributaries and reservoirs. As the species is not known to inhabit reservoirs and because individuals of the species
are not likely to move 100 river miles through these large reservoirs, the possibility that this population could come
in contact with extant wild populations is unlikely.
(ii) The Tellico River NEP area is within the species' historic range and is defined as follows: The Tellico River,
between the backwaters of the Tellico Reservoir (approximately Tellico River mile 19 (30.4 kilometers) and Tellico
River mile 33 (52.8 kilometers), near the Tellico Ranger Station, Monroe County, Tennessee. This species is not
currently known to exist in the Tellico River or its tributaries. Based on its habitat requirements, we do not expect
this species to become established outside this NEP area. However, if individuals of this population move
upstream or downstream or into tributaries outside the designated NEP area, we would presume that they came
from the reintroduced population. We would then amend this regulation to enlarge the boundaries of the NEP area
to include the entire range of the expanded population.
(iii) The French Broad River and Holston River NEP area is within the species' historic range and is defined as
follows: the French Broad River, Knox and Sevier Counties, Tennessee, from the base of Douglas Dam (river mile
(RM) 32.3 (51.7 km)) downstream to the confluence with the Holston River; then up the Holston River, Knox,
Grainger, and Jefferson Counties, Tennessee, to the base of Cherokee Dam (RM 52.3 (83.7 km)); and the lower 5
RM (8 km) of all tributaries that enter these river reaches. This species is not known to exist in any of the
tributaries to the free-flowing reaches of the French Broad River below Douglas Dam, Knox and Sevier Counties,
Tennessee, or of the Holston River below the Cherokee Dam, Knox, Grainger, and Jefferson Counties, Tennessee.
Based on its habitat requirements, we do not expect this species to become established outside this NEP area.
However, if individuals of this population move upstream or downstream or into tributaries outside the designated
NEP area, we would presume that they came from the reintroduced population. We would then amend this
regulation to enlarge the boundaries of the NEP area to include the entire range of the expanded population.
(iv) We do not intend to change the NEP designations to “essential experimental,” “threatened,” or “endangered”
within the NEP areas. Additionally, we will not designate critical habitat for these NEPs, as provided by 16 U.S.C.
1539(j)(2)(C)(ii).
(2) What activities are not allowed in the NEP areas? (i) Except as expressly allowed in paragraph (e)(3) of this
section, all the prohibitions of §17.31(a) and (b) apply to the yellowfin madtom.
(ii) Any manner of take not described under paragraph (e)(3) of this section is prohibited in the NEP area. We may
refer unauthorized take of this species to the appropriate authorities for prosecution.
(iii) You may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any of the
identified fishes, or parts thereof, that are taken or possessed in violation of paragraph (e)(2) of this section or in
violation of the applicable State fish and wildlife laws or regulations or the Act.
(iv) You may not attempt to commit, solicit another to commit, or cause to be committed any offense defined in
paragraph (e)(2) of this section.
(3) What take is allowed in the NEP area? Take of this species that is accidental and incidental to an otherwise
legal activity, such as recreation (e.g., fishing, boating, wading, trapping, or swimming), forestry, agriculture, and
other activities that are in accordance with Federal, State, and local laws and regulations, is allowed.
(4) How will the effectiveness of these reintroductions be monitored? We will prepare periodic progress reports and
fully evaluate these reintroduction efforts after 5 and 10 years to determine whether to continue or terminate the
reintroduction efforts.
(5) Note: Map of the NEP area for the yellowfin madtom in the Tellico River, Tennessee, appears immediately
following paragraph (m)(5) of this section.
(6) Note: Map of the NEP area for the yellowfin madtom in the French Broad River and Holston River, Tennessee,
appears immediately following paragraph (m)(7) of this section.
(f) Guam rail (Rallus owstoni). (1) The Guam rail population identified in paragraph (f)(7) of this section is a
nonessential experimental population.
(2) No person shall take this species, except:
(i) In accordance with a valid permit issued by the Service under §17.32 for educational purposes, scientific
purposes, the enhancement of propagation or survival of the species, zoological exhibition, and other conservation
purposes consistent with the Act; or
(ii) As authorized by the laws and regulations of the Commonwealth of the Northern Mariana Islands, after the
Service has made the determination that the experimental population has become well established and occupies
all suitable habitat island-wide.
(3) Any employee of the Service, the Commonwealth of the Northern Mariana Islands Division of Fish and Wildlife,
or the Guam Division of Aquatic and Wildlife Resources who is designated for such purposes, may, when acting in
the course of official duties, take a Guam rail without a permit if such action is necessary to:
(i) Aid a sick, injured, or orphaned specimen;
(ii) Dispose of a dead specimen;
(iii) Salvage a dead specimen that may be useful for scientific study; or
(iv) Take an animal that is responsible for depredations to personal property if it has not been possible to otherwise
eliminate such depredations and/or loss of personal property, provided that such taking must be done in a humane
manner and may involve injuring or killing the bird only if it has not been possible to eliminate depredations by live
capturing and releasing the specimen unharmed in other suitable habitats.
(4) Any violation of applicable commonwealth of the Northern Mariana Islands fish and wildlife conservation laws
or regulations with respect to the taking of this species (other than taking as described in paragraph (f)(2)(ii) of this
section) will also be a violation of the Endangered Species Act.
(5) No person shall possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever, any
such species taken in violation of these regulations or in violation of applicable Commonwealth of the Northern
Mariana Islands fish and wildlife laws or regulations or the Endangered Species Act.
(6) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (f) (2) through (5) of this section.
(7) The sites for introduction of Guam rails on Rota, Commonwealth of the Northern Mariana Islands, are on an
island separated from Guam by 50 kilometers of ocean. The last known observation of an individual of this species
occurred near the northern tip of Guam, which is closest to the island of Rota. No intermingling of these
populations will occur since this species has been extirpated in the wild on Guam. The Rota release sites are of
necessity outside the historic range of the Guam rail, as described in this regulation, because its primary range
has been unsuitably and irreversibly destroyed by the brown tree snake.
(8) The nonessential experimental population on Rota will be checked periodically by staff of the Commonwealth
of the Northern Mariana Islands Division of Fish and Wildlife and cooperating staff from the University of
Tennessee to determine dispersal patterns, mortality, and reproductive success. The overall success of the
releases and general health of the population will also be assessed.
(g) Black-footed ferret (Mustela nigripes). (1) The black-footed ferret populations identified in paragraphs (g)(9)(i)
through (viii) of this section are nonessential experimental populations. We will manage each of these populations,
and each reintroduction site within the Wyoming Experimental Population Area, in accordance with their respective
management plans.
(2) No person may take this species in the wild in the experimental population area, except as provided in
paragraphs (g)(3), (4), (5), and (10) of this section.
(3) Any person with a valid permit issued by the U.S. Fish and Wildlife Service (Service) under section 17.32 may
take black-footed ferrets in the wild in the experimental population areas.
(4) Any employee or agent of the Service or appropriate State wildlife agency designated for such purposes, acting
in the course of official duties, may take a black-footed ferret in the wild in the experimental population areas if
such action is necessary:
(i) For scientific purposes;
(ii) To relocate a ferret to avoid conflict with human activities;
(iii) To relocate a ferret that has moved outside the Little Snake Black-footed Ferret Management Area/Coyote
Basin Primary Management Zone or the Rosebud Sioux Reservation Experimental Population Area when that
relocation is necessary to protect the ferret or is requested by an affected landowner or land manager, or whose
removal is requested pursuant to paragraph (g)(12) of this section.
(iv) To relocate ferrets within the experimental population area to improve ferret survival and recovery prospects;
(v) To relocate ferrets from the experimental population areas into other ferret reintroduction areas or captivity;
(vi) To aid a sick, injured, or orphaned animal; or
(vii) To salvage a dead specimen for scientific purposes.
(5) A person may take a ferret in the wild within the experimental population areas, provided such take is incidental
to and not the purpose of, the carrying out of an otherwise lawful activity and if such ferret injury or mortality was
unavoidable, unintentional, and did not result from negligent conduct. Such conduct is not considered intentional or
“knowing take” for the purposes of this regulation, and the Service will not take legal action for such conduct.
However, we will refer cases of knowing take to the appropriate authorities for prosecution.
(6) You must report any taking pursuant to paragraphs (g)(3), (4)(vi) and (vii), and (5) of this section to the
appropriate Service Field Supervisor, who will determine the disposition of any live or dead specimens.
(i) Report such taking in Wyoming, including the Shirley Basin/Medicine Bow experimental population area, to the
Field Supervisor, Ecological Services, Fish and Wildlife Service, Cheyenne, Wyoming (telephone: 307/772-2374).
(ii) Report such taking in the Conata Basin/Badlands experimental population area to the Field Supervisor,
Ecological Services, Fish and Wildlife Service, Pierre, South Dakota (telephone: 605/224-8693).
(iii) Report such taking in the northcentral Montana experimental population area to the Field Supervisor,
Ecological Services, Fish and Wildlife Service, Helena, Montana (telephone: 406/449-5225).
(iv) Report such taking in the Aubrey Valley experimental population area to the Field Supervisor, Ecological
Services, Fish and Wildlife Service, Phoenix, Arizona (telephone: 602/640-2720).
(v) Report such taking in the northwestern Colorado/northeastern Utah experimental population area to the
appropriate Field Supervisor, Ecological Services, U.S. Fish and Wildlife Service, Lakewood, Colorado (telephone:
303/275-2370), or Salt Lake City, Utah (telephone: 801/524-5001).
(vi) Report such taking in the Cheyenne River Sioux Tribe Experimental Population Area to the Field Supervisor,
Ecological Services, U.S. Fish and Wildlife Service, Pierre, South Dakota (telephone 605/224-8693).
(vii) Report such taking in the Rosebud Sioux Reservation Experimental Population Area to the Field Supervisor,
Ecological Services, U.S. Fish and Wildlife Service, Pierre, South Dakota (telephone 605/224-8693).
(7) No person shall possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever, any
ferret or part thereof from the experimental populations taken in violation of these regulations or in violation of
applicable State fish and wildlife laws or regulations or the Endangered Species Act.
(8) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to commit, any offense
defined in paragraphs (g)(2) and (7) of this section.
(9) The sites for reintroduction of black-footed ferrets are within the historical range of the species.
(i) We consider the Shirley Basin/Medicine Bow Management Area on the attached map of Wyoming to be the
core recovery area for this species in southeastern Wyoming. The boundaries of the nonessential experimental
population are that part of Wyoming south and east of the North Platte River within Natrona, Carbon, and Albany
Counties (see Wyoming map). All marked ferrets found in the wild within these boundaries prior to the first
breeding season following the first year of releases constituted the nonessential experimental population during
this period. All ferrets found in the wild within these boundaries during and after the first breeding season following
the first year of releases comprise the nonessential experimental population, thereafter.
(ii) We consider the Conata Basin/Badlands Reintroduction Area on the attached map for South Dakota to be the
core recovery area for this species in southwestern South Dakota. The boundaries of the nonessential
experimental population area occur north of State Highway 44 and BIA Highway 2 east of the Cheyenne River and
BIA Highway 41, south of I-90, and west of State Highway 73 within Pennington, Shannon, and Jackson Counties,
South Dakota. Any black-footed ferret found in the wild within these boundaries is part of the nonessential
experimental population after the first breeding season following the first year of releases of black-footed ferret in
the Reintroduction Area. A black-footed ferret occurring outside the experimental population area in South Dakota
is considered as endangered but may be captured for genetic testing. We will dispose of the captured animal in
one of the following ways if necessary:
(A) We may return an animal genetically related to the experimental population to the Reintroduction Area or to a
captive facility.
(B) Under an existing contingency plan, we will use up to nine black-footed ferrets genetically unrelated to the
experimental population in the captive-breeding program. If a landowner outside the experimental population area
wishes to retain black-footed ferrets on his property, we will develop a conservation agreement or easement with
the landowner.
(iii) We consider the Northcentral Montana Reintroduction Area shown on the attached map for Montana to be the
core recovery area for this species in northcentral Montana. The boundaries of the nonessential experimental
population are those parts of Phillips and Blaine Counties, Montana, described as the area bounded on the north
beginning at the northwest corner of the Fort Belknap Indian Reservation on the Milk River; east following the Milk
River to the east Phillips County line; then south along said line to the Missouri River; then west along the Missouri
River to the west boundary of Phillips County; then north along said county line to the west boundary of Fort
Belknap Indian Reservation; then further north along said boundary to the point of origin at the Milk River. All
marked ferrets found in the wild within these boundaries prior to the first breeding season following the first year of
releases constituted the nonessential experimental population during this period. All ferrets found in the wild within
these boundaries during and after the first breeding season following the first year of releases comprise the
nonessential experimental population thereafter. A black-footed ferret occurring outside the experimental area in
Montana is initially considered as endangered but may be captured for genetic testing. We will dispose of the
captured animal in one of the following ways if necessary:
(A) We may return an animal genetically related to the experimental population to the reintroduction area or to a
captive facility.
(B) Under an existing contingency plan, we will use up to nine black-footed ferrets genetically unrelated to the
experimental population in the captive-breeding program. If a landowner outside the experimental population area
wishes to retain black-footed ferrets on his property, we will develop a conservation agreement or easement with
the landowner.
(iv) We consider the Aubrey Valley Experimental Population Area shown on the attached map for Arizona to be the
core recovery area for this species in northwestern Arizona. The boundary of the nonessential experimental
population area is those parts of Coconino, Mohave, and Yavapai Counties that include the Aubrey Valley west of
the Aubrey Cliffs, starting from Chino Point, north along the crest of the Aubrey cliffs to the Supai Road (State
Route 18), southwest along the Supai Road to Township 26 North, then west to Range 11 West, then south to the
Hualapai Indian Reservation boundary, then east and northeast along the Hualapai Indian Reservation boundary
to U.S. Highway Route 66; then southeast along Route 66 for approximately 6 km (2.3 miles) to a point
intercepting the east boundary of section 27, Township 25 North, Range 9 West; then south along a line to where
the Atchison-Topeka Railroad enters Yampa Divide Canyon; then southeast along the Atchison-Topeka Railroad
alignment to the intersection of the Range 9 West/Range 8 West boundary; then south to the SE corner of section
12, Township 24 North, Range 9 West; then southeast to SE corner section 20, Township 24 West, Range 8 West;
then south to the SE corner section 29, Township 24 North, Range 8 West; then southeast to the half section point
on the east boundary line of section 33, Township 24 North, Range 8 West; then northeast to the SE corner of
section 27, Township 24 North, Range 8 West; then southeast to the SE corner Section 35, Township 24 North,
Range 8 West; then southeast to the half section point on the east boundary line of section 12, Township 23 North,
Range 8 West; then southeast to the SE corner of section 8, Township 23 North, Range 7 West; then southeast to
the SE corner of section 16, Township 23 North, Range 7 West; then east to the half section point of the north
boundary line of section 14, Township 23 North, Range 7 West; then south to the half section point on the north
boundary line of section 26, Township 23 North, Range 7 West; then east along section line to route 66; then
southeast along route 66 to the point of origin at Chino Point. Any black-footed ferrets found in the wild within
these boundaries is part of the nonessential experimental population after the first breeding season following the
first year of releases of ferrets into the reintroduction area. A black-footed ferret occurring outside the experimental
area in Arizona is initially considered as endangered but may be captured for genetic testing. We will dispose of
the captured animal in one of the following ways if necessary:
(A) We may return an animal genetically related to the experimental population to the reintroduction area or to a
captive facility. If a landowner outside the experimental population area wishes to retain black-footed ferrets on his
property, we will develop a conservation agreement or easement with the landowner.
(B) Under an existing contingency plan, we will use up to nine black-footed ferrets genetically unrelated to the
experimental population in the captive-breeding program. If a landowner outside the experimental population area
wishes to retain black-footed ferrets on his property, we will develop a conservation agreement or easement with
the landowner.
(v) We consider the Little Snake Black-footed Ferret Management Area in Colorado and the Coyote Basin Blackfooted Ferret Primary Management Zone in Utah as the initial recovery sites for this species within the
Northwestern Colorado/Northeastern Utah Experimental Population Area (see Colorado/Utah map). The
boundaries of the nonessential Experimental Population Area will be all of Moffat and Rio Blanco Counties in
Colorado west of Colorado State Highway 13; all of Uintah and Duchesne Counties in Utah; and in Sweetwater
County, Wyoming, the line between Range 96 and 97 West (eastern edge), Range 102 and 103 West (western
edge), and Township 14 and 15 North (northern edge). All marked ferrets found in the wild within these boundaries
prior to the first breeding season following the first year of release will constitute the nonessential experimental
population during this period. All ferrets found in the wild within these boundaries during and after the first breeding
season following the first year of releases of ferrets into the reintroduction area will comprise the nonessential
experimental population thereafter. A black-footed ferret occurring outside the Experimental Population Area is
initially considered as endangered but may be captured for genetic testing. We will dispose of the captured animal
in one of the following ways if necessary:
(A) We may return an animal genetically related to the experimental population to the Reintroduction Area or to a
captive facility.
(B) Under an existing contingency plan, we will use up to nine black-footed ferrets genetically unrelated to the
experimental population in the captive-breeding program. If a landowner outside the experimental population area
wishes to retain black-footed ferrets on his property, we will develop a conservation agreement or easement with
the landowner.
(vi) The Cheyenne River Sioux Tribe Reintroduction Area is shown on the map of north-central South Dakota at
the end of paragraph (g) of this section. The boundaries of the nonessential experimental population area are the
exterior boundaries of the Cheyenne River Sioux Reservation which includes all of Dewey and Ziebach Counties,
South Dakota. Any black-footed ferret found in the wild within these counties will be considered part of the
nonessential experimental population after the first breeding season following the first year of black-footed ferret
release. A black-footed ferret occurring outside the Experimental Population Area in north-central South Dakota
would initially be considered as endangered but may be captured for genetic testing. When a ferret is found
outside the Experimental Population Area, the following may occur:
(A) If an animal is genetically determined to have originated from the experimental population, we may return it to
the reintroduction area or to a captive-breeding facility.
(B) If an animal is determined to be genetically unrelated to the experimental population, we will place it in captivity
under an existing contingency plan. Up to nine black-footed ferrets may be taken for use in the captive-breeding
program.
(vii) The Rosebud Sioux Reservation Experimental Population Area is shown on the map of south-central South
Dakota at the end of paragraph (g) of this section. The boundaries of the nonessential experimental population
area include all of Gregory, Mellette, Todd, and Tripp Counties in South Dakota. Any black-footed ferret found
within these four counties will be considered part of the nonessential experimental population after the first
breeding season following the first year of black-footed ferret release. A black-footed ferret occurring outside the
nonessential experimental population area in south-central South Dakota will initially be considered as endangered
but may be captured for genetic testing. If necessary, disposition of the captured animal may occur in the following
ways:
(A) If an animal is genetically determined to have originated from the experimental population, we may return it to
the reintroduction area or to a captive-breeding facility.
(B) If an animal is determined to be genetically unrelated to the experimental population, we will place it in captivity
under an existing contingency plan. Up to nine black-footed ferrets may be taken for use in the captive-breeding
program.
(viii) The Wyoming Experimental Population Area encompasses most of the State of Wyoming. The boundaries of
the nonessential experimental population include all areas in the State of Wyoming outside of the Shirley
Basin/Medicine Bow Management Area (see paragraph (g)(9)(i) of this section) and the small portion of Wyoming
included as part of the Northwestern Colorado/Northeastern Utah Experimental Population Area (see paragraph
(g)(9)(v) of this section). Collectively, however, these three 10(j) areas cover the entire State of Wyoming. Any
black-footed ferret found within the Wyoming NEP Experimental Population Area will be considered part of a
nonessential experimental population. A black-footed ferret that disperses beyond the boundaries of the
nonessential experimental population area takes on the status of that area (endangered, unless within another
nonessential experimental population area). Such animals may be captured for genetic testing and relocation. If
necessary, disposition of the captured animal may occur in the following ways:
(A) If an animal is genetically determined to have originated from the experimental population, we may return it to
the reintroduction area or to a captive-breeding facility.
(B) If an animal is determined to be genetically unrelated to the experimental population, we will place it in captivity
under an existing contingency plan.
(10) Monitoring the reintroduced populations will occur continually during the life of the project, including the use of
radio telemetry and other remote sensing devices, as appropriate. Vaccination of all released animals will occur
prior to release, as appropriate, to prevent diseases prevalent in mustelids. Any animal that is sick, injured, or
otherwise in need of special care may be captured by authorized personnel of the Service or appropriate State
wildlife agency or their agents and given appropriate care. Such an animal may be released back to its appropriate
reintroduction area or another authorized site as soon as possible, unless physical or behavioral problems make it
necessary to return the animal to captivity.
(11) We will reevaluate the status of the experimental population within the first five years after the first year of
release of black-footed ferrets to determine future management needs. This review will take into account the
reproductive success and movement patterns of the individuals released into the area, as well as the overall health
of the experimental population and the prairie dog ecosystem in the above described areas. We will propose
reclassification of the black-footed ferret when we meet the appropriate recovery objectives for the species.
(12) We will not include a reevaluation of the “nonessential experimental” designation for these populations during
our review of the initial five year reintroduction program. We do not foresee any likely situation justifying alteration
of the nonessential experimental status of these populations. Should any such alteration prove necessary and it
results in a substantial modification to black-footed ferret management on non-Federal lands, any private
landowner who consented to the introduction of black-footed ferrets on their lands may rescind their consent, and
at their request, we will relocate the ferrets pursuant to paragraph (g)(4)(iii) of this section.
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(h) Whooping crane (Grus americana). (1) The whooping crane populations identified in paragraphs (h)(9)(i)
through (iv) of this section are nonessential experimental populations (NEPs) as defined in §17.80.
(i) The only natural extant population of whooping cranes, known as the Aransas/Wood Buffalo National Park
population, occurs well west of the Mississippi River. This population nests in the Northwest Territories and
adjacent areas of Alberta, Canada, primarily within the boundaries of the Wood Buffalo National Park, and winters
along the Central Texas Gulf of Mexico coast at Aransas National Wildlife Refuge.
(ii) No natural populations of whooping cranes are likely to come into contact with the NEPs set forth in paragraphs
(h)(9)(i) through (iv) of this section. Whooping cranes adhere to ancestral breeding grounds, leaving little possibility
that individuals from the extant Aransas/Wood Buffalo National Park population will stray into the NEPs. Studies of
whooping cranes have shown that migration is a learned rather than an innate behavior.
(2) No person may take this species in the wild in the experimental population areas, except when such take is
accidental and incidental to an otherwise lawful activity, or as provided in paragraphs (h)(3) and (4) of this section.
Examples of otherwise lawful activities include, but are not limited to, oil and gas exploration and extraction,
aquacultural practices, agricultural practices, pesticide application, water management, construction, recreation,
trapping, or hunting, when such activities are in full compliance with all applicable laws and regulations.
(3) Any person with a valid permit issued by the Fish and Wildlife Service (Service) under §17.32 may take
whooping cranes in the wild in the experimental population areas for educational purposes, scientific purposes, the
enhancement of propagation or survival of the species, and other conservation purposes consistent with the ESA
and in accordance with applicable State fish and wildlife conservation laws and regulations.
(4) Any employee or agent of the Service or State wildlife agency who is designated for such purposes, when
acting in the course of official duties, may take a whooping crane in the wild in the experimental population areas if
such action is necessary to:
(i) Relocate a whooping crane to avoid conflict with human activities;
(ii) Relocate a whooping crane that has moved outside any of the areas identified in paragraphs (h)(9)(i) through
(iv) of this section, when removal is necessary or requested and is authorized by a valid permit under §17.22;
(iii) Relocate whooping cranes within the experimental population areas to improve survival and recovery
prospects;
(iv) Relocate whooping cranes from the experimental population areas into captivity;
(v) Aid a sick, injured, or orphaned whooping crane; or
(vi) Dispose of a dead specimen or salvage a dead specimen that may be useful for scientific study.
(5) Any taking pursuant to paragraphs (h)(3) and (4) of this section must be immediately reported to the National
Whooping Crane Coordinator, U.S. Fish and Wildlife Service, P.O. Box 100, Austwell, TX 77950 (Phone: 361-2863559), who, in conjunction with his counterpart in the Canadian Wildlife Service, will determine the disposition of
any live or dead specimens.
(6) No person shall possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever, any
such species from the experimental populations taken in violation of these regulations or in violation of applicable
State fish and wildlife laws or regulations or the Endangered Species Act.
(7) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed any
offense defined in paragraphs (h)(2) through (6) of this section.
(8) The Service will not mandate any closure of areas, including National Wildlife Refuges, during hunting or
conservation order seasons, or closure or modification of hunting or conservation order seasons, in the following
situations:
(i) For the purpose of avoiding take of whooping cranes in the NEPs identified in paragraphs (h)(9)(i) through (iv)
of this section;
(ii) If a clearly marked whooping crane from the NEPs identified in paragraphs (h)(9)(i) through (iv) of this section
wanders outside the designated NEP areas. In this situation, the Service will attempt to capture the stray bird and
return it to the appropriate area if removal is requested by the State.
(9) All whooping cranes found in the wild within the boundaries listed in paragraphs (h)(9)(i) through (iv) of this
section will be considered nonessential experimental animals. Geographic areas the nonessential experimental
populations may inhabit are within the historic range of the whooping crane in the United States and include the
following:
(i) The entire State of Florida (the Kissimmee Prairie NEP). The reintroduction site is the Kissimmee Prairie
portions of Polk, Osceola, Highlands, and Okeechobee Counties. The experimental population released at
Kissimmee Prairie is expected to remain mostly within the prairie region of central Florida.
(ii) The States of Colorado, Idaho, New Mexico, and Utah, and the western half of the State of Wyoming (the
Rocky Mountain NEP).
(iii) That portion of the eastern contiguous United States that includes the States of Alabama, Arkansas, Florida,
Georgia, Illinois, Indiana, Iowa, Kentucky, Louisiana, Michigan, Minnesota, Mississippi, Missouri, North Carolina,
Ohio, South Carolina, Tennessee, Virginia, West Virginia, and Wisconsin (the Eastern Migratory NEP). Whooping
cranes within this population are expected to occur mostly within the States of Wisconsin, Illinois, Indiana,
Kentucky, Tennessee, Georgia, and Florida. The additional States included within the experimental population
area are those expected to receive occasional use by the cranes, or which may be used as breeding or wintering
areas in the event of future population expansion.
(iv) The entire State of Louisiana (the Louisiana Nonmigratory NEP). The reintroduction site is the White Lake
Wetlands Conservation Area of southwestern Louisiana in Vermilion Parish. Current information indicates that
White Lake is the historic location of a resident nonmigratory population of whooping cranes that bred and reared
young in Louisiana. Whooping cranes within this nonmigratory population are expected to occur mostly within the
White Lake Wetlands Conservation Area and the nearby wetlands in Vermilion Parish. The marshes and wetlands
of southwestern Louisiana are expected to receive occasional use by the cranes and may be used in the event of
future population expansion.
(v) A map of all NEP areas in the United States for whooping cranes follows:
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(10) The reintroduced populations will be monitored during the duration of the projects by the use of radio
telemetry and other appropriate measures. Any animal that is determined to be sick, injured, or otherwise in need
of special care will be recaptured to the extent possible by Service and/or State wildlife personnel or their
designated agent and given appropriate care. Such animals will be released back to the wild as soon as possible,
unless physical or behavioral problems make it necessary to return them to a captive-breeding facility.
(11) The Service will reevaluate the status of the experimental populations periodically to determine future
management needs. This review will take into account the reproductive success and movement patterns of the
individuals released within the experimental population areas.
(i) [Reserved]
(j) California condor (Gymnogyps californianus). (1) The California condor (Gymnogyps californianus) population
identified in paragraph (j)(8) of this section is a nonessential experimental population, and the release of such
population will further the conservation of the species.
(2) You must not take any California condor in the wild in the experimental population area except as provided by
this rule:
(i) Throughout the entire California condor experimental population area, you will not be in violation of the
Endangered Species Act (Act) if you unavoidably and unintentionally take (including killing or injuring) a California
condor, provided such take is non-negligent and incidental to a lawful activity, such as hunting, driving, or
recreational activities, and you report the take as soon as possible as provided under paragraph 5 below.
(ii) [Reserved]
(3) If you have a valid permit issued by the Service under §17.32, you may take California condors in the wild in
the experimental population area, pursuant to the terms of the permit.
(4) Any employee or agent of the Fish and Wildlife Service (Service), Bureau of Land Management or appropriate
State wildlife agency, who is designated for such purposes, when acting in the course of official duties, may take a
California condor from the wild in the experimental population area and vicinity if such action is necessary:
(i) For scientific purposes;
(ii) To relocate California condors within the experimental population area to improve condor survival, and to
address conflicts with ongoing or proposed activities, or with private landowners, when removal is necessary to
protect the condor, or is requested by an adversely affected landowner or land manager, or other adversely
affected party. Adverse effects and requests for condor relocation will be documented, reported and resolved in as
an expedient manner as appropriate to the specific situation to protect condors and avoid conflicts. Prior to any
efforts to relocate condors, the Service will obtain permission from the appropriate landowner(s);
(iii) To relocate California condors that have moved outside the experimental population area, by returning the
condor to the experimental population area or moving it to a captive breeding facility. All captures and relocations
from outside the experimental population area will be coordinated with Service Cooperators, and conducted with
the permission of the landowner(s) or appropriate land management agency(s).
(iv) To aid a sick, injured, or orphaned California condor;
(v) To salvage a dead specimen that may be useful for scientific study; or
(vi) To dispose of a dead specimen.
(5) Any taking pursuant to paragraphs (j)(2), (j)(4)(iv), (j)(4)(v), and (j)(4)(vi), of this section must be reported as
soon as possible to the Field Supervisor, U.S. Fish and Wildlife Service, Ecological Services, Arizona Field Office,
Phoenix, 2321 W. Royal Palm Road, Suite 103, Arizona (telephone 602/640-2720) who will determine the
disposition of any live or dead specimens.
(6) You must not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever, any
California condor or part thereof from the experimental population taken in violation of this paragraph (j) or in
violation of applicable State or Tribal laws or regulations or the Act.
(7) It is unlawful for you to attempt to commit, solicit another to commit, or cause to be committed, any offense
defined in paragraphs (j)(2) and (j)(6) of this section.
(8) The designated experimental population area of the California condor includes portions of three states—
Arizona, Nevada, and Utah. The southern boundary is Interstate Highway 40 in Arizona from its junction with
Highway 191 west across Arizona to Kingman; the western boundary starts at Kingman, goes northwest on
Highway 93 to Interstate Highway 15, continues northeasterly on Interstate Highway 15 in Nevada and Utah, to
Interstate Highway 70 in Utah; where the northern boundary starts and goes across Utah to Highway 191; where
the eastern boundary starts and goes south through Utah until Highway 191 meets Interstate Highway 40 in
Arizona (See map at end of this paragraph (j)).
(i) All California condors released into the experimental population area, and their offspring, are to be marked and
visually identifiable by colored and coded patagial wing markers.
(ii) The Service has designated the experimental population area to accommodate the potential future movements
of a wild population of condors. All released condors and their progeny are expected to remain in the experimental
area due to the geographic extent of the designation.
(9) The nonessential experimental population area includes the entire highway rights-of-way of the highways in
paragraph (j)(8) of this section that constitute the perimeter boundary. All California condors found in the wild
within these boundaries will comprise the experimental population.
(i) The experimental population is to be monitored during the reintroduction project. All California condors are to be
given physical examinations before being released.
(ii) If there is any evidence that the condor is in poor health or diseased, it will not be released to the wild.
(iii) Any condor that displays signs of illness, is injured, or otherwise needs special care may be captured by
authorized personnel of the Service, Bureau of Land Management, or appropriate State wildlife agency or their
agents, and given the appropriate care. These condors are to be re-released into the reintroduction area as soon
as possible, unless physical or behavioral problems make it necessary to keep them in captivity for an extended
period of time, or permanently.
(10) The status of the reintroduction project is to receive an informal review on an annual basis and a formal
evaluation within the first 5 years after the initial release, and every 5 years thereafter. This evaluation will include,
but not be limited to: a review of management issues; compliance with agreements; assessment of available
carrion; dependence of older condors on supplemental food sources; post release behavior; causes and rates of
mortality; alternative release sites; project costs; public acceptance; and accomplishment of recovery tasks
prescribed in California Condor Recovery Plan. The number of variables that could affect this reintroduction project
make it difficult to develop criteria for success or failure after 5 years. However, if after 5 years the project is
experiencing a 40 percent or greater mortality rate or released condors are not finding food on their own, serious
consideration will be given to terminating the project.
(11) The Service does not intend to pursue a change in the nonessential experimental population designation to
experimental essential, threatened, or endangered, or modify the experimental population area boundaries without
consulting with and obtaining the full cooperation of affected parties located within the experimental population
area, the reintroduction program cooperators identified in the memorandum of understanding (MOU) for this
program, and the cooperators identified in the agreement for this program.
(i) The Service does not intend to change the status of this nonessential population until the California condor is
recovered and delisted in accordance with the Act or if the reintroduction is not successful and the rule is revoked.
No designation of critical habitat will be made for nonessential populations (16 U.S.C. §1539(j)(2)(C)(ii).
(ii) Legal actions or other circumstances may compel a change in this nonessential experimental population's legal
status to essential, threatened, or endangered, or compel the Service to designate critical habitat for the California
condors within the experimental population area defined in this rule. If this happens, all California condors will be
removed from the area and this experimental population rule will be revoked, unless the parties to the MOU and
agreement existing at that time agree that the birds should remain in the wild. Changes in the legal status and/or
removal of this population of California condors will be made in compliance with any applicable Federal rulemaking
and other procedures.
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(k) Mexican wolf (Canis lupus baileyi). This paragraph (k) sets forth the provisions of a rule to establish an
experimental population of Mexican wolves.
(1) Purpose of the rule. The U.S. Fish and Wildlife Service (Service) finds that reestablishment of an experimental
population of Mexican wolves into the subspecies' probable historical range will further the conservation of the
Mexican wolf subspecies. The Service found that the experimental population was not essential under §17.81(c)
(2).
(2) Determinations. The Mexican wolf population reestablished in the Mexican Wolf Experimental Population Area
(MWEPA), identified in paragraph (k)(4) of this section, is one nonessential experimental population. This
nonessential experimental population will be managed according to the provisions of this rule. The Service does
not intend to change the nonessential experimental designation to essential experimental, threatened, or
endangered. Critical habitat cannot be designated under the nonessential experimental classification, 16 U.S.C.
1539(j)(2)(C)(ii).
(3) Definitions. Key terms used in this rule have the following definitions:
Active den means a den or a specific site above or below ground that is used by Mexican wolves on a daily basis
to bear and raise pups, typically between approximately April 1 and July 31. More than one den site may be used
in a single season.
Cross-foster means the removal of offspring from their biological parents and placement with surrogate parents.
Depredation means the confirmed killing or wounding of lawfully present domestic animals by one or more
Mexican wolves. The Service, Wildlife Services, or other Service-designated agencies will confirm cases of wolf
depredation on lawfully present domestic animals. Cattle trespassing on Federal lands are not considered lawfully
present domestic animals.
Designated agency means a Federal, State, or tribal agency designated by the Service to assist in implementing
this rule, all or in part, consistent with a Service-approved management plan, special management measure,
conference opinion pursuant to section 7(a)(4) of the Act, section 6 of the Act as described in §17.31 for State
game and fish agencies with authority to manage Mexican wolves, or a valid permit issued by the Service through
§17.32.
Disturbance-causing land-use activity means any activity on Federal lands within a 1-mi (1.6-km) radius around
release pens when Mexican wolves are in them, around active dens between April 1 and July 31, and around
active Mexican wolf rendezvous sites between June 1 and September 30, which the Service determines could
adversely affect reproductive success, natural behavior, or persistence of Mexican wolves. Such activities may
include, but are not limited to, timber or wood harvesting, prescribed fire, mining or mine development, camping
outside designated campgrounds, livestock husbandry activities (e.g., livestock drives, roundups, branding,
vaccinating, etc.), off-road vehicle use, hunting, and any other use or activity with the potential to disturb wolves.
The following activities are specifically excluded from this definition:
(A) Lawfully present livestock and use of water sources by livestock;
(B) Livestock drives if no reasonable alternative route or timing exists;
(C) Vehicle access over established roads to non-Federal land where legally permitted activities are ongoing if no
reasonable alternative route exists;
(D) Use of lands within the National Park or National Wildlife Refuge Systems as safety buffer zones for military
activities and Department of Homeland Security border security activities;
(E) Fire-fighting activities associated with wildfires; and
(F) Any authorized, specific land use that was active and ongoing at the time Mexican wolves chose to locate a
den or rendezvous site nearby.
Domestic animal means livestock as defined in this paragraph (k)(3) and non-feral dogs.
Federal land means land owned and under the administration of Federal agencies including, but not limited to, the
Service, National Park Service, Bureau of Land Management, U.S. Forest Service, Department of Energy, or
Department of Defense.
Feral dog means any dog (Canis familiaris) or wolf-dog hybrid that, because of absence of physical restraint or
conspicuous means of identifying it at a distance as non-feral, is reasonably thought to range freely without
discernible, proximate control by any person. Feral dogs do not include domestic dogs that are penned, leashed,
or otherwise restrained (e.g., by shock collar) or which are working livestock or being lawfully used to trail or locate
wildlife.
Harass means intentional or negligent actions or omissions that create the likelihood of injury to wildlife by
annoying it to such an extent as to significantly disrupt normal behavioral patterns, which include, but are not
limited to, breeding, feeding, or sheltering.
In the act of biting, killing, or wounding means grasping, biting, wounding, or feeding upon a live domestic animal
on non-Federal land or live livestock on Federal land. The term does not include feeding on an animal carcass.
Initial release means the release of Mexican wolves to the wild within Zone 1, as defined in this paragraph (k)(3),
or in accordance with tribal or private land agreements in Zone 2, as defined in this paragraph (k)(3), that have
never been in the wild, or releasing pups that have never been in the wild and are less than 5 months old within
Zones 1 or 2. The initial release of pups less than 5 months old into Zone 2 allows for the cross-fostering of pups
from the captive population into the wild, as well as enables translocation-eligible adults to be re-released in Zone
2 with pups born in captivity.
Intentional harassment means deliberate, preplanned harassment of Mexican wolves, including by less-than-lethal
means (such as 12-gauge shotgun rubber-bullets and bean-bag shells) designed to cause physical discomfort and
temporary physical injury, but not death. Intentional harassment includes situations where the Mexican wolf or
wolves may have been unintentionally attracted—or intentionally tracked, waited for, chased, or searched out—
and then harassed. Intentional harassment of Mexican wolves is only allowed under a permit issued by the Service
or its designated agency.
Livestock means domestic alpacas, bison, burros (donkeys), cattle, goats, horses, llamas, mules, and sheep, or
other domestic animals defined as livestock in Service-approved State and tribal Mexican wolf management plans.
Poultry is not considered livestock under this rule.
Mexican Wolf Experimental Population Area (MWEPA) means an area in Arizona and New Mexico including
Zones 1, 2, and 3, as defined in this paragraph (k)(3), that lies south of Interstate Highway 40 to the international
border with Mexico.
Non-Federal land means any private, State-owned, or tribal trust land.
Occupied Mexican wolf range means an area of confirmed presence of Mexican wolves based on the most recent
map of occupied range posted on the Service's Mexican Wolf Recovery Program Web site
at http://www.fws.gov/southwest/es/mexicanwolf/. Specific to the prohibitions at paragraphs (k)(5)(iii) and (k)(5)(vii)
(D) of this section, Zone 3, as defined in this paragraph (k)(3), and tribal trust lands are not considered occupied
range.
Opportunistic harassment means scaring any Mexican wolf from the immediate area by taking actions such as
discharging firearms or other projectile-launching devices in proximity to, but not in the direction of, the wolf,
throwing objects at it, or making loud noise in proximity to it. Such harassment might cause temporary, nondebilitating physical injury, but is not reasonably anticipated to cause permanent physical injury or death.
Opportunistic harassment of Mexican wolves can occur without a permit issued by the Service or its designated
agency.
Problem wolves mean Mexican wolves that, for purposes of management and control by the Service or its
designated agent(s), are:
(A) Individuals or members of a group or pack (including adults, yearlings, and pups greater than 4 months of age)
that were involved in a depredation on lawfully present domestic animals;
(B) Habituated to humans, human residences, or other facilities regularly occupied by humans; or
(C) Aggressive when unprovoked toward humans.
Rendezvous site means a gathering and activity area regularly used by Mexican wolf pups after they have
emerged from the den. Typically, these sites are used for a period ranging from about 1 week to 1 month in the
first summer after birth during the period from June 1 to September 30. Several rendezvous sites may be used in
succession within a single season.
Service-approved management plan means management plans approved by the Regional Director or Director of
the Service through which Federal, State, or tribal agencies may become a designated agency. The management
plan must address how Mexican wolves will be managed to achieve conservation goals in compliance with the Act,
this experimental population rule, and other Service policies. If a Federal, State, or tribal agency becomes a
designated agency through a Service-approved management plan, the Service will help coordinate their activities
while retaining authority for program direction, oversight, guidance, and authorization of Mexican wolf removals.
Take means to harass, harm, pursue, hunt, shoot, wound, kill, trap, capture, or collect, or to attempt to engage in
any such conduct (16 U.S.C. 1532(19)).
Translocate means the release of Mexican wolves into the wild that have previously been in the wild. In the
MWEPA, translocations will occur only in Zones 1 and 2, as defined in this paragraph (k)(3).
Tribal trust land means any lands title to which is either: Held in trust by the United States for the benefit of any
Indian tribe or individual; or held by any Indian tribe or individual subject to restrictions by the United States against
alienation. For purposes of this rule, tribal trust land does not include land purchased in fee title by a tribe. We
consider fee simple land purchased by tribes to be private land.
Unacceptable impact to a wild ungulate herd will be determined by a State game and fish agency based upon
ungulate management goals, or a 15 percent decline in an ungulate herd as documented by a State game and fish
agency, using their preferred methodology, based on the preponderance of evidence from bull to cow ratios, cow
to calf ratios, hunter days, and/or elk population estimates.
Unintentional take means the take of a Mexican wolf by any person if the take is unintentional and occurs while
engaging in an otherwise lawful activity, occurs despite the use of due care, is coincidental to an otherwise lawful
activity, and is not done on purpose. Taking a Mexican wolf by poisoning or shooting will not be considered
unintentional take.
Wild ungulate herd means an assemblage of wild ungulates (bighorn sheep, bison, deer, elk, or pronghorn) living
in a given area.
Wildlife Services means the U.S. Department of Agriculture, Animal and Plant Health Inspection Service, Wildlife
Services.
Wounded means exhibiting scraped or torn hide or flesh, bleeding, or other evidence of physical damage caused
by a Mexican wolf bite.
Zone 1 means an area within the MWEPA in Arizona and New Mexico into which Mexican wolves will be allowed
to naturally disperse and occupy and where Mexican wolves may be initially released from captivity or
translocated. Zone 1 includes all of the Apache, Gila, and Sitgreaves National Forests; the Payson, Pleasant
Valley, and Tonto Basin Ranger Districts of the Tonto National Forest; and the Magdalena Ranger District of the
Cibola National Forest.
Zone 2 is an area within the MWEPA into which Mexican wolves will be allowed to naturally disperse and occupy,
and where Mexican wolves may be translocated.
(A) On Federal land in Zone 2, initial releases of Mexican wolves are limited to pups less than 5 months old, which
allows for the cross-fostering of pups from the captive population into the wild, as well as enables translocationeligible adults to be re-released with pups born in captivity. On private and tribal land in Zone 2, Mexican wolves of
any age, including adults, can also be initially released under a Service- and State-approved management
agreement with private landowners or a Service-approved management agreement with tribal agencies.
(B) The northern boundary of Zone 2 is Interstate Highway 40; the western boundary extends south from Interstate
Highway 40 and follows Arizona State Highway 93, Arizona State Highway 89/60, Interstate Highway 10, and
Interstate Highway 19 to the United States-Mexico international border; the southern boundary is the United
States-Mexico international border heading east, then follows New Mexico State Highway 81/146 north to
Interstate Highway 10, then along New Mexico State Highway 26 to Interstate Highway 25; the boundary
continues along New Mexico State Highway 70/54/506/24; the eastern boundary follows the eastern edge of Otero
County, New Mexico, to the north and then along the southern and then eastern edge of Lincoln County, New
Mexico, until it intersects with New Mexico State Hwy 285 and follows New Mexico State Highway 285 north to the
northern boundary of Interstate Highway 40. Zone 2 excludes the area in Zone 1, as defined in this paragraph (k)
(3).
Zone 3 means an area within the MWEPA into which Mexican wolves will be allowed to disperse and occupy, but
neither initial releases nor translocations will occur there.
(A) Zone 3 is an area of less suitable Mexican wolf habitat where Mexican wolves will be more actively managed
under the authorities of this rule to reduce human conflict. We expect Mexican wolves to occupy areas of suitable
habitat where ungulate populations are adequate to support them and conflict with humans and their livestock is
low. If Mexican wolves move outside of areas of suitable habitat, they will be more actively managed.
(B) Zone 3 is two separate geographic areas on the eastern and western sides of the MWEPA. One area of Zone
3 is in western Arizona, and the other is in eastern New Mexico. In Arizona, the northern boundary of Zone 3 is
Interstate Highway 40; the eastern boundary extends south from Interstate Highway 40 and follows State Highway
93, State Highway 89/60, Interstate Highway 10, and Interstate Highway 19 to the United States-Mexico
international border; the southern boundary is the United States-Mexico international border; the western boundary
is the Arizona-California State border. In New Mexico, the northern boundary of Zone 3 is Interstate Highway 40;
the eastern boundary is the New Mexico-Texas State border; the southern boundary is the United States-Mexico
international border heading west, then follows State Highway 81/146 north to Interstate Highway 10, then along
State Highway 26 to Interstate Highway 25, the southern boundary continues along State Highway 70/54/506/24;
the western boundary follows the eastern edge of Otero County to the north and then along the southern and then
eastern edge of Lincoln County until it follows State Highway 285 north to the northern boundary of Interstate
Highway 40.
(4) Designated area. The designated experimental population area for Mexican wolves classified as a nonessential
experimental population by this rule is within the subspecies' probable historical range and is wholly separate
geographically from the current range of any known Mexican wolves. The boundaries of the MWEPA are the
portions of Arizona and New Mexico that are south of Interstate Highway 40 to the international border with
Mexico. A map of the MWEPA follows:
eCFR graphic er16ja15.020.gif
View or download PDF
(5) Prohibitions. Take of any Mexican wolf in the experimental population is prohibited, except as provided in
paragraph (k)(7) of this section. Specifically, the following actions are prohibited by this rule:
(i) No person may possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any
Mexican wolf or wolf part from the experimental population except as authorized in this rule or by a valid permit
issued by the Service under §17.32. If a person kills or injures a Mexican wolf or finds a dead or injured wolf or
wolf parts, the person must not disturb them (unless instructed to do so by the Service or a designated agency),
must minimize disturbance of the area around them, and must report the incident to the Service's Mexican Wolf
Recovery Coordinator or a designated agency of the Service within 24 hours as described in paragraph (k)(6) of
this section.
(ii) No person may attempt to commit, solicit another to commit, or cause to be committed, any offense defined in
this rule.
(iii) Taking a Mexican wolf with a trap, snare, or other type of capture device within occupied Mexican wolf range is
prohibited (except as authorized in paragraph (k)(7)(iv) of this section) and will not be considered unintentional
take, unless due care was exercised to avoid injury or death to a wolf. With regard to trapping activities, due care
includes:
(A) Following the regulations, proclamations, recommendations, guidelines, and/or laws within the State or tribal
trust lands where the trapping takes place.
(B) Modifying or using appropriately sized traps, chains, drags, and stakes that provide a reasonable expectation
that the wolf will be prevented from either breaking the chain or escaping with the trap on the wolf, or using
sufficiently small traps (less than or equal to a Victor #2 trap) that allow a reasonable expectation that the wolf will
either immediately pull free from the trap or span the jaw spread when stepping on the trap.
(C) Not taking a Mexican wolf using neck snares.
(D) Reporting the capture of a Mexican wolf (even if the wolf has pulled free) within 24 hours to the Service as
described in paragraph (k)(6) of this section.
(E) If a Mexican wolf is captured, trappers can call the Interagency Field Team (1-888-459-WOLF [9653]) as soon
as possible to arrange for radio-collaring and releasing of the wolf. Per State regulations for releasing nontarget
animals, trappers may also choose to release the animal alive and subsequently contact the Service or
Interagency Field Team.
(6) Reporting requirements. Unless otherwise specified in this rule or in a permit, any take of a Mexican wolf must
be reported to the Service or a designated agency within 24 hours. We will allow additional reasonable time if
access to the site is limited. Report any take of Mexican wolves, including opportunistic harassment, to the
Mexican Wolf Recovery Program, U.S. Fish and Wildlife Service, New Mexico Ecological Services Field Office,
2105 Osuna Road, NE., Albuquerque, NM 87113; by telephone 505-761-4704; or by facsimile 505-346-2542.
Additional contact information can also be found on the Mexican Wolf Recovery Program's Web site
at http://www.fws.gov/southwest/es/mexicanwolf/. Unless otherwise specified in a permit, any wolf or wolf part
taken legally must be turned over to the Service, which will determine the disposition of any live or dead wolves.
(7) Allowable forms of take of Mexican wolves. Take of Mexican wolves in the experimental population is allowed
as follows:
(i) Take in defense of human life. Under section 11(a)(3) of the Act and §17.21(c)(2), any person may take (which
includes killing as well as nonlethal actions such as harassing or harming) a Mexican wolf in self-defense or
defense of the lives of others. This take must be reported as specified in accordance with paragraph (k)(6) of this
section. If the Service or a designated agency determines that a Mexican wolf presents a threat to human life or
safety, the Service or the designated agency may kill the wolf or place it in captivity.
(ii) Opportunistic harassment. Anyone may conduct opportunistic harassment of any Mexican wolf at any time
provided that Mexican wolves are not purposefully attracted, tracked, searched out, or chased and then harassed.
Such harassment of Mexican wolves might cause temporary, non-debilitating physical injury, but is not reasonably
anticipated to cause permanent physical injury or death. Any form of opportunistic harassment must be reported
as specified in accordance with paragraph (k)(6) of this section.
(iii) Intentional harassment. After the Service or its designated agency has confirmed Mexican wolf presence on
any land within the MWEPA, the Service or its designated agency may issue permits valid for not longer than 1
year, with appropriate stipulations or conditions, to allow intentional harassment of Mexican wolves. The
harassment must occur in the area and under the conditions specifically identified in the permit. Permittees must
report this take as specified in accordance with paragraph (k)(6) of this section.
(iv) Take on non-Federal lands. (A) On non-Federal lands anywhere within the MWEPA, domestic animal owners
or their agents may take (including kill or injure) any Mexican wolf that is in the act of biting, killing, or wounding a
domestic animal, as defined in paragraph (k)(3) of this section. After the take of a Mexican wolf, the Service must
be provided evidence that the wolf was in the act of biting, killing, or wounding a domestic animal at the time of
take, such as evidence of freshly wounded or killed domestic animals. This take must be reported as specified in
accordance with paragraph (k)(6) of this section. The take of any Mexican wolf without evidence of biting, killing, or
wounding domestic animals may be referred to the appropriate authorities for investigation.
(B) Take of Mexican wolves by livestock guarding dogs, when used to protect livestock on non-Federal lands, is
allowed. If such take by a guard dog occurs, it must be reported as specified in accordance with paragraph (k)(6)
of this section.
(C) Based on the Service's or a designated agency's discretion and in conjunction with a removal action
authorized by the Service, the Service or designated agency may issue permits to domestic animal owners or their
agents (e.g., employees, land manager, local officials) to take (including intentional harassment or killing) any
Mexican wolf that is present on non-Federal land where specified in the permit. Permits issued under this provision
will specify the number of days for which the permit is valid and the maximum number of Mexican wolves for which
take is allowed. Take by permittees under this provision will assist the Service or designated agency in completing
control actions. Domestic animal owners or their agents must report this take as specified in accordance with
paragraph (k)(6) of this section.
(v) Take on Federal land. (A) Based on the Service's or a designated agency's discretion and in conjunction with a
removal action authorized by the Service, the Service may issue permits to livestock owners or their agents (e.g.,
employees, land manager, local officials) to take (including intentional harassment or killing) any Mexican wolf that
is in the act of biting, killing, or wounding livestock on Federal land where specified in the permit.
(1) Permits issued under this provision will specify the number of days for which the permit is valid and the
maximum number of Mexican wolves for which take is allowed. Take by permittees under this provision will assist
the Service or designated agency in completing control actions. Livestock owners or their agents must report this
take as specified in accordance with paragraph (k)(6) of this section.
(2) After the take of a Mexican wolf, the Service must be provided evidence that the wolf was in the act of biting,
killing, or wounding livestock at the time of take, such as evidence of freshly wounded or killed livestock. The take
of any Mexican wolf without evidence of biting, killing, or wounding domestic animals may be referred to the
appropriate authorities for investigation.
(B) Take of Mexican wolves by livestock guarding dogs, when used to protect livestock on Federal lands, is
allowed. If such take by a guard dog occurs, it must be reported as specified in accordance with paragraph (k)(6)
of this section.
(C) This provision for take on Federal land does not exempt Federal agencies and their contractors from
complying with sections 7(a)(1) and 7(a)(4) of the Act, the latter of which requires a conference with the Service if
they propose an action that is likely to jeopardize the continued existence of the Mexican wolf. In areas within the
National Park System and National Wildlife Refuge System, Federal agencies must treat Mexican wolves as a
threatened species for purposes of complying with section 7 of the Act.
(vi) Take in response to unacceptable impacts to a wild ungulate herd. If the Arizona or New Mexico game and fish
agency determines that Mexican wolf predation is having an unacceptable impact to a wild ungulate herd, as
defined in paragraph (k)(3) of this section, the respective State game and fish agency may request approval from
the Service that Mexican wolves be removed from the area of the impacted wild ungulate herd. Upon written
approval from the Service, the State (Arizona or New Mexico) or any designated agency may be authorized to
remove (capture and translocate in the MWEPA, move to captivity, transfer to Mexico, or lethally take) Mexican
wolves. These management actions must occur in accordance with the following provisions:
(A) The Arizona or New Mexico game and fish agency must prepare a science-based document that:
(1) Describes what data indicate that the wild ungulate herd is below management objectives, what data indicate
that the impact on the wild ungulate herd is influenced by Mexican wolf predation, why Mexican wolf removal is a
warranted solution to help restore the wild ungulate herd to State game and fish agency management objectives,
the type (level and duration) of Mexican wolf removal management action being proposed, and how wild ungulate
herd response to wolf removal will be measured and control actions adjusted for effectiveness;
(2) Demonstrates that attempts were and are being made to identify other causes of wild ungulate herd declines
and possible remedies or conservation measures in addition to wolf removal;
(3) If appropriate, identifies areas of suitable habitat for Mexican wolf translocation; and
(4) Has been subjected to peer review and public comment prior to its submittal to the Service for written
concurrence. In order to comply with this requirement, the State game and fish agency must:
(i) Conduct the peer review process in conformance with the Office of Management and Budget's most recent
Final Information and Quality Bulletin for Peer Review and include in their proposal an explanation of how the
bulletin's standards were considered and satisfied; and
(ii) Obtain at least three independent peer reviews from individuals with relevant expertise other than staff
employed by the State (Arizona or New Mexico) requesting approval from the Service that Mexican wolves be
removed from the area of the affected wild ungulate herd.
(B) Before the Service will allow Mexican wolf removal in response to impacts to wild ungulates, the Service will
evaluate the information provided by the requesting State (Arizona or New Mexico) and provide a written
determination to the requesting State game and fish agency on whether such actions are scientifically based and
warranted.
(C) If all of the provisions above are met, the Service will, to the maximum extent allowable under the Act, make a
determination providing for Mexican wolf removal. If the request is approved, the Service will include in the written
determination which management action (capture and translocate in MWEPA, move to captivity, transfer to
Mexico, lethally take, or no action) is most appropriate for the conservation of the Mexican wolf subspecies.
(D) Because tribes are able to request the capture and removal of Mexican wolves from tribal trust lands at any
time, take in response to impacts to wild ungulate herds is not applicable on tribal trust lands.
(vii) Take by Service personnel or a designated agency. The Service or a designated agency may take any
Mexican wolf in the experimental population in a manner consistent with a Service-approved management plan,
special management measure, biological opinion pursuant to section 7(a)(2) of the Act, conference opinion
pursuant to section 7(a)(4) of the Act, section 6 of the Act as described in §17.31 for State game and fish agencies
with authority to manage Mexican wolves, or a valid permit issued by the Service through §17.32.
(A) The Service or designated agency may use leg-hold traps and any other effective device or method for
capturing or killing Mexican wolves to carry out any measure that is a part of a Service-approved management
plan, special management measure, or valid permit issued by the Service under §17.32, regardless of State law.
The disposition of all Mexican wolves (live or dead) or their parts taken as part of a Service-approved management
activity must follow provisions in Service-approved management plans or interagency agreements or procedures
approved by the Service on a case-by-case basis.
(B) The Service or designated agency may capture; kill; subject to genetic testing; place in captivity; or euthanize
any feral wolf-like animal or feral wolf hybrid found within the MWEPA that shows physical or behavioral evidence
of: Hybridization with other canids, such as domestic dogs or coyotes; being a wolf-like animal raised in captivity,
other than as part of a Service-approved wolf recovery program; or being socialized or habituated to humans. If
determined to be a pure Mexican wolf, the wolf may be returned to the wild.
(C) The Service or designated agency may carry out intentional or opportunistic harassment, nonlethal control
measures, translocation, placement in captivity, or lethal control of problem wolves. To determine the presence of
problem wolves, the Service will consider all of the following:
(1) Evidence of wounded domestic animal(s) or remains of domestic animal(s) that show that the injury or death
was caused by Mexican wolves;
(2) The likelihood that additional Mexican wolf-caused depredations or attacks of domestic animals may occur if no
harassment, nonlethal control, translocation, placement in captivity, or lethal control is taken;
(3) Evidence of attractants or intentional feeding (baiting) of Mexican wolves; and
(4) Evidence that Mexican wolves are habituated to humans, human residences, or other facilities regularly
occupied by humans, or evidence that Mexican wolves have exhibited unprovoked and aggressive behavior
toward humans.
(D) Wildlife Services will not use M-44's and choking-type snares in occupied Mexican wolf range. Wildlife
Services may restrict or modify other predator control activities pursuant to a Service-approved management
agreement or a conference opinion between Wildlife Services and the Service.
(viii) Unintentional take. (A) Take of a Mexican wolf by any person is allowed if the take is unintentional and occurs
while engaging in an otherwise lawful activity. Such take must be reported as specified in accordance with
paragraph (k)(6) of this section. Hunters and other shooters have the responsibility to identify their quarry or target
before shooting; therefore, shooting a Mexican wolf as a result of mistaking it for another species will not be
considered unintentional take. Take by poisoning will not be considered unintentional take.
(B) Federal, State, or tribal agency employees or their contractors may take a Mexican wolf or wolf-like animal if
the take is unintentional and occurs while engaging in the course of their official duties. This includes, but is not
limited to, military training and testing and Department of Homeland Security border security activities. Take of
Mexican wolves by Federal, State, or tribal agencies must be reported as specified in accordance with paragraph
(k)(6) of this section.
(C) Take of Mexican wolves by Wildlife Services employees while conducting official duties associated with
predator damage management activities for species other than Mexican wolves may be considered unintentional if
it is coincidental to a legal activity and the Wildlife Services employees have adhered to all applicable Wildlife
Services' policies, Mexican wolf standard operating procedures, and reasonable and prudent measures or
recommendations contained in Wildlife Service's biological and conference opinions.
(ix) Take for research purposes. The Service may issue permits under §17.32, and designated agencies may issue
permits under State and Federal laws and regulations, for individuals to take Mexican wolves pursuant to scientific
study proposals approved by the agency or agencies with jurisdiction for Mexican wolves and for the area in which
the study will occur. Such take should lead to management recommendations for, and thus provide for the
conservation of, the Mexican wolf.
(8) Disturbance-causing land-use activities. For any activity on Federal lands that the Service determines could
adversely affect reproductive success, natural behavior, or persistence of Mexican wolves, the Service will work
with Federal agencies to use their authorities to temporarily restrict human access and disturbance-causing landuse activities within a 1-mi (1.6-km) radius around release pens when Mexican wolves are in them, around active
dens between approximately April 1 and July 31, and around active Mexican wolf rendezvous sites between
approximately June 1 and September 30, as necessary.
(9) Management. (i) On private land within Zones 1 and 2, as defined in paragraph (k)(3) of this section, of the
MWEPA, the Service or designated agency may develop and implement management actions to benefit Mexican
wolf recovery in cooperation with willing private landowners, including initial release and translocation of Mexican
wolves onto such lands in Zones 1 or 2 if requested by the landowner and with the concurrence of the State game
and fish agency.
(ii) On tribal trust land within Zones 1 and 2, as defined in paragraph (k)(3) of this section, of the MWEPA, the
Service or a designated agency may develop and implement management actions in cooperation with willing tribal
governments, including: occupancy by natural dispersal, initial release, and translocation of Mexican wolves onto
such lands. No agreement between the Service and a Tribe is necessary for the capture and removal of Mexican
wolves from tribal trust lands if requested by the tribal government.
(iii) Based on end-of-year counts, we will manage for a population objective of 300 to 325 Mexican wolves in the
MWEPA in Arizona and New Mexico. So as not to exceed this population objective, we will exercise all
management options with preference for translocation to other Mexican wolf populations to further the
conservation of the subspecies. The Service may change this provision as necessary to accommodate a new
recovery plan.
(iv) We are implementing a phased approach to Mexican wolf management within the MWEPA in western Arizona
as follows:
(A) Phase 1 will be implemented for the first 5 years following February 17, 2015. During this phase, initial
releases and translocation of Mexican wolves can occur throughout Zone 1 with the exception of the area west of
State Highway 87 in Arizona. No translocations can be conducted west of State Highway 87 in Arizona in Zone 2.
Mexican wolves can disperse naturally from Zones 1 and 2 into, and occupy, the MWEPA (Zones 1, 2, and 3, as
defined in paragraph (k)(3) of this section). However, during Phase 1, dispersal and occupancy in Zone 2 west of
State Highway 87 will be limited to the area north of State Highway 260 and west to Interstate 17. A map of Phase
1 follows:
eCFR graphic er16ja15.021.gif
View or download PDF
(B) In Phase 2, initial releases and translocation of Mexican wolves can occur throughout Zone 1 including the
area west of State Highway 87 in Arizona. No translocations can be conducted west of Interstate Highway 17 in
Arizona. Mexican wolves can disperse naturally from Zones 1 and 2 into, and occupy, the MWEPA (Zones 1, 2,
and 3, as defined in paragraph (k)(3) of this section). However, during Phase 2, dispersal and occupancy west of
Interstate Highway 17 will be limited to the area east of Highway 89 in Arizona. A map of Phase 2 follows:
eCFR graphic er16ja15.022.gif
View or download PDF
(C) In Phase 3, initial release and translocation of Mexican wolves can occur throughout Zone 1. No translocations
can be conducted west of State Highway 89 in Arizona. Mexican wolves can disperse naturally from Zones 1 and
2 into, and occupy, the MWEPA (Zones 1, 2, and 3, as defined in paragraph (k)(3) of this section). A map of Phase
3 follows:
eCFR graphic er16ja15.023.gif
View or download PDF
(D) While implementing this phased approach, two evaluations will be conducted: The first evaluation will cover the
first 5 years and the second evaluation will cover the first 8 years after February 17, 2015 in order to determine if
we will move forward with the next phase.
(1) Each phase evaluation will consider adverse human interactions with Mexican wolves, impacts to wild ungulate
herds, and whether or not the Mexican wolf population in the MWEPA is achieving a population number consistent
with a 10 percent annual growth rate based on end-of-year counts, such that 5 years after February 17, 2015, the
population of Mexican wolves in the wild is at least 150, and 8 years after February 17, 2015, the population of
Mexican wolves in the wild is at least 200.
(2) If we have not achieved this population growth, we will move forward to the next phase. Regardless of the
outcome of the two evaluations, by the beginning of year 12 from February 17, 2015, we will move to full
implementation of this rule throughout the MWEPA, and the phased management approach will no longer apply.
(E) The phasing may be expedited with the concurrence of participating State game and fish agencies.
(10) Evaluation. The Service will evaluate Mexican wolf reestablishment progress and prepare periodic progress
reports and detailed annual reports. In addition, approximately 5 years after February 17, 2015, the Service will
prepare a one-time overall evaluation of the experimental population program that focuses on modifications
needed to improve the efficacy of this rule, reestablishment of Mexican wolves to the wild, and the contribution the
experimental population is making to the recovery of the Mexican wolf.
(l) Grizzly bear (Ursus arctos horribilis). (1) Where does this special rule apply? The special rule in this paragraph
(l) applies to the designated Bitterroot Grizzly Bear Experimental Population Area (Experimental Population Area),
which is found within the species' historic range and is defined as follows:
The boundaries of the Experimental Population Area are delineated by U.S. 93 from its junction with the Bitterroot
River near Missoula, Montana, to Challis, Idaho; Idaho 75 from Challis to Stanley, Idaho; Idaho 21 from Stanley to
Lowman, Idaho; State Highway 17 from Lowman to Banks, Idaho; Idaho 55 from Banks to New Meadows, Idaho;
U.S. 95 from New Meadows to Coeur d'Alene, Idaho; Interstate 90 from Coeur d'Alene, Idaho, to its junction with
the Clark Fork River near St. Regis, Montana; the Clark Fork River from its junction with Interstate 90 near St.
Regis to its confluence with the Bitterroot River near Missoula, Montana; and the Bitterroot River from its
confluence with the Clark Fork River to its junction with U.S. Highway 93, near Missoula, Montana (See map at the
end of this paragraph (l)).
(2) What is the legal status of the grizzly bear? (i) The grizzly bear is listed as “threatened” in §17.11 (h) and
protected under this part. However, the grizzly bear population to which this paragraph (l) applies is considered a
nonessential experimental population in accordance with section 10(j) of the Act.
(ii) We have determined that, as of December 18, 2000, no grizzly bear population exists in the Experimental
Population Area. We find, in accordance with §17.81 (b), that the reintroduction of grizzly bears as a nonessential
experimental population, as defined in §17.81 (b), will further the conservation of the species and will be consistent
with provisions of section 10(j) of the Act, which requires that an experimental population be geographically
separate from other nonexperimental populations of the same species. We also find, in accordance with §17.81 (c)
(2), that the experimental population of grizzly bears in the Experimental Population Area is not essential to the
survival of the species in the wild.
(iii) Grizzly bears within the Experimental Population Area and the Recovery Area will be accommodated through
management provisions provided for in this paragraph (l) and through management plans and policies developed
by the Citizen Management Committee (Committee; see paragraph (l)(6) of this section). After reintroduction,
every grizzly bear found within the Experimental Population Area will be considered a member of the nonessential
experimental population.
(iv) In the conterminous United States, a grizzly bear that is outside the Experimental Population Area identified in
paragraph (l)(1) of this section will be considered as threatened.
(3) Where will grizzly bears be released, and where will recovery be emphasized? The Bitterroot Grizzly Bear
Recovery Area identifies the area of recovery emphasis within the Experimental Population Area. The Recovery
Area consists of the Selway-Bitterroot Wilderness and the Frank Church-River of No Return Wilderness (See map
at the end of paragraph (l) of this section). All reintroductions will take place in the Selway-Bitterroot Wilderness
unless it is later determined that reintroduction in the Frank Church-River of No Return Wilderness is appropriate.
If, in the future, new wilderness areas are designated adjacent to the Recovery Area, the Committee may
recommend to the Secretary their addition to the Recovery Area. The Secretary would have to amend this
paragraph (l) to change the definition of the Recovery Area.
(4) What activities are prohibited in the Experimental Population Area? (i) You may not take (see definition in
§10.12 of this subchapter) any grizzly bear in the Experimental Population Area, except as provided in this
paragraph (l). We may refer unauthorized take of grizzly bears to the appropriate authorities for prosecution.
(ii) You may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any grizzly
bear or parts thereof that are taken from the Experimental Population Area or possessed in violation of the
regulations in this paragraph (l) or in violation of applicable State wildlife conservation laws or regulations or the
Act.
(iii) You may not attempt to commit, solicit another to commit, or cause to be committed, any offense defined in this
paragraph (l).
(5) What activities are allowed in the Experimental Population Area? (i) For purposes of this paragraph (l), except
for persons engaged in hunting or shooting activities, you will not be in violation of the Act for “unavoidable and
unintentional take” (see definition in paragraph (l)(16) of this section) of grizzly bears within the Experimental
Population Area when such take is incidental to a legal activity and is not a result of negligent conduct lacking
reasonable due care, and when due care was exercised to avoid the taking. Any taking must be reported within 24
hours to appropriate authorities as listed in paragraph (l)(5)(iii) of this section. Persons lawfully engaged in hunting
or shooting activities must correctly identify their target before shooting in order to avoid illegally shooting a grizzly
bear. Shooting a grizzly bear as a result of mistaking it for another species is considered a lack of reasonable due
care. The act of taking a grizzly bear that is wrongly identified as another species may be referred to appropriate
authorities for prosecution.
(ii) Any person with a valid permit issued by us may take grizzly bears in the Experimental Population Area for
scientific purposes, the enhancement of propagation or survival of the species, zoological exhibition, and other
conservation purposes. Such permits must be consistent with the Act, with management plans adopted for the
nonessential experimental population, and with applicable State wildlife conservation laws and regulations.
(iii) You may take grizzly bears in the Experimental Population Area in self-defense or in defense of the lives of
others. Such taking must be reported within 24 hours as to date, exact location, and circumstances to the Grizzly
Bear Recovery Coordinator, University Hall, Room 309, University of Montana, Missoula, Montana 59812 (406243-4903); or the Assistant Regional Director for Law Enforcement, Eastside Federal Complex, 911 NE 11th
Avenue, Portland, Oregon 97232-4181 (503-231-6125); or the Assistant Regional Director for Law Enforcement,
P.O. Box 25486, DFC, Denver, Colorado 80225 (303-236-7540); and either the Idaho Department of Fish and
Game, P.O. Box 25, Boise Idaho 83707 (208-334-3700); or the Montana Department of Fish, Wildlife and Parks,
1420 E. Sixth Avenue, Helena, Montana 59620 (406-444-2535); and Nez Perce Tribal authorities (208-843-2253)
(as appropriate).
(iv) Livestock owners may obtain a permit from the Service, and the Idaho Department of Fish and Game, the
Montana Department of Fish, Wildlife and Parks, or appropriate Tribal authorities to harass (see definition in §17.3)
grizzly bears found in the Experimental Population Area that are actually pursuing or killing livestock (to include
permitting the use of livestock guard dogs around livestock to harass such grizzly bears). Prior to issuance of such
a permit, authorized State, Federal, or Tribal officials must document pursuit or killing of livestock. All such
harassment must be accomplished by an opportunistic, noninjurious method (see definition of “opportunistic,
noninjurious harassment” in paragraph (l)(16) of this section) to the grizzly bear, and such harassment must be
reported within 24 hours as to date, exact location, and circumstances to the authorities listed under paragraph (l)
(5)(iii) of this section.
(v) Livestock owners may obtain a permit from the Service, and the Idaho Department of Fish and Game, the
Montana Department of Fish, Wildlife and Parks or appropriate Tribal authorities to take grizzly bears on private
lands found in the Experimental Population Area in a manner other than harassment as defined in this paragraph
(l), in order to protect livestock actually pursued or being killed on private property. Prior to issuance of such a
permit, authorized State, Federal, or Tribal officials must document pursuit or killing of livestock. Any response
protocol established by the Committee must have been satisfied and efforts to capture depredating grizzly bears
by Service or State or Tribal wildlife agency personnel must have proven unsuccessful. All such taking must be
reported as to date, exact location, and circumstances within 24 hours to the authorities listed under paragraph (l)
(5)(iii) of this section.
(vi) Any authorized employee or agent of the Service or appropriate State wildlife agency or Nez Perce Tribe who
is lawfully designated for such purposes, when acting in the course of official duties, may take a grizzly bear from
the wild in the Experimental Population Area if such action is necessary to:
(A) Aid a sick, injured, or orphaned grizzly bear;
(B) Dispose of a dead grizzly bear, or salvage a dead grizzly bear that may be useful for scientific study;
(C) Take a grizzly bear that constitutes a demonstrable but nonimmediate threat to human safety or that is
responsible for depredations to lawfully present domestic animals or other personal property, if otherwise
eliminating such depredation or loss of personal property has not been possible, and after eliminating such threat
by live-capturing and releasing the grizzly bear unharmed in the area defined in paragraph (l)(2) of this section or
other areas approved by the Committee has been demonstrated not to be possible;
(D) Move a grizzly bear for genetic management purposes;
(E) Relocate grizzly bears within the Experimental Population Area to improve grizzly bear survival and recovery
prospects; or (F) Relocate a grizzly bear to avoid conflict with human activities. However, grizzly bears in the
Experimental Population Area will not be disturbed unless they demonstrate a real and imminent threat to human
safety, livestock, or bees. Unless the Committee determines otherwise, this rule provides that on private lands
outside the national forest boundary in the Bitterroot Valley, Montana (exclusion area), any human/grizzly conflicts
will be considered unacceptable. Grizzly bear occupancy will be discouraged in the exclusion area, and grizzly
bears found there will be captured and returned to the Recovery Area, or placed in captivity, or destroyed,
depending on the history of each bear. If a grizzly bear enters the exclusion area, State and Federal wildlife
management agencies will attempt to capture it immediately and notify the public of its presence as soon as
possible. The public will be kept updated until the bear is caught. Further, any grizzly bear that occupies inhabited
human settlement areas on private land within the Experimental Population Area that, in the judgment of the
management agencies or Committee, presents a clear threat to human safety or whose behavior indicates that it
may become habituated to humans, will be relocated or destroyed by management agencies.
(6) How will local citizens be involved in the management of the Bitterroot nonessential experimental grizzly bear
population? (i) The Secretary will establish a Citizen Management Committee for the Bitterroot grizzly bear
experimental population and will authorize management implementation responsibility as described in paragraph
(l)(9) of this section, in consultation with the Governors of Idaho and Montana. As soon as possible after the
effective date of this rule, the Secretary will organize the Committee by requesting nominations of citizen members
from the Governors of Idaho and Montana and the Nez Perce Tribe and nominations of agency members by
represented agencies.
(ii) The Committee will be composed of 15 members serving 6-year terms. Appointments may initially be of lesser
terms to ensure staggered replacement.
(A) Membership will consist of seven individuals appointed by the Secretary based upon the recommendations of
the Governor of Idaho, five members appointed by the Secretary based upon the recommendations of the
Governor of Montana, one member representing the Nez Perce Tribe appointed by the Secretary based on the
recommendation of the Nez Perce Tribe, one member representing the Forest Service appointed by the Secretary
of Agriculture, and one member representing the Fish and Wildlife Service appointed by the Secretary. Members
recommended by the Governors of Idaho and Montana will be based on the recommendations of interested
parties and will include at least one representative each from the appropriate State wildlife agencies. If either
Governor or the Tribe fails to make recommendations within 60 days, the Secretary (or his/her designee) will
accept recommendations from interested parties, and will make the appointments.
(B) The Committee will consist of a cross-section of interests reflecting a balance of viewpoints, and members are
to be selected for their diversity of knowledge and experience in natural resource issues, and for their commitment
to collaborative decision-making. In their recommendations to the Secretary, the Governors of Idaho and Montana
will attach written documentation of the qualifications of those nominated relating to their knowledge of, and
experience in, natural resource issues and their commitment to collaborative decision-making.
(C) Except for the representatives from Federal agencies, the Committee will be selected from communities within
and adjacent to the Recovery and Experimental Population Areas.
(D) The Secretary will fill vacancies as they occur with the appropriate members based on the recommendation of
the appropriate Governor, the Nez Perce Tribe, or agency.
(7) Will independent scientific information be readily available to the Committee? The Secretary will appoint two
scientific advisors to the Committee as nonvoting members to attend all meetings of the Committee and to provide
scientific expertise to the Committee. These scientific advisors will not be employed by Federal agencies involved
in grizzly bear recovery. The Secretary will contact the Wildlife Society Chapters in Idaho and Montana and the
Universities of Idaho and Montana for nominations and will select one wildlife scientist representing each State
and appoint them as advisors to the Committee.
(8) What is the overall mission of the Committee, and how will it operate? (i) The mission of the Committee is to
facilitate recovery of the grizzly bear in the Bitterroot ecosystem by assisting in implementing the Bitterroot
ecosystem chapter of the recovery plan (Bitterroot Ecosystem Recovery Plan Chapter—Supplement to the Grizzly
Bear Recovery Plan, U.S. Fish and Wildlife Service, Missoula, Montana, 1996). The Committee will make
recommendations to land and wildlife management agencies that it believes will lead to recovery of the grizzly
bear. Decisions on, and implementation of, these recommendations are the responsibility of the land and wildlife
management agencies.
(ii) The Committee will meet a minimum of two times per year. These meetings will be open to the public.
Additionally, the committee will provide reasonable public notice of meetings, produce and provide written minutes
of meetings to interested persons, and involve the public in its decision-making process. This public participation
process will allow members of the public and/or special interest groups to have input to Committee decisions and
management actions.
(9) What authority will the Committee have, and what will be its primary tasks? The Committee will have the
authority and the responsibility to carry out the following functions:
(i) Developing a process for obtaining the best biological, social, and economic data. This process will include an
explicit mechanism for soliciting peer-reviewed, scientific articles on grizzly bears and their management, and
holding periodic public meetings not less than every 2 years, in which qualified scientists may submit comments to
and be questioned by the Committee. The two scientific advisors will lead this process. The Committee will base
its decisions upon the best scientific and commercial data available. All decisions of the Committee, including
components of its management plans, must lead toward recovery of the grizzly bear in the Bitterroot ecosystem
and minimize social and economic impacts to the extent practicable within the context of the existing recovery
goals for the species.
(ii) Soliciting technical advice and guidance from outside experts. The scientific advisors will lead the development
of an ongoing process to provide the Committee with the best scientific and commercial data available. The
scientific advisors will provide this information in the form of peer-reviewed scientific articles on grizzly bears and
their management, Committee meetings with presentations by scientific experts, and requests to State and
Federal management agencies and the private sector for scientific expertise and advice.
(iii) Implementing the Bitterroot Ecosystem Chapter of the Grizzly Bear Recovery Plan consistent with this
paragraph (l). The Committee will develop recommendations on existing management plans and policies of land
and wildlife management agencies, as necessary, for the management of grizzly bears in the Experimental
Population Area. The Committee will make recommendations to land and wildlife management agencies regarding
changes to plans and policies, but the final decision on implementation of those recommendations will be made by
those agencies. If Committee recommendations require significant changes to existing plans and policy, and the
agencies tentatively agree to accept those recommendations, then the requirements of the National Environmental
Policy Act may apply. Such management plans and policies will be in accordance with applicable State and
Federal laws. The Committee will give full consideration to Service comments and opinions and those of the
Forest Service, Idaho Department of Fish and Game, the Montana Department of Fish, Wildlife and Parks, and the
Nez Perce Tribe.
(iv) Providing means by which the public may participate in, review, and comment on the decisions of the
Committee. The Committee must thoroughly consider and respond to public input prior to making decisions.
(v) Developing its internal processes, where appropriate, such as governance, decision-making, quorum, terms of
members, officers, meeting schedules and location, public notice of meetings, and minutes.
(vi) Requesting staff support from the Service, the Idaho Department of Fish and Game, Montana Department of
Fish, Wildlife and Parks, Forest Service, other affected Federal agencies, and the Nez Perce Tribe, when
necessary to perform administrative functions, and requesting reimbursement from us for non-Federal Committee
members for costs associated with travel, lodging, and incidentals.
(vii) Reviewing existing grizzly bear standards and guidelines used by the Forest Service and other agencies and
landowners. The Committee will perform an annual review of grizzly bear mortalities and the number and location
of bear/human conflicts. This review will be the primary mechanism to assess the adequacy of existing
management techniques and standards. If the Committee deems such standards and guidelines inadequate for
recovery of grizzly bears, the Committee may recommend changes to the Forest Service and other agencies and
landowners.
(viii) Developing grizzly bear guidance for proper camping and sanitation within the Experimental Population Area
and making recommendations to land management agencies for adoption of such guidelines. Existing camping
and sanitation procedures developed in other ecosystems with grizzly bears will serve as a basis for such
guidelines.
(ix) Developing a protocol for responding to grizzly/human encounters, livestock depredations, damage to lawfully
present property, and other grizzly/human conflicts within the Experimental Population Area. Any response
protocol developed by the Committee will have to undergo public comment and be revised as appropriate based
on comments received. Any conflicts or mortalities associated with these activities will result in review by the
Committee to determine what the Committee may do to help prevent future conflicts or mortalities. The Committee
will recommend, as necessary, policy changes on trail restrictions for human safety to appropriate wildlife and land
management agencies.
(x) Recommending to the Service changes to recovery criteria, including mortality limits, population
determinations, and other criteria for recovery as appropriate.
(xi) Reviewing all human-caused grizzly bear mortalities to determine whether new measures for avoiding future
occurrences are required and make recommendations on such measures to appropriate land and wildlife
management agencies. If grizzly bear mortalities occur as a result of black bear hunting, the Committee will work
with the State Fish and Game Departments in both Idaho and Montana to develop solutions to minimize the effects
on grizzly bears of black bear hunting.
(xii) Developing strategies to emphasize recovery inside the Recovery Area and to accommodate grizzly bears
inside other areas of the Experimental Population Area.
(A) Grizzly bears may range outside the Recovery Area because grizzly bear habitat exists throughout the
Experimental Population Area. The Committee will not recommend that bears be disturbed or moved unless
conflicts are both significant and cannot be corrected as determined by the Committee. This provision includes
conflicts associated with livestock, for which the Committee will develop strategies to discourage grizzly bear
occupancy in portions of the Experimental Population Area outside of the Recovery Area.
(B) Unless the Committee determines otherwise, this rule provides that private land outside the national forest
boundary in the Bitterroot Valley, Montana (exclusion area), is an area where any human/grizzly conflicts will be
considered unacceptable. Grizzly bear occupancy will be discouraged in these areas, and grizzly bears will be
captured and returned to the Recovery Area. If a grizzly bear enters the exclusion area, State and Federal wildlife
management agencies will attempt to capture it immediately and notify the public of its presence as soon as
possible. The public will be kept updated until the bear is caught. Further, any grizzly bear that occupies the
exclusion area or other inhabited human settlement areas on private land within the Experimental Population Area
that, in the judgment of the management agencies or Committee, presents a clear threat to human safety or
whose behavior indicates that it may become habituated to humans, will be relocated or destroyed by
management agencies.
(xiii) Establishing standards for determining whether the experimental reintroduction has been successful and
making recommendations on the inclusion of such standards in the Grizzly Bear Recovery Plan. These standards
will be based on the best scientific and commercial information available and will reflect that, absent extraordinary
circumstances, the success or failure of the program cannot be measured in fewer than 20 years. General
guidelines for the standards by which failure will be measured include, but are not limited to, one or more of the
following conditions:
(A) If, within the number of years established by the Committee following initial reintroduction, no relocated grizzly
bear remains within the Experimental Population Area and the reasons for emigration or mortality cannot be
identified and/or remedied; or
(B) If, within the number of years established by the Committee following initial reintroduction, no cubs of the year
or yearlings exist and the relocated bears are not showing signs of successful reproduction as evidenced by no
cubs of the year or yearlings.
(xiv) Developing procedures for the expeditious issuance of permits described in paragraphs (l)(5)(iv) and (l)(5)(v)
of this section, and making recommendations on such procedures to appropriate agencies.
(xv) Developing 2-year work plans for the recovery effort for submittal to the Secretary pursuant to paragraph (l)
(11)(i) of this section.
(xvi) Establishing, based on the best available science, a refined interim recovery goal for the Bitterroot Ecosystem
Chapter of the Grizzly Bear Recovery Plan and a final recovery goal when sufficient information is available and
after grizzly bears are reintroduced and occupy suitable habitats in the Experimental Population Area. As this
information becomes available, the Committee may recommend the recovery goal to the Secretary along with
procedures for determining how this goal will be measured. The recovery goal for the Bitterroot grizzly bear
population will be consistent with the habitat available within the Recovery Area. Additional adjacent areas of
public land can be considered for contribution of suitable habitat when setting the recovery goal if additional land is
shown to be necessary by the best scientific and commercial data available. Any recommendations for revised
recovery goals developed by the Committee will require public review and our approval as appropriate prior to
revision of any recovery plan. Grizzly bears outside the Recovery Area and within the Experimental Population
Area can contribute to meeting the recovery goal if their long-term occupancy in such habitats outside the
Recovery Area is reasonably certain.
(10) What agencies will be responsible for day-to-day management activities? The Idaho Department of Fish and
Game, the Montana Department of Fish, Wildlife and Parks, the Nez Perce Tribe, and the Forest Service, in
coordination with us, will exercise day-to-day management responsibility within the Experimental Population Area
in accordance with this paragaraph (l). The Service and these cooperating agencies will share management
responsibility as per agreements with, and in consideration of, recommendations from the Committee.
(11) How will progress of the Committee be monitored; and what process will be followed by the Secretary to
resolve disputes over whether Committee actions are leading to recovery? (i) The Secretary or our representative
on the Committee will review the Committee's 2-year work plans (see paragraph (l)(9)(xv) of this section). If the
Secretary determines, through our representative on the Committee, that the Committee's decisions, work plans,
or the implementation of those plans are not leading to the recovery of the grizzly bear within the Experimental
Population Area or are not in compliance with this paragraph (l), our representative will ask the Committee to
determine whether such a decision, plan, or implementation of a plan is leading to recovery and is in compliance
with this paragraph (l). The Secretary, who retains final responsibility and authority for implementation of the Act,
will review the Committee's determination, as provided in paragraphs (l)(11)(ii) through (iv) of this section, and then
make a final determination. Should the Secretary find that a decision, work plan, or implementation of a plan by the
Committee is inadequate for recovery of the grizzly bear or is not in compliance with this paragraph (l), the
Secretary may assume lead management responsibility.
(ii) The Service representative will consider Committee input before making any determination that Committee
actions are not leading to recovery or are not in compliance with this paragraph (l). In the event that our
representative on the Committee determines that the actions of the Committee are not leading to recovery of the
Bitterroot grizzly bear population or are not in compliance with this paragraph (l), he or she will recommend to the
Committee, based on the best scientific and commercial data available, alternative or corrective actions and
provide 6 months for the Committee to accomplish those actions. Should the Committee reject these corrective
actions, our representative will convene a Scientific Review Panel of three and will submit to the panel for review
those Committee actions or decisions that he or she has determined are not leading to recovery or are not in
compliance with this paragrpah (l). The Service representative will consider the views of all Committee members
prior to convening a Scientific Review Panel.
(iii) Members of the Scientific Review Panel will be professional scientists who have had no involvement with the
Committee and are not employed by Federal agencies responsible for grizzly bear recovery efforts. The Secretary
will select one member of the panel, and the Governors of Idaho and Montana in consultation with the Universities
of Idaho and Montana (respectively), will select one panel member each. The Scientific Review Panel will review
Committee actions or decisions, solicit additional information if necessary and, using the best scientific and
commercial data available, make timely recommendations to the Committee as to whether Committee actions will
lead to recovery of the grizzly bear in the Bitterroot ecosystem and are in compliance with paragraph (l). Examples
of Committee actions, decisions, or lack of actions that can be submitted to the Scientific Review Panel include,
but are not limited to, the following: sufficiency of public involvement in Committee activities; decisions involving
sanitation and outreach activities; management of nuisance bears; adequacy of recommendations to land and
wildlife management agencies; adequacy of Committee actions in addressing issues such as excessive humancaused grizzly bear mortality; and other actions important to recovery of the grizzly bear in the Bitterroot
ecosystem. Committee compliance with paragraph (l) provides the basis for the recommendations of the Scientific
Review Panel.
(iv) If, after timely review, the Committee rejects the recommendations of the Scientific Review Panel, and our
representative determines that Committee actions are not leading to recovery of the Bitterroot population, he or
she will notify the Secretary. The Secretary will review the Panel's recommendations and determine the disposition
of the Committee.
(A) If the Secretary determines that the Committee should maintain lead management responsibility, the
Committee will continue to operate according to the provisions of this paragraph (l) until the recovery objectives
under paragraph (l)(9)(xvi) of this section or the Bitterroot Ecosystem Chapter of the Recovery Plan have been met
and the Secretary has completed delisting.
(B) If the Secretary decides to assume lead management responsibility, the Secretary will consult with the
Governors of Idaho and Montana regarding that decision and further attempt to resolve the disagreement. If, after
such consultation, the Secretary assumes lead management responsibility, the Secretary will publish a notice in
the Federal Register explaining the rationale for the determination and notify the Governors of Idaho and Montana.
The Committee will disband, and all requirements identified in this paragraph (l) regarding the Committee will be
nullified.
(12) How will the Bitterroot grizzly bear population be monitored? The reintroduced population will be monitored
closely by Federal and State agencies in cooperation with the Committee for the duration of the recovery process,
generally by use of radio telemetry as appropriate.
(13) How will success or failure of the project be evaluated? The status of Bitterroot grizzly bear recovery will be
reevaluated separately by the Committee and by the Secretary at 5-year intervals. This review will take into
account the reproductive success of the grizzly bears released, human-caused mortality, movement patterns of
individual bears, food habits, and overall health of the population and will recommend changes and improvements
in the recovery program. Evaluating these parameters will assist in determining success or failure of the
restoration.
(14) What process will be followed if the Secretary determines the project has failed? (i) If, based on the criteria
established by the Committee, the Secretary, after consultation with the Committee, the Governors of Idaho and
Montana, the Idaho Department of Fish and Game, the Montana Department of Fish, Wildlife and Parks, and the
Nez Perce Tribe, determines that the reintroduction has failed to produce a self-sustaining population, this
paragraph (l) will not be used to reintroduce additional bears. Any remaining bears will retain their experimental
status.
(ii) Prior to declaring the experimental reintroduction a failure, we will investigate the probable causes of the failure.
If the causes can be determined, and legal and reasonable remedial measures identified and implemented, we will
consider continuing the recovery effort and maintaining the relocated population. If such reasonable measures
cannot be identified and implemented, we will publish the results of our evaluation in the Federal Register in a
proposed rulemaking to terminate the authority for additional experimental grizzly bear reintroductions in the
Bitterroot ecosystem.
(15) Will the legal status of grizzly bears in the Experimental Population Area change? We do not intend to change
the “nonessential experimental” designation to “essential experimental,” “threatened,” or “endangered” and foresee
no likely situation that would result in such changes. Critical habitat cannot be designated under the nonessential
experimental classification, 16 U.S.C. 1539(j)(2)(C)(ii).
(16) What are the definitions of key terms used in the special rule in this paragraph (l)? In addition to terms defined
in §10.12 and 17.3 of this subchapter, the following terms apply to this paragraph (l):
Accommodate means allowing grizzly bears that move outside the Recovery Area onto public land in the
Experimental Population Area to remain undisturbed unless they demonstrate a real and imminent threat to human
safety or livestock.
Citizen Management Committee (Committee) means that Committee described in paragraph (l)(6) of this section.
Current range means the area inside or within 10 miles of the recovery zone line of currently occupied grizzly bear
recovery zones or any area where there is a grizzly bear population, as defined in this paragraph (l)(16).
Exclusion area (Bitterroot Valley) means those private lands in Montana lying within the Bitterroot Experimental
Population Area in the Bitterroot Valley outside the Bitterroot National Forest boundary south of U.S. Highway 12
to Lost Trail Pass and west of Highway 93.
Experimental Population Area (Bitterroot Grizzly Bear Experimental Population Area) means that area delineated
in paragraph (l)(1) of this section within which management plans developed as part of the Committee described in
paragraph (l)(9) of this section will be in effect. This area includes the Recovery Area. The Experimental
Population Area is within the historic range of the grizzly bear, but geographically separate from the current range
of the grizzly bear.
Geographically separate means separated by more than 10 miles. The term refers to “wholly separate
geographically” in section 10(j)(2) of the Act. The Experimental Population Area and the recovery zone boundary
of any existing grizzly bear population must be geographically separate.
Grizzly bear population is defined by verified evidence within the previous 6 years which consists of photos within
the area, verified tracks, or sightings by reputable scientists or agency personnel of at least two different female
grizzly bears with young or one female with different litters in 2 different years in an area geographically separate
from other grizzly bear populations. Verifiable evidence of females with young, to be geographically separate,
would have to occur greater than 10 miles from the nearest nonexperimental grizzly bear population recovery zone
boundary.
Opportunistic, noninjurious harassment means harassment (see definition of “harass” in §17.3) that occurs when
the grizzly bear presents itself (for example, the bear travels onto and is observed on private land or near
livestock). This paragraph (l) permits only this type of harassment. You cannot track, attract, search out, or chase a
grizzly bear and then harass it. Any harassment must not cause bodily injury or death to the grizzly bear. The
intent of harassment permitted by this definition is to scare bears away from the immediate area.
Recovery Area (Bitterroot Grizzly Bear Recovery Area) means the area of recovery emphasis within the
Experimental Population Area, and is delineated in paragraph (l)(2) of this section. This area consists of the
Selway-Bitterroot and Frank Church-River of No Return Wilderness areas. The Recovery Area is within the historic
range of the species.
Recovery emphasis means grizzly bear management decisions in the Recovery Area will favor bear recovery so
that this area can serve as core habitat for survival, reproduction, and dispersal of the recovering population.
Reintroduction of grizzly bears is planned to occur within the Selway-Bitterroot Wilderness portion of the Recovery
Area unless it is later determined that reintroduction in the Frank Church-River of No Return Wilderness is
appropriate.
Unavoidable and unintentional take means accidental, unintentional take (see definition of take in §10.12 of this
subchapter) that occurs despite reasonable care, is incidental to an otherwise lawful activity, and is not done on
purpose. An example would be striking a grizzly bear with an automobile. Taking a grizzly bear by shooting will not
be considered unavoidable and unintentional take. Shooters have the responsibility to be sure of their targets.
eCFR graphic er17no00.008.gif
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(m) Spotfin chub (=turquoise shiner) (Erimonax monachus)—(1) Where is the spotfin chub designated as a
nonessential experimental population (NEP)? We have designated three populations of this species as NEPs: the
Tellico River NEP, the Shoal Creek NEP, and the French Broad River and Holston River NEP. This species is not
currently known to exist in the Tellico River or its tributaries, the Shoal Creek or its tributaries, or any of the
tributaries to the free-flowing reaches of the French Broad River below Douglas Dam, Knox and Sevier Counties,
Tennessee, or of the Holston River below the Cherokee Dam, Knox, Grainger, and Jefferson Counties, Tennessee.
Based on its habitat requirements, we do not expect this species to become established outside the NEP areas.
However, if individuals move upstream or downstream or into tributaries outside any of the designated NEP areas,
we would presume that those individuals came from the closest reintroduced population. We would then amend
this regulation and enlarge the boundaries of the NEP area to include the entire range of the expanded population.
(i) The Tellico River NEP area is within the species' probable historic range and is defined as follows: The Tellico
River, between the backwaters of the Tellico Reservoir (approximately Tellico River mile 19 (30.4 kilometers (km))
and Tellico River mile 33 (52.8 km), near the Tellico Ranger Station, Monroe County, Tennessee.
(ii) The Shoal Creek NEP area is within the species' historic range and is defined as follows: Shoal Creek (from
Shoal Creek mile 41.7 (66.7 km)) at the mouth of Long Branch, Lawrence County, TN, downstream to the
backwaters of Wilson Reservoir (Shoal Creek mile 14 (22 km)) at Goose Shoals, Lauderdale County, AL, including
the lower 5 miles (8 km) of all tributaries that enter this reach.
(iii) The French Broad River and Holston River NEP area is within the species' historic range and is defined as
follows: the French Broad River, Knox and Sevier Counties, Tennessee, from the base of Douglas Dam (river mile
(RM) 32.3 (51.7 km)) downstream to the confluence with the Holston River; then up the Holston River, Knox,
Grainger, and Jefferson Counties, Tennessee, to the base of Cherokee Dam (RM 52.3 (83.7 km)); and the lower 5
RM (8 km) of all tributaries that enter these river reaches.
(iv) We do not intend to change the NEP designations to “essential experimental,” “threatened,” or “endangered”
within the NEP area. Additionally, we will not designate critical habitat for these NEPs, as provided by 16 U.S.C.
1539(j)(2)(C)(ii).
(2) What activities are not allowed in the NEP area? (i) Except as expressly allowed in paragraph (m)(3) of this
section, all the provisions of §17.31(a) and (b) apply to the spotfin chub.
(ii) Any manner of take not described under paragraph (m)(3) of this section is prohibited in the NEP area. We may
refer unauthorized take of this species to the appropriate authorities for prosecution.
(iii) You may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any of the
identified fishes, or parts thereof, that are taken or possessed in violation of paragraph (m)(2) of this section or in
violation of the applicable State fish and wildlife laws or regulations or the Act.
(iv) You may not attempt to commit, solicit another to commit, or cause to be committed any offense defined in
paragraph (m)(2) of this section.
(3) What take is allowed in the NEP area? Take of this species that is accidental and incidental to an otherwise
legal activity, such as recreation (e.g., fishing, boating, wading, trapping, or swimming), forestry, agriculture, and
other activities that are in accordance with Federal, State, and local laws and regulations, is allowed.
(4) How will the effectiveness of these reintroductions be monitored? (i) In the Tellico River NEP area, we will
prepare periodic progress reports and fully evaluate these reintroduction efforts after 5 and 10 years to determine
whether to continue or terminate the reintroduction efforts.
(ii) In the Shoal Creek NEP area, after the initial stocking of fish, we will monitor annually their presence or
absence and document any spawning behavior or young-of-the-year fish that might be present. This monitoring
will be conducted primarily by snorkeling or seining and will be accomplished by contracting with the appropriate
species experts. We will produce annual reports detailing the stocking rates and monitoring activities that took
place during the previous year. We will also fully evaluate these reintroduction efforts after 5 and 10 years to
determine whether to continue or terminate the reintroduction efforts.
(iii) In the Lower French Broad and Lower Holston Rivers NEP area, after the initial stocking of these species, we
will monitor annually their presence or absence and document any spawning behavior or young-of-the-year that
might be present. This monitoring will be conducted primarily by snorkeling or seining and will be accomplished by
contracting with the appropriate species experts. Annual reports will be produced detailing the stocking rates and
monitoring activities that took place during the previous year. We will also fully evaluate these reintroduction efforts
after 5 and 10 years to determine whether to continue or terminate the reintroduction efforts.
(5) Note: Map of the Tellico River NEP area for spotfin chub, dusky darter, smoky madtom, and yellowfin madtom
in Tennessee follows:
eCFR graphic er13se07.000.gif
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(6) Note: Map of the Shoal Creek NEP area for spotfin chub and boulder darter in Tennessee and Alabama
follows:
eCFR graphic er13se07.001.gif
View or download PDF
(7) Note: Map of the French Broad River and Holston River NEP area for spotfin chub, slender chub, duskytail
darter, pygmy madtom, and yellowtail madtom in Tennessee follows:
eCFR graphic er13se07.002.gif
View or download PDF
(n) [Reserved]
(o) Boulder darter (Etheostoma wapiti). (1) Where is the boulder darter designated as a nonessential experimental
population (NEP)? (i) The NEP area for the boulder darter is within the species' historic range and is defined as
follows: Shoal Creek (from Shoal Creek mile 41.7 (66.7 km)) at the mouth of Long Branch, Lawrence County, TN,
downstream to the backwaters of Wilson Reservoir (Shoal Creek mile 14 (22 km)) at Goose Shoals, Lauderdale
County, AL, including the lower 5 miles (8 km) of all tributaries that enter this reach.
(ii) The boulder darter is not currently known to exist in Shoal Creek or its tributaries. Based on the habitat
requirements of this fish, we do not expect it to become established outside the NEP area. However, if any
individuals of the species move upstream or downstream or into tributaries outside the designated NEP area, we
would presume that they came from the reintroduced population. We would then amend this rule through our
normal rulemaking process in order to enlarge the boundaries of the NEP area to include the entire range of the
expanded population.
(iii) We do not intend to change the NEP designations to “essential experimental,” “threatened,” or “endangered”
within the NEP area. Additionally, we will not designate critical habitat for these NEPs, as provided by 16 U.S.C.
1539(j)(2)(C)(ii).
(2) What activities are not allowed in the NEP area? (i) Except as expressly allowed in paragraph (o)(3) of this
section, all the provisions of §17.31(a) and (b) apply to the boulder darter.
(ii) Any manner of take not described under paragraph (o)(3) of this section is prohibited in the NEP area. We may
refer unauthorized take of these species to the appropriate authorities for prosecution.
(iii) You may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any of the
identified fishes, or parts thereof, that are taken or possessed in violation of paragraph (o)(2) of this section or in
violation of the applicable State fish and wildlife laws or regulations or the Act.
(iv) You may not attempt to commit, solicit another to commit, or cause to be committed any offense defined in
paragraph (o)(2) of this section.
(3) What take is allowed in the NEP area? Take of this species that is accidental and incidental to an otherwise
legal activity, such as recreation (e.g., fishing, boating, wading, trapping, or swimming), forestry, agriculture, and
other activities that are in accordance with Federal, State, and local laws and regulations, is allowed.
(4) How will the effectiveness of these reintroductions be monitored? After the initial stocking of fish, we will
monitor annually their presence or absence and document any spawning behavior or young-of-the-year fish that
might be present. This monitoring will be conducted primarily by snorkeling or seining and will be accomplished by
contracting with the appropriate species experts. We will produce annual reports detailing the stocking rates and
monitoring activities that took place during the previous year. We will also fully evaluate these reintroduction efforts
after 5 and 10 years to determine whether to continue or terminate the reintroduction efforts.
(5) Note: Map of the NEP area for the boulder darter in the Shoal Creek, Tennessee and Alabama, appears
immediately following paragraph (m)(6) of this section.
(p) Northern aplomado falcon (Falco femoralis septentrionalis). (1) The northern aplomado falcon (Falco femoralis
septentrionalis) (falcon) population identified in paragraph (p)(9)(i) of this section is a nonessential experimental
population (NEP).
(2) No person may take this species, except as provided in paragraphs (p)(3) through (5) and (p)(10) of this
section.
(3) Any person with a valid permit issued by the U.S. Fish and Wildlife Service (Service) under §17.32 may take
falcons for educational purposes, scientific purposes, the enhancement of propagation or survival of the species,
zoological exhibition, and other conservation purposes consistent with the Endangered Species Act (Act);
(4) A falcon may be taken within the NEP area, provided that such take is not willful, knowing, or due to
negligence, or is incidental to and not the purpose of the carrying out of an otherwise lawful activity; and that such
taking is reported within 24 hours, as provided under paragraph (p)(6) of this section.
(5) Any employee of the Service, New Mexico Department of Game and Fish, or Arizona Game and Fish
Department, who is designated for such purpose, or any person with a valid permit issued by the Service under 50
CFR 17.32, may, when acting in the course of official duties, take a falcon if such action is necessary to:
(i) Aid a sick, injured, or orphaned specimen;
(ii) Dispose of a dead specimen, or salvage a dead specimen that may be useful for scientific study;
(iii) Move a bird within the NEP area for genetic purposes or to improve the health of the population;
(iv) Relocate falcons that have moved outside the NEP area, by returning the falcon to the NEP area or moving it
to a captive breeding facility. All captures and relocations from outside the NEP area will be conducted with the
permission of the landowner(s) or appropriate land management agencies; or
(v) Collect nesting data or band individuals.
(6) Any taking pursuant to paragraphs (p)(3) through (5) of this section must be reported within 24 hours by
contacting the U.S. Fish and Wildlife Service, New Mexico Ecological Services Field Office, 2105 Osuna NE,
Albuquerque, NM 87113; (505) 346-2525. Upon contact, a determination will be made as to the disposition of any
live or dead specimens.
(7) No person shall possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever, any
such species taken in violation of these regulations.
(8) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (p)(2) and (p)(7) of this section.
(9)(i) The boundaries of the designated NEP area are based on county borders and include the entire States of
New Mexico and Arizona. The reintroduction area is within the historical range of the species in New Mexico.
(ii) All falcons found in the wild within the boundaries of the NEP area after the first releases will be considered
members of the NEP. A falcon occurring outside of the NEP area is considered endangered under the Act unless it
is marked or otherwise known to be a member of the NEP.
(iii) The Service has designated the NEP area to accommodate the potential future movements of a wild
population of falcons. All released birds and their progeny are expected to remain in the NEP area due to the
geographic extent of the designation.
(10) The NEP will be monitored closely for the duration of the reintroduction program. Any bird that is determined
to be sick, injured, or otherwise in need of special care will be recaptured to the extent possible by Service and/or
State or permitted Tribal wildlife personnel and given appropriate care. Such birds will be released back to the wild
as soon as possible, unless physical or behavioral problems make it necessary to return them to a captivebreeding facility or they are euthanized if treatment would be unlikely to be effective.
(11) The Service plans to evaluate the status of the NEP every 5 years to determine future management status
and needs, with the first evaluation expected to be not more than 5 years after the first release of birds into the
NEP area. All reviews will take into account the reproductive success and movement patterns of individuals
released, food habits, and overall health of the population. This evaluation will include a progress report.
(q) Duskytail darter (Etheostoma percnurum). (1) Where is the duskytail darter designated as a nonessential
experimental population (NEP)? We have designated two populations of this species as NEPs: The Tellico River
NEP and the French Broad River and Holston River NEP. This species is not currently known to exist in the Tellico
River or its tributaries or in any of the tributaries to the free-flowing reaches of the French Broad River below
Douglas Dam, Knox and Sevier Counties, Tennessee, or of the Holston River below the Cherokee Dam, Knox,
Grainger, and Jefferson Counties, Tennessee. Based on its habitat requirements, we do not expect this species to
become established outside these NEP areas. However, if individuals move upstream or downstream or into
tributaries outside either of the designated NEP areas, we would presume that these individuals came from the
reintroduced population. We would then amend this rule and enlarge the boundaries of the NEP area to include
the entire range of the expanded population.
(i) The Tellico River NEP area is within the species' historic range and is defined as follows: The Tellico River,
between the backwaters of the Tellico Reservoir (approximately Tellico River mile 19 (30.4 kilometers) and Tellico
River mile 33 (52.8 kilometers), near the Tellico Ranger Station, Monroe County, Tennessee.
(ii) The French Broad River and Holston River NEP area is within the species' historic range and is defined as
follows: the French Broad River, Knox and Sevier Counties, Tennessee, from the base of Douglas Dam (river mile
(RM) 32.3 (51.7 km)) downstream to the confluence with the Holston River; then up the Holston River, Knox,
Grainger, and Jefferson Counties, Tennessee, to the base of Cherokee Dam (RM 52.3 (83.7 km)); and the lower 5
RM (8 km) of all tributaries that enter these river reaches.
(iii) We do not intend to change the NEP designations to “essential experimental,” “threatened,” or “endangered”
within the NEP area. Additionally, we will not designate critical habitat for these NEPs, as provided by 16 U.S.C.
1539(j)(2)(C)(ii).
(2) What activities are not allowed in the NEP area? (i) Except as expressly allowed in paragraph (q)(3) of this
section, all the prohibitions of §17.31(a) and (b) apply to the duskytail darter.
(ii) Any manner of take not described under paragraph (q)(3) of this section is prohibited in the NEP area. We may
refer unauthorized take of this species to the appropriate authorities for prosecution.
(iii) You may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any of the
identified fishes, or parts thereof, that are taken or possessed in violation of paragraph (q)(2) of this section or in
violation of the applicable State fish and wildlife laws or regulations or the Act.
(iv) You may not attempt to commit, solicit another to commit, or cause to be committed any offense defined in
paragraph (q)(2) of this section.
(3) What take is allowed in the NEP area? Take of this species that is accidental and incidental to an otherwise
legal activity, such as recreation (e.g., fishing, boating, wading, trapping, or swimming), forestry, agriculture, and
other activities that are in accordance with Federal, State, and local laws and regulations, is allowed.
(4) How will the effectiveness of these reintroductions be monitored? We will prepare periodic progress reports and
fully evaluate these reintroduction efforts after 5 and 10 years to determine whether to continue or terminate the
reintroduction efforts.
(5) Note: Map of the NEP area for the duskytail darter in the Tellico River, Tennessee, appears immediately
following paragraph (m)(5) of this section.
(6) Note: Map of the NEP area for the duskytail darter in the French Broad River and Holston River, Tennessee,
appears immediately following paragraph (m)(7) of this section.
(r) Smoky madtom (Noturus baileyi). (1) Where is the smoky madtom designated as a nonessential experimental
population (NEP)?
(i) The NEP area for the smoky madtom is within the species' probable historic range and is defined as follows:
The Tellico River, between the backwaters of the Tellico Reservoir (approximately Tellico River mile 19 (30.4
kilometers) and Tellico River mile 33 (52.8 kilometers), near the Tellico Ranger Station, Monroe County,
Tennessee.
(ii) The smoky madtom is not currently known to exist in the Tellico River or its tributaries. Based on the habitat
requirements of this fish, we do not expect it to become established outside the NEP area. However, if any
individuals of the species move upstream or downstream or into tributaries outside the designated NEP area, we
would presume that they came from the reintroduced population. We would then amend paragraph (r)(1)(i) of this
section and enlarge the boundaries of the NEP area to include the entire range of the expanded population.
(iii) We do not intend to change the NEP designations to “essential experimental,” “threatened,” or “endangered”
within the NEP area. Additionally, we will not designate critical habitat for this NEP, as provided by 16 U.S.C.
1539(j)(2)(C)(ii).
(2) What activities are not allowed in the NEP area? (i) Except as expressly allowed in paragraph (r)(3) of this
section, all the prohibitions of §17.31(a) and (b) apply to the smoky madtom.
(ii) Any manner of take not described under paragraph (r)(3) of this section is prohibited in the NEP area. We may
refer unauthorized take of this species to the appropriate authorities for prosecution.
(iii) You may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any of the
identified fishes, or parts thereof, that are taken or possessed in violation of paragraph (r)(2) of this section or in
violation of the applicable State fish and wildlife laws or regulations or the Act.
(iv) You may not attempt to commit, solicit another to commit, or cause to be committed any offense defined in
paragraph (r)(2) of this section.
(3) What take is allowed in the NEP area? Take of this species that is accidental and incidental to an otherwise
legal activity, such as recreation (e.g., fishing, boating, wading, trapping, or swimming), forestry, agriculture, and
other activities that are in accordance with Federal, State, and local laws and regulations, is allowed.
(4) How will the effectiveness of these reintroductions be monitored? We will prepare periodic progress reports and
fully evaluate these reintroduction efforts after 5 and 10 years to determine whether to continue or terminate the
reintroduction efforts.
(5) Note: Map of the NEP area for the smoky madtom in the Tellico River, Tennessee, appears immediately
following paragraph (m)(6) of this section.
(s) Slender chub (Erimystax cahni). (1) Where is the slender chub designated as a nonessential experimental
population (NEP)?
(i) The NEP area for the slender chub is within the species' historic range and is defined as follows: the French
Broad River, Knox and Sevier Counties, Tennessee, from the base of Douglas Dam (river mile (RM) 32.3 (51.7
km)) downstream to the confluence with the Holston River; then up the Holston River, Knox, Grainger, and
Jefferson Counties, Tennessee, to the base of Cherokee Dam (RM 52.3 (83.7 km)); and the lower 5 RM (8 km) of
all tributaries that enter these river reaches.
(ii) The slender chub is not known to exist in any of the tributaries to the free-flowing reaches of the French Broad
River below Douglas Dam, Knox and Sevier Counties, Tennessee, or of the Holston River below the Cherokee
Dam, Knox, Grainger, and Jefferson Counties, Tennessee. Based on its habitat requirements, we do not expect
this species to become established outside this NEP area. However, if individuals of this population move
upstream or downstream or into tributaries outside the designated NEP area, we would presume that they came
from the reintroduced population. We would then amend this regulation to enlarge the boundaries of the NEP area
to include the entire range of the expanded population.
(iii) We do not intend to change the NEP designations to “essential experimental,” “threatened,” or “endangered”
within the NEP area. Additionally, we will not designate critical habitat for this NEP, as provided by 16 U.S.C.
1539(j)(2)(C)(ii).
(2) What activities are not allowed in the NEP area? (i) Except as expressly allowed in paragraph (s)(3) of this
section, all the prohibitions of §17.31(a) and (b) apply to the slender chub.
(ii) Any manner of take not described under paragraph (s)(3) of this section is prohibited in the NEP area. We may
refer unauthorized take of this species to the appropriate authorities for prosecution.
(iii) You may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any of the
identified fishes, or parts thereof, that are taken or possessed in violation of paragraph (s)(2) of this section or in
violation of the applicable State fish and wildlife laws or regulations or the Act.
(iv) You may not attempt to commit, solicit another to commit, or cause to be committed any offense defined in
paragraph (s)(2) of this section.
(3) What take is allowed in the NEP area? Take of this species that is accidental and incidental to an otherwise
legal activity, such as recreation (e.g., fishing, boating, wading, trapping, or swimming), forestry, agriculture, and
other activities that are in accordance with Federal, State, and local laws and regulations, is allowed.
(4) How will the effectiveness of these reintroductions be monitored? We will prepare periodic progress reports and
fully evaluate these reintroduction efforts after 5 and 10 years to determine whether to continue or terminate the
reintroduction efforts.
(5) Note: Map of the NEP area for the slender chub in the French Broad River and Holston River, Tennessee,
appears immediately following paragraph (m)(7) of this section.
(t) Pygmy madtom (Noturus stanauli). (1) Where is the pygmy madtom designated as a nonessential experimental
population (NEP)?
(i) The NEP area for the pygmy madtom is within the species' historic range and is defined as follows: the French
Broad River, Knox and Sevier Counties, Tennessee, from the base of Douglas Dam (river mile (RM) 32.3 (51.7
km)) downstream to the confluence with the Holston River; then up the Holston River, Knox, Grainger, and
Jefferson Counties, Tennessee, to the base of Cherokee Dam (RM 52.3 (83.7 km)); and the lower 5 RM (8 km) of
all tributaries that enter these river reaches.
(ii) The pygmy madtom is not known to exist in any of the tributaries to the free-flowing reaches of the French
Broad River below Douglas Dam, Knox and Sevier Counties, Tennessee, or of the Holston River below the
Cherokee Dam, Knox, Grainger, and Jefferson Counties, Tennessee. Based on its habitat requirements, we do not
expect this species to become established outside this NEP area. However, if individuals of this population move
upstream or downstream or into tributaries outside the designated NEP area, we would presume that they came
from the reintroduced population. We would then amend this regulation to enlarge the boundaries of the NEP area
to include the entire range of the expanded population.
(iii) We do not intend to change the NEP designations to “essential experimental,” “threatened,” or “endangered”
within the NEP area. Additionally, we will not designate critical habitat for this NEP, as provided by 16 U.S.C.
1539(j)(2)(C)(ii).
(2) What activities are not allowed in the NEP area? (i) Except as expressly allowed in paragraph (t)(3) of this
section, all the prohibitions of §17.31(a) and (b) apply to the pygmy madtom.
(ii) Any manner of take not described under paragraph (t)(3) of this section is prohibited in the NEP area. We may
refer unauthorized take of this species to the appropriate authorities for prosecution.
(iii) You may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any of the
identified fishes, or parts thereof, that are taken or possessed in violation of paragraph (t)(2) of this section or in
violation of the applicable State fish and wildlife laws or regulations or the Act.
(iv) You may not attempt to commit, solicit another to commit, or cause to be committed any offense defined in
paragraph (t)(2) of this section.
(3) What take is allowed in the NEP area? Take of this species that is accidental and incidental to an otherwise
legal activity, such as recreation (e.g., fishing, boating, wading, trapping, or swimming), forestry, agriculture, and
other activities that are in accordance with Federal, State, and local laws and regulations, is allowed.
(4) How will the effectiveness of these reintroductions be monitored? We will prepare periodic progress reports and
fully evaluate these reintroduction efforts after 5 and 10 years to determine whether to continue or terminate the
reintroduction efforts.
(5) Note: Map of the NEP area for the pygmy madtom in the French Broad River and Holston River, Tennessee,
appears immediately following paragraph (m)(7) of this section.
(u) Rio Grande silvery minnow (Hybognathus amarus)—(1) Where are populations of this fish designated as
nonessential experimental populations (NEP)?
(i) The NEP area for the Rio Grande silvery minnow is within the species' historical range and is defined as follows:
Rio Grande, from Little Box Canyon downstream of Fort Quitman, Hudspeth County, Texas, through Big Bend
National Park and the Rio Grande Wild and Scenic River, to Amistad Dam; and on the Pecos River, from its
confluence with Independence Creek to its confluence with the Rio Grande.
(ii) The Rio Grande silvery minnow is not currently known to exist in the Rio Grande or Pecos River in Texas.
Based on the habitat requirements of this fish, we do not expect it to become established outside the NEP area.
However, if any individuals of this species move upstream or downstream or into tributaries outside the designated
NEP area, we would presume that they came from the reestablished populations. We would then amend
paragraph (u)(1)(i) of this section to enlarge the boundaries of the NEP to include the entire range of the expanded
population.
(iii) We do not intend to change the NEP designation to “essential experimental,” “threatened,” or “endangered”
within the NEP area. Additionally, we will not designate critical habitat for this NEP, as provided by 16 U.S.C.
1539(j)(2)(C)(ii).
(2) What take is allowed of this species in the NEP area? (i) A Rio Grande silvery minnow may be taken within the
NEP area, provided that such take is either not willful, knowing, or due to negligence, or is incidental to and not the
purpose of the carrying out of an otherwise lawful activity, such as recreation (e.g., fishing, boating, wading,
trapping, or swimming), agriculture, and other activities that are in accordance with Federal, State, and local laws
and regulations. However, Federal agencies, must consult under section 7 of the Act on their activities that may
affect the Rio Grande silvery minnow within Big Bend National Park or the Wild and Scenic River.
(ii) Any person with a valid permit issued by the U.S. Fish and Wildlife Service (Service) under 50 CFR 17.32 may
take Rio Grande silvery minnows for educational purposes, scientific purposes, the enhancement of propagation
or survival of the species, zoological exhibition, and other conservation purposes consistent with the Act;
(iii) Any taking pursuant to paragraph (u)(2)(i) of this section must be reported within 7 days by contacting the
Service, Austin Ecological Services Field Office, 107011 Burnet Road, Suite 200, Austin, TX 78758; (512) 4900057. Once the Service is contacted, a determination will be made as to the disposition of any live or dead
specimens. Reporting requirements for take pursuant to paragraph (u)(2)(ii) of this section will be specifically
defined in the permit issued by the Service.
(3) What take of this species is not allowed in the NEP area? (i) Except as expressly allowed in paragraph (u)(2) of
this section, all the provisions of 50 CFR 17.31(a) and (b) apply to the fish identified in paragraph (u)(1) of this
section.
(ii) Any manner of take not described under paragraph (u)(2) of this section is prohibited in the NEP area.
(iii) You may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any of the
identified fishes, or parts thereof, that are taken or possessed in violation of paragraph (u)(3) of this section or in
violation of the applicable State or local fish and wildlife laws or regulations or the Act.
(iv) You may not attempt to commit, solicit another to commit, or cause to be committed any offense defined in
paragraph (u)(3) of this section.
(4) How will the effectiveness of the reestablishment be monitored? (i) After the initial stocking of this fish, we will
monitor their presence or absence at least annually and document any spawning behavior or young-of-year fish
that might be present. Depending on available resources, monitoring may occur more frequently, especially during
the first few years of reestablishment efforts. This monitoring will be conducted primarily by seining and will be
accomplished by Service, National Park Service, or State employees or by contracting with the appropriate
species experts. Annual reports will be produced detailing stocking and monitoring activities that took place during
the previous year.
(ii) The Service will fully evaluate these reestablishment efforts every 5 years to determine whether to continue or
terminate them.
(iii) Note: Map of the NEP area for the Rio Grande silvery minnow in Texas follows:
eCFR graphic er08de08.000.gif
View or download PDF
(v) Sonoran pronghorn (Antilocapra americana sonoriensis). (1) The Sonoran pronghorn (Antilocapra americana
sonoriensis) population identified in paragraph (v)(12) of this section is a nonessential experimental population
(NEP).
(2) No person may take this species, except as provided in paragraphs (v)(3) through (v)(6) of this section.
(3) Any person with a valid permit issued by the U.S. Fish and Wildlife Service under §17.32 may take pronghorn
within the NEP area for scientific purposes, the enhancement of propagation or survival of the species, and other
conservation purposes consistent with the Endangered Species Act.
(4) A Sonoran pronghorn may be taken within the boundaries of Yuma Proving Grounds; Barry M. Goldwater
Range; lands of the Arizona State Land Department; Bureau of Land Management lands; privately owned lands;
and lands of the Tohono O'odham Nation, Colorado River Indian Tribes, Gila River Indian Reservation, Ak-Chin
Indian Reservation, Pascua Yaqui Indian Reservation, and San Xavier Reservation within the NEP area, provided
that such take is incidental to, and not the purpose of, carrying out any otherwise lawful activity; and provided that
such taking is reported as soon as possible in accordance with paragraph (v)(6) of this section. Otherwise lawful
activities are any activities in compliance with applicable land management regulations, hunting regulations, tribal
law, and all other applicable law and regulations, and include, but are not limited to, military training and testing,
border security and enforcement carried out by Federal law enforcement officials (e.g., U.S. Customs and Border
Protection), agriculture, rural and urban development, livestock grazing, camping, hiking, hunting, recreational
vehicle use, sightseeing, nature or scientific study, rockhounding, and geocaching, where such activities are
permitted.
(5) Any employee or agent of the U.S. Fish and Wildlife Service, the Arizona Department of Game and Fish, and
the tribes listed in paragraph (v)(4) of this section, who is designated for such purpose may, when acting in the
course of official duties, take a Sonoran pronghorn if such action is necessary to:
(i) Aid a sick, injured, or orphaned Sonoran pronghorn, including rescuing such animals from canals;
(ii) Dispose of a dead Sonoran pronghorn specimen, or salvage a dead specimen that may be useful for scientific
study;
(iii) Move a Sonoran pronghorn for genetic purposes or to improve the health of the population; or
(iv) Capture and release a Sonoran pronghorn for relocation, to collect biological data, or to attach, service, or
detach radio-telemetry equipment.
(6) Any taking pursuant to paragraphs (v)(3) through (v)(5) of this section must be reported as soon as possible by
calling the U.S. Fish and Wildlife Service, Arizona Ecological Services Office, 201 N Bonita Avenue, Suite 141,
Tucson, AZ 85745 (520/670-6150), or the Cabeza Prieta National Wildlife Refuge, 1611 North Second Avenue,
Ajo, AZ 85321 (520/387-6483). Upon contact, a determination will be made as to the disposition of any live or
dead specimens.
(7) No person may possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever, any
Sonoran pronghorn or Sonoran pronghorn parts taken in violation of these regulations.
(8) It is unlawful for any person to attempt to commit, solicit another to commit, or cause to be committed, any
offense defined in paragraphs (v)(2) and (7) of this section.
(9) The boundaries of the designated NEP area are based on the maximum estimated range of pronghorn that are
released in and become established within the NEP area. These boundaries are physical barriers to movements,
including major freeways and highways, and the Colorado River. All release sites will be within the NEP area.
(i) All Sonoran pronghorn found in the wild within the boundaries of the NEP area will be considered members of
the NEP. Any Sonoran pronghorn occurring outside of the NEP area are considered endangered under the Act.
(ii) The Service has designated the NEP area to accommodate the potential future movements of wild Sonoran
pronghorn. All released Sonoran pronghorn and their progeny are expected to remain in the NEP area due to the
geographical extent of the designation and substantial barriers to movement that form the boundaries of the NEP.
(10) The NEP will be monitored closely for the duration of the program. Any pronghorn that is determined to be
sick, injured, or otherwise in need of special care will be recaptured to the extent possible by Service and/or State
or Tribal wildlife personnel or their designated agent and given appropriate care. Such pronghorn will be released
back to the wild as soon as possible, unless physical or behavioral problems make it necessary to return them to a
captive-breeding facility.
(11) The Service plans to evaluate the status of the NEP every 5 years to determine future management status
and needs, with the first evaluation occurring not more than 5 years after the first release of pronghorn into the
NEP area. All reviews will take into account the reproductive success and movement patterns of individuals
released, food habits, and overall health of the population. This evaluation will include a progress report.
(12) The areas covered by this proposed nonessential experimental population designation are in Arizona. They
include the area north of Interstate 8 and south of Interstate 10, bounded by the Colorado River on the west and
Interstate 10 on the east, and an area south of Interstate 8, bounded by Highway 85 on the west, Interstates 10
and 19 on the east, and the U.S.-Mexico border on the south.
(13) Note: Map of the NEP area for the Sonoran pronghorn in southwestern Arizona follows:
eCFR graphic er05my11.128.gif
View or download PDF
(w) Bull Trout (Salvelinus confluentus)—(1) Where are populations of this fish designated as nonessential
experimental populations (NEPs)?
(i) The NEP area for the bull trout is within the species' historical range and is defined as follows: the entire
Clackamas River subbasin as well as the mainstem Willamette River, from Willamette Falls to its points of
confluence with the Columbia River, including Multnomah Channel.
(ii) Bull trout are not currently known to exist in the Clackamas River subbasin or the mainstem Willamette River,
from Willamette Falls to its points of confluence with the Columbia River, including Multnomah Channel, in Oregon.
Should any bull trout be found in the Willamette River within the NEP boundary, the U.S. Fish and Wildlife Service
(Service) will assume the fish to be part of the reintroduced population, unless the fish is tagged or otherwise
known to be from another population. Given the presence of suitable overwintering and forage habitat in the upper
portion of the Clackamas River, as well as the geographic distance from spawning and rearing habitat in the upper
Clackamas River to any overwintering and foraging habitat in the lower Clackamas and Willamette Rivers, we do
not expect the reintroduced fish to become established outside the NEP. Bull trout found outside of the NEP
boundary, but known to be part of the NEP, will assume the status of bull trout within the geographic area in which
they are found.
(iii) We do not intend to change the NEP designation to “essential experimental,” “threatened,” or “endangered”
within the NEP area. Additionally, we will not designate critical habitat for the NEP, as provided by 16 U.S.C.
1539(j)(2)(C)(ii).
(2) What take is allowed of this species in the NEP area? (i) Bull trout may be taken within the NEP area, provided
that such take is:
(A) Not willful, knowing, or due to negligence.
(B) Incidental to and not the purpose of carrying out an otherwise lawful activity, such as recreation (e.g., fishing,
boating, wading, trapping, or swimming), agriculture, hydroelectric power generation, and other activities that are
in accordance with Federal, State, Tribal, and local laws and regulations.
(C) Consistent with Oregon Department of Fish and Wildlife (ODFW) fishing regulations that have been
coordinated with the Service, if due to fishing.
(D) Incidental to any activities related to or associated with the operation and maintenance of the Clackamas River
Hydroelectric Project (FERC Project No. 2195) by Portland General Electric (PGE) as administered under a
license issued by FERC. Acceptable forms of taking of bull trout include, but are not limited to, mortality, stranding,
injury, impingement and entrainment at project facilities, or delay in up- or downstream passage associated with or
caused by any of the following activities. Activities related to the operation and maintenance of Project 2195
include, but are not limited to:
(1) Hydroelectric generation at any project facility;
(2) Maintenance of project facilities;
(3) Provision of upstream and downstream fish passage, whether through fish passage facilities, powerhouses,
bypass facilities, bypass reaches, or spillways;
(4) Fish handling at fish separation and counting facilities;
(5) Fish removal from fish passage facilities and areas critical to downstream migrant passage testing at the time
of testing (Bull trout removed for this testing do not need to be returned to the Clackamas River subbasin.);
(6) Fish conservation activities;
(7) Fish handling, tagging, and sampling in connection with FERC-approved studies; and
(8) Approved resource protection, mitigation, and enhancement measures.
(E) Consistent with the adaptive management process identified for this project including:
(1) The targeted relocation or possible removal of bull trout by the Service or our project partners, if bull trout are
documented staging at the entrance to, within, or below, juvenile fish passage facilities within the Clackamas
Hydroelectric Project; and
(2) Discontinuation of the reintroduction project and complete removal of bull trout from the Clackamas River if the
Service determines, in consultation and coordination with the State of Oregon, NMFS, and other project partners,
and based on project monitoring and evaluation, that the reintroduction efforts cannot be carried out in a manner
consistent with the recovery of threatened salmon and steelhead.
(ii) Any person with a valid permit issued by the Service under §17.32 and a valid State permit issued by ODFW
may take bull trout for educational purposes, scientific purposes, the enhancement of propagation or survival of
the species, zoological exhibition, and other conservation purposes consistent with the Act.
(3) What take of this species is not allowed in the NEP area? (i) Except as expressly allowed in paragraph (w)(2)
of this section, all the provisions of §17.31(a) and (b) apply to the fish identified in paragraph (w)(1) of this section.
(ii) Any manner of take not described under paragraph (w)(2) of this section or Oregon Revised Statute (ORS)
498.002 and Oregon Angling Regulations pursuant to ORS 498.002 is prohibited in the NEP area. Should State
statutes or regulations change, take prohibitions will change accordingly. Any changes to State recreational fishing
regulations pertaining to the experimental population of bull trout in the Clackamas River subbasin will be made by
the State in collaboration with the Service. We may refer unauthorized take of this species to ODFW law
enforcement authorities or Service law enforcement authorities for prosecution.
(iii) A person may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any
of the identified fishes, or parts thereof, that are taken or possessed in a manner not expressly allowed in
paragraph (w)(2) of this section, or in violation of the applicable State fish and wildlife laws or regulations or the
Act.
(iv) A person may not attempt to commit, solicit another to commit, or cause to be committed any offense except
the take expressly allowed in paragraph (w)(2) of this section.
(4) How will the effectiveness of the reestablishment be monitored? (i) Effectiveness monitoring of the project will
be conducted jointly by the Service and ODFW, with assistance from the U.S. Forest Service (USFS) and PGE.
(ii) We will monitor the effectiveness of the reintroduction during phase 1 of the project (2011-2017) by annually
assessing: Distribution and movement, relative survival of translocated bull trout via presence and absence
surveys, occurrence of spawning and reproduction, and genetic health, as measured against the donor population.
These monitoring objectives will be accomplished by methodologies that include Passive Integrated Transponder
(PIT) tagging of all fish translocated to the Clackamas River, radio tagging of the adult and subadult life stages,
snorkel surveys, redd surveys, and minnow trapping.
(iii) If successful reproduction of reintroduced bull trout is detected, we will incorporate monitoring to assess the
distribution, movement, growth, and survival of the initial cohorts of naturally produced bull trout.
(iv) Monitoring activities in phase 2 (2018-2024) and phase 3 (2025-2030) will be informed by phase 1 monitoring
and evaluation.
(v) Annual reports that summarize the implementation and monitoring activities that occurred the previous year will
be collaboratively developed by the Service, ODFW, and USFS.
(vi) We will evaluate the implementation strategy annually, and we will evaluate the reestablishment effort at the
completion of phase 1 to determine whether to continue translocation of bull trout in phase 2.
(5) What safeguards are in place to ensure the protection of Federally listed salmon and steelhead in the NEP
area? (i) In consultation and coordination with the National Marine Fisheries Service (NMFS) and other project
partners, we have developed a plan to facilitate management decisions associated with potential impacts from the
bull trout reintroduction on listed anadromous salmonids. If specific bull trout and/or anadromous salmonid
thresholds are triggered, we will follow the planned management actions to minimize impacts to salmon and
steelhead from the reintroduction of bull trout in the Clackamas River.
(ii) Our management actions implemented and the frequency of those actions, will be informed by:
(A) The reintroduction project's monitoring and evaluation program, jointly implemented by the Service, ODFW,
and USFS; and
(B) The conservation status of the listed Clackamas River anadromous salmonid populations.
(iii) Because we cannot predict all likely impact scenarios and appropriate management responses, we will modify
our plan as necessary, in consultation and coordination with NMFS, ODFW, and other project partners, consistent
with the overall adaptive management of the project.
(iv) Although our analysis indicates a low likelihood for population-level impacts to Federally listed salmon and
steelhead populations, if the Service determines, in consultation and coordination with the State of Oregon, NMFS,
and other project partners, and based on project monitoring and evaluation, that the reintroduction efforts are not
consistent with the recovery of salmon or steelhead, the reintroduction program will be discontinued and bull trout
will be removed from the experimental population area.
(v) Prior to releasing bull trout into the Clackamas River, the Service will complete any required interagency
cooperation with NMFS pursuant to section 7(a)(2) of the Act.
(6) Note: Map of the NEP area for bull trout in Oregon follows:
eCFR graphic er21jn11.026.gif
View or download PDF
(x) Wood bison (Bison bison athabascae). (1) Wood bison within the area identified in paragraph (x)(2)(i) of this
section are members of a nonessential experimental population (NEP) and will be managed primarily by the State
of Alaska (State), through its Department of Fish and Game (ADF&G), in cooperation with the Service, in
accordance with this rule and the respective management plans.
(2) Where are wood bison in Alaska designated as an NEP?
(i) The boundaries of the NEP area encompass the Yukon, Tanana, and Kuskokwim River drainages in Alaska
(Figure 1). The NEP area includes much of the wood bison's historical range in Alaska, and the release sites are
within the species' historical range. The NEP area is defined as follows: the Yukon River drainage from the United
States-Canada border downstream to its mouth; the Tanana River drainage from the United States-Canada border
downstream to its confluence with the Yukon River; and the Kuskokwim River drainage from its headwaters
downstream to its mouth at the Bering Sea.
eCFR graphic er07my14.002.gif
View or download PDF
(ii) Any wood bison found within the Alaska wood bison NEP area will be considered part of the NEP. The bison
will be managed by the State to prevent establishment of any population outside the NEP area.
(3) Under what circumstances might an Alaska wood bison NEP be eliminated?
(i) We do not anticipate eliminating all individuals within an Alaska wood bison NEP unless:
(A) The State deems the reintroduction efforts a failure or most members of reintroduced populations have
disappeared for any reason;
(B) Monitoring of wood bison in Alaska indicates appreciable harm to other native wildlife, such as the introduction
of disease or other unanticipated environmental consequences associated with their presence; or
(C) Legal or statutory changes reduce or eliminate the State's ability to complete the restoration effort as designed
and intended in its management plans, with the management flexibility and protection of other land uses (including
other resource development) provided in this NEP designation.
(ii) If any of the circumstances listed in paragraph (x)(3)(i) of this section occur, some or all wood bison may be
removed from the wild in Alaska by any method deemed practicable by the State, including lethal removal. If the
reintroduction of wood bison under this nonessential experimental designation is discontinued for any reason and
no action is taken by the Service and the State to change the designation, all remaining wood bison in Alaska will
retain their NEP status.
(4) Which agency is the management lead for wood bison in Alaska? The Alaska Department of Fish and Game
will have primary responsibility for leading and implementing the wood bison restoration effort, in cooperation with
the Service, and will keep the Service apprised of the status of the effort on an ongoing basis. The Service will
retain responsibility for ensuring compliance with all provisions of the Endangered Species Act of 1973, as
amended (ESA; 16 U.S.C. 1531 et seq.), including compliance with section 7 for actions occurring on National
Wildlife Refuge and National Park Service lands.
(5) What take of wood bison is allowed in the NEP area? In the following instances, wood bison may be taken in
accordance with applicable State fish and wildlife conservation laws and regulations:
(i) Hunting will be an allowed take based on sustained yield principles as established by ADF&G.
(ii) A wood bison may be taken within the NEP area, provided that such take is not willful, knowing, or due to
negligence, or is incidental to and not the purpose of the carrying out of an otherwise lawful activity, including but
not limited to recreation (e.g., trapping, hiking, camping, or shooting activities); forestry; agriculture; oil and gas
exploration and development and associated activities; construction and maintenance of roads or railroads,
buildings, facilities, energy projects, pipelines, and transmission lines of any kind; mining; mineral exploration;
travel by any means, including vehicles, watercraft, snow machines, or aircraft; tourism; and other activities that
are in accordance with Federal, State, and local laws and regulations and specific authorizations. Such conduct is
not considered intentional or “knowing take” for purposes of this regulation, and neither the Service nor the State
will take legal action for such conduct. Any cases of “knowing take” will be referred to the appropriate authorities
for prosecution.
(iii) Any person with a valid permit issued by the Service under 50 CFR 17.32 or by ADF&G may take wood bison
for educational purposes, scientific purposes, the enhancement of propagation or survival of the species,
zoological exhibition, and other conservation purposes consistent with the ESA. Additionally, any employee or
agent of the Service or ADF&G designated for such purposes, acting in the course of official duties, may take a
wood bison if such action is necessary:
(A) For scientific purposes;
(B) To relocate a wood bison to avoid conflict with human activities;
(C) To relocate a wood bison if necessary to protect the wood bison;
(D) To relocate wood bison within the NEP area to improve wood bison survival and recovery prospects or for
genetic purposes;
(E) To relocate wood bison from one population in the NEP area into another, or into captivity;
(F) To relocate wood bison that have moved outside the NEP area back into the NEP area or remove them;
(G) To aid or euthanize a sick, injured, or orphaned wood bison;
(H) To dispose of a dead wood bison, or salvage a dead wood bison for scientific purposes; or
(I) To aid in law enforcement investigations involving wood bison.
(iv) Any person may take a wood bison in defense of the individual's life or the life of another person. The Service,
the State, or our designated agent(s) may also promptly remove any wood bison that the Service, the State, or our
designated agent(s) determine to be a threat to human life or safety. Any such taking must be reported within 24
hours to the location identified in paragraph (x)(5)(vi) of this section.
(v) In connection with otherwise lawful activities, including but not limited to the use and development of land,
provided at paragraph (x)(5)(ii) of this section, the Federal Government, the State, municipalities of the State, other
local governments, Native American Tribal Governments, and all landowners and their employees or authorized
agents, tenants, or designees may harass wood bison in the areas defined in paragraph (x)(2)(i) of this section,
provided that all such harassment is by methods that are not lethal or physically injurious to wood bison and is
reported within 24 hours to the location identified in paragraph (x)(5)(vi) of this section.
(vi) Any taking pursuant to paragraph (x)(5)(ii) of this section must be reported within 14 days by contacting the
Alaska Department of Fish and Game, 1300 College Road, Fairbanks, AK 99701; (907) 459-7206. ADF&G will
determine the most appropriate course of action regarding any live or dead specimens.
(6) What take of wood bison is not allowed in the NEP area?
(i) Except as expressly allowed in paragraph (x)(5) of this section, all the provisions of 50 CFR 17.31(a) and (b)
apply to the wood bison identified in paragraph (x)(1) of this section.
(ii) Any manner of take not described under paragraph (x)(5) of this section is prohibited in the NEP area.
(iii) A person may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any
of the identified wood bison, or parts thereof, that are taken or possessed in a manner not expressly allowed in
paragraph (x)(5) of this section or in violation of the applicable State or local fish and wildlife laws or regulations or
the ESA.
(iv) A person may not attempt to commit, solicit another to commit, or cause to be committed any take of wood
bison, except that take expressly allowed in paragraph (x)(5) of this section.
(7) How will the effectiveness of the wood bison reintroduction be monitored? ADF&G will monitor the population
status of reintroduced bison herds at least annually and will document productivity, survival, and population size.
The Service or other Federal agencies may also be involved in population monitoring, particularly where National
Wildlife Refuge System or Bureau of Land Management lands are involved. Tribal governments or other
organizations may also participate in population monitoring and other management activities. Depending on
available resources, monitoring may occur more frequently, especially during the first few years of reestablishment
efforts. This monitoring will be conducted primarily through aerial surveys and will be accomplished by State or
Service employees, through cooperative efforts with local governments, or by contracting with other appropriate
species experts.
(8) What other provisions apply to this special rule?
If any particular provision of this rule or the application of any particular provision to any entity or circumstance is
held invalid, the remainder of this finding and rule and the application of such provisions to other entities or
circumstances shall not be affected by such holding.
[49 FR 35954, Sept. 13, 1984; 50 FR 30194, July 24, 1985]
Editorial Note: For Federal Register citations affecting §17.84, see the List of CFR Sections Affected, which
appears in the Finding Aids section of the printed volume and at www.govinfo.gov.
return arrow Back to Top
§17.85 Special rules—invertebrates.
(a) Seventeen mollusks in the Tennessee River. The species in the following table comprise nonessential
experimental populations (NEPs):
Common name
Cumberland bean (pearlymussel)
tubercled blossom (pearlymussel)
turgid blossom (pearlymussel)
yellow blossom (pearlymussel)
catspaw (purple cat's paw pearlymussel)
clubshell
Cumberlandian combshell
Alabama lampmussel
winged mapleleaf (mussel)
Cumberland monkeyface (pearlymussel)
oyster mussel
birdwing pearlymussel
cracking pearlymussel
dromedary pearlymussel
fine-rayed pigtoe
shiny pigtoe
Anthony's riversnail
Scientific name
Villosa trabalis
Epioblasma torulosa torulosa
Epioblasma turgidula
Epioblasma florentina florentina
Epioblasma obliquata obliquata
Pleurobema clava
Epioblasma brevidens
Lampsilis virescens
Quadrula fragosa
Quadrula intermedia
Epioblasma capsaeformis
Lemiox rimosus
Hemistena lata
Dromus dromas
Fusconaia cuneolus
Fusconaia cor
Athearnia anthonyi
(1) Where are these mollusks designated as nonessential experimental populations (NEPs)? (i) The NEP Area for
these 17 mollusks is within the species' historic ranges, and is defined as follows: The free-flowing reach of the
Tennessee River from the base of Wilson Dam downstream to the backwaters of Pickwick Reservoir (river mile
(RM) 259.4 [414.0 km] to RM 246.0 [393.6 km] and includes the lower 5 RM (8 km) of all tributaries to this reach in
Colbert and Lauderdale Counties, Alabama.
(ii) None of the identified species are known to exist in any of the tributaries to the free-flowing reach of the
Tennessee River below Wilson Dam or from below the backwaters of Pickwick Reservoir, Colbert and Lauderdale
Counties, Alabama. In the future, if any of the 17 mollusks are found upstream of the lower 5 RM (8 km) of these
tributaries or downstream into Pickwick Reservoir, we will presume the animals came from the reintroduced NEP,
and we will amend this rule and enlarge the boundaries of the NEP Area to include the entire range of the
expanded population.
(iii) We do not intend to change the NEP designations to “essential experimental,” “threatened,” or “endangered”
within the NEP Area. Additionally, we will not designate critical habitat for these NEPs, as provided by 16 U.S.C.
1539(j)(2)(C)(ii).
(2) What activities are not allowed in the NEP Area? (i) Except as expressly allowed in this rule, all the prohibitions
of 17.31(a) and (b) apply to the mollusks identified in this special rule.
(ii) Any manner of take not described under paragraph (a)(3) of this section will not be allowed in the NEP Area.
We may refer the unauthorized take of these species to the appropriate authorities for prosecution.
(iii) You may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any of the
identified 17 mollusks, or parts thereof, that are taken or possessed in violation of these regulations or in violation
of the applicable State fish and wildlife laws or regulations or the Act.
(iv) You may not attempt to commit, solicit another to commit, or cause to be committed any offense defined in this
paragraph (a).
(3) What take is allowed in the NEP Area? (i) Take of these species that is accidental and incidental to an
otherwise lawful activity such as fishing, boating, commercial navigation, trapping, wading, or mussel harvesting, is
allowed.
(ii) Any individual collecting or harvesting mussels must check their collection prior to leaving the immediate area
and return any NEP mussels to the site where they were obtained.
(4) How will the effectiveness of these reintroductions be monitored? We will prepare periodic progress reports and
fully evaluate these reintroduction efforts after 5 and 10 years to determine whether to continue or terminate the
reintroduction efforts.
(b) Sixteen mollusks in the French Broad and Holston Rivers. The species in the following table comprise
nonessential experimental populations (NEP):
Common name
Cumberland bean (pearlymussel)
Cumberlandian combshell
fanshell
Appalachian monkeyface (pearlymussel)
Cumberland monkeyface (pearlymussel)
oyster mussel
birdwing pearlymussel
cracking pearlymussel
dromedary pearlymussel
fine-rayed pigtoe
rough pigtoe
shiny pigtoe
orange-foot pimpleback (pearlymussel)
ring pink (mussel)
white wartyback (pearlymussel)
Anthony's riversnail
Scientific name
Villosa trabalis
Epioblasma brevidens
Cyprogenia stegaria
Quadrula sparsa
Quadrula intermedia
Epioblasma capsaeformis
Lemiox rimosus
Hemistena lata
Dromus dromas
Fusconaia cuneolus
Pleurobema plenum
Fusconaia cor
Plethobasus cooperianus
Obovaria retusa
Plethobasus cicatricosus
Athearnia anthonyi
(1) Where are these mollusks designated as NEPs? (i) The NEP area for these mollusks is within the species'
historical range and is defined as follows: The French Broad River, Knox and Sevier Counties, Tennessee, from
the base of Douglas Dam (river mile (RM) 32.3 (51.7 kilometers (km)) downstream to the confluence with the
Holston River; then up the Holston River, Knox, Grainger, and Jefferson Counties, Tennessee, to the base of
Cherokee Dam (RM 52.3 (83.7 km)); and the lower 5 RM (8 km) of all tributaries that enter these river reaches.
None of the species identified in paragraph (b) are known to exist in any of the tributaries to the free-flowing
reaches of the French Broad River below Douglas Dam, Knox and Sevier Counties, Tennessee, or of the Holston
River below the Cherokee Dam, Knox, Grainger, and Jefferson Counties, Tennessee. Based on their habitat
requirements, we do not expect these species to become established outside this NEP area. However, if any
individuals are found upstream or downstream or into tributaries outside the designated NEP area, we would
presume that they came from the reintroduced populations. We would then amend paragraph (b)(1)(i) of this
section to enlarge the boundaries of the NEP area to include the entire range of the expanded population.
(ii) Another NEP area for 10 of these mollusks (Cumberland bean, Cumberlandian combshell, Cumberland
monkeyface, oyster mussel, birdwing pearlymussel, cracking pearlymussel, dromedary pearlymussel, fine-rayed
pigtoe, shiny pigtoe, and Anthony's riversnail) is provided in paragraph (a) of this section.
(iii) We do not intend to change the NEP designations to “essential experimental,” “threatened,” or “endangered”
within the NEP area. Additionally, we will not designate critical habitat for these NEPs, as provided by 16 U.S.C.
1539(j)(2)(C)(ii).
(2) What activities are not allowed in the NEP area? (i) Except as expressly allowed in paragraph (b)(3) of this
section, all the prohibitions of §17.31(a) and (b) apply to the mollusks identified in paragraph (b) of this section.
(ii) Any manner of take not described under paragraph (b)(3) of this section will not be allowed in the NEP area.
We may refer the unauthorized take of these species to the appropriate authorities for prosecution.
(iii) You may not possess, sell, deliver, carry, transport, ship, import, or export by any means whatsoever any of the
identified mollusks, or parts thereof, that are taken or possessed in violation of paragraph (b)(2) of this section or in
violation of the applicable State fish and wildlife laws or regulations or the Act.
(iv) You may not attempt to commit, solicit another to commit, or cause to be committed any offense defined in
paragraph (b)(2) of this section.
(3) What take is allowed in the NEP area? Take of these species that is accidental and incidental to an otherwise
legal activity, such as recreation (e.g., fishing, boating, wading, trapping, or swimming), forestry, agriculture, and
other activities that are in accordance with Federal, State, and local laws and regulations, is allowed.
(4) How will the effectiveness of these reintroductions be monitored? We will prepare periodic progress reports and
fully evaluate these reintroduction efforts after 5 and 10 years to determine whether to continue or terminate the
reintroduction efforts.
(5) Note: Map of the NEP area in Tennessee for the 16 mollusks listed in paragraph (b) of this section follows:
eCFR graphic er13se07.003.gif
View or download PDF
(c) American Burying Beetle (Nicrophorus americanus).
(1) Where is the American burying beetle designated as a nonessential experimental population (NEP)? (i) The
NEP area for the American burying beetle is within the species' historical range and is defined as follows: The
Missouri Counties of Cedar, St. Clair, Bates, and Vernon.
(ii) The American burying beetle is not known to exist in Cedar, St. Clair, Bates, or Vernon Counties in Missouri, as
of the date of enacting this regulation. Based on its habitat requirements and movement patterns, we do not
expect this species to become established outside this NEP area.
(2) What activities are not allowed in the NEP area? (i) You may not possess, sell, deliver, carry, transport, ship,
import, or export by any means, American burying beetles, or parts thereof, that are taken or possessed in
violation of paragraph (c)(3) of this section or in violation of applicable State fish and wildlife laws or regulations or
the Act.
(ii) You may not attempt to commit, solicit another to commit, or cause to be committed any offense defined in
paragraph (c)(2)(i) of this section.
(3) What take is allowed in the NEP area? Take of this species that is accidental and incidental to an otherwise
legal activity, such as agriculture, forestry and wildlife management, land development, recreation, and other
activities, is allowed.
(4) How will the effectiveness of these reintroductions be monitored? We will prepare periodic progress reports and
fully evaluate these reintroduction efforts after 5 years to determine whether to continue or terminate the
reintroduction efforts.
(5) Note: Map of the NEP area for the American burying beetle follows:
eCFR graphic er22mr12.003.gif
View or download PDF
(d) Oregon Silverspot Butterfly (Speyeria zerene hippolyta).
(1) Where is the Oregon silverspot butterfly designated as a nonessential experimental population (NEP)? (i) The
NEP areas for the Oregon silverspot butterfly are within the subspecies' historical range in Tillamook and Clatsop
Counties, Oregon. The boundary of the NEP includes those Public Land Survey System sections intersecting with
a 4.25-mile (6.8-kilometer) radius around the release locations. This boundary was selected to encompass all
likely movements of Oregon silverspot butterflies away from the release areas while maintaining geographic
separation from existing populations.
(A) The Nestucca Bay NEP area, centered on the coastal prairie habitat on the Cannery Hill Unit of the Nestucca
Bay National Wildlife Refuge (Nestucca Bay NEP area), includes Township 4 South, Range 10 West, Sections 15
through 36; Township 4 South, Range 11 West, Sections 13, 24, 25, and 36; Township 5 South, Range 10 West,
Sections 2 through 11, 14 through 23, 27 through 30; and Township 5 South, Range 11 West, Sections 12, 13, 24,
and 25.
(B) The Saddle Mountain NEP area, centered on the coastal prairie habitat on top of Saddle Mountain State
Natural Area (Saddle Mountain NEP area), includes Township 6 North, Range 7 West, Sections 7, 17 through 20,
29 through 32; Township 6 North, Range 8 West, Sections 1 through 36; Township 6 North, Range 9 West,
Sections 1, 11 through 14, 23 through 26, 35, and 36; Township 5 North, Range 7 West, Sections 5 through 8, 17,
18, and 19; Township 5 North, Range 8 West, Sections 1 through 24; and Township 5 North, Range 9 West,
Sections 1, 2, 3, 11, 12, 13, and 14.
(ii) The nearest known extant population to the Nestucca Bay NEP area is 8 miles (13 kilometers) to the south,
beyond the longest known flight distance of the butterfly (4.1 miles (6.6 kilometers)) and with little or no suitable
habitat between them. The nearest known extant population to the Saddle Mountain NEP area is 50 miles (80
kilometers) to the south, well beyond the longest known flight distance of the butterfly (4.1 miles (6.6 kilometers)).
Given its habitat requirements, movement patterns, and distance from extant populations, the NEP is wholly
separate from extant populations, and we do not expect the reintroduced Oregon silverspot butterflies to become
established outside the NEP areas. Oregon silverspot butterflies outside of the NEP boundaries will assume the
status of Oregon silverspot butterflies within the geographic area in which they are found.
(iii) We will not change the NEP designations to “essential experimental,” “threatened,” or “endangered” within the
NEP areas without engaging in notice-and-comment rulemaking. Additionally, we will not designate critical habitat
for this NEP, as provided by 16 U.S.C. 1539(j)(2)(C)(ii).
(2) What take of the Oregon silverspot butterfly is allowed in the NEP areas? (i) Oregon silverspot butterflies may
be taken within the NEP area, provided that such take is not willful, knowing, or due to negligence, and is
incidental to carrying out an otherwise lawful activity, such as agriculture, forestry and wildlife management, land
development, recreation, and other activities that are in accordance with Federal, State, Tribal, and local laws and
regulations.
(ii) Any person with a valid permit issued by the Service under 50 CFR 17.32 may take the Oregon silverspot
butterfly for educational purposes, scientific purposes, the enhancement of propagation or survival of the species,
zoological exhibition, and other conservation purposes consistent with the Act. Additionally, any employee or agent
of the Service, any other Federal land management agency, or a State conservation agency, who is designated by
the agency for such purposes, may, when acting in the course of official duties, take an Oregon silverspot butterfly
in the wild in the NEP area if such action is necessary:
(A) For scientific purposes;
(B) To relocate Oregon silverspot butterflies to avoid conflict with human activities;
(C) To relocate Oregon silverspot butterflies within the NEP area to improve Oregon silverspot butterfly survival
and recovery prospects or for genetic purposes;
(D) To relocate Oregon silverspot butterflies from one population in the NEP into another in the NEP, or into
captivity;
(E) To euthanize an injured Oregon silverspot butterfly;
(F) To dispose of a dead Oregon silverspot butterfly, or salvage a dead Oregon silverspot butterfly for scientific
purposes;
(G) To relocate an Oregon silverspot butterfly that has moved outside the NEP area back into the NEP area; or
(H) To aid in law enforcement investigations involving the Oregon silverspot butterfly.
(3) What take of Oregon silverspot butterfly is not allowed in the NEP area? (i) Except as expressly allowed in
paragraph (d)(2) of this section, all of the provisions of 50 CFR 17.31(a) and (b) apply to the Oregon silverspot
butterfly in areas identified in paragraph (d)(1) of this section.
(ii) A person may not possess, sell, deliver, carry, transport, ship, import, or export by any means, Oregon
silverspot butterflies, or parts thereof, that are taken or possessed in a manner not expressly allowed in paragraph
(d)(2) of this section or in violation of applicable State fish and wildlife laws or regulations or the Act.
(iii) Any manner of take not described under paragraph (d)(2) of this section is prohibited in the NEP areas.
(iv) A person may not attempt to commit, solicit another to commit, or cause to be committed any take of the
Oregon silverspot butterfly, except as expressly allowed in paragraph (d)(2) of this section.
(4) How will the effectiveness of these reintroductions be monitored? We will monitor populations annually for
trends in abundance in cooperation with partners, monitor habitat quality, and prepare annual progress reports. We
will fully evaluate reintroduction efforts after 5 years to determine whether to continue or terminate the
reintroduction efforts.
(5) Maps of the NEP areas for the Oregon silverspot butterfly in Northwest Oregon.
(i) Note: Map of the Oregon silverspot butterfly NEP follows:
eCFR graphic er23jn17.001.gif
View or download PDF
(ii) Note: Map of Nestucca Bay NEP area for the Oregon silverspot butterfly follows:
eCFR graphic er23jn17.002.gif
View or download PDF
(iii) Note: Map of Saddle Mountain NEP area for the Oregon silverspot butterfly follows:
eCFR graphic er23jn17.003.gif
View or download PDF
[66 FR 32263, June 14, 2001, as amended at 72 FR 52459, Sept. 13, 2007; 77 FR 16717, Mar. 22, 2012; 82 FR
28578, June 23, 2017]
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§17.86 Special rules—plants. [Reserved]
return arrow Back to Top
Subpart I—Interagency Cooperation
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§17.94 Critical habitats.
(a) The areas listed in §17.95 (fish and wildlife), §17.96 (plants), and §17.99 (plants on the Hawaiian Islands) and
referred to in the lists at §§17.11 and 17.12 have been determined by the Director to be critical habitat. All Federal
agencies must insure that any action authorized, funded, or carried out by them is not likely to result in the
destruction or adverse modification of the constituent elements essential to the conservation of the listed species
within these defined critical habitats. (See part 402 for rules concerning this prohibition; see also part 424 for rules
concerning the determination of critical habitat).
(b) Maps.
If the critical habitat
map appears in
Then . . .
. . .
(1) A critical habitat
designation in
The map provided by the Secretary of the Interior, as clarified or refined by any
§17.95(a), (b), (d),
textual language within the rule, constitutes the definition of the boundaries of
(e), (f), (g), (h), or (i),
a critical habitat. Each critical habitat area will be shown on a map, with moreand the designation
detailed information discussed in the preamble of the rulemaking documents
does not state that
published in the Federal Registerand made available from the lead field office
the map(s) is for
of the Service responsible for such designation. Each area will be referenced
informational
to the State(s), county(ies), or other local government units within which all or
purposes only, or (2)
part of the critical habitat is located. General descriptions of the location and
A critical habitat
boundaries of each area may be provided to clarify or refine what is included
designation in
within the boundaries depicted on the map, or to explain the exclusion of sites
§17.99, or (3) A
(e.g., paved roads, buildings) within the mapped area. Unless otherwise
critical habitat
indicated within the critical habitat descriptions, the names of the State(s) and
designation
county(ies) are provided for informational purposes only and do not constitute
published and
the boundaries of the area.
effective after May
31, 2012
(4) A critical habitat
designation that
states that the
The map provided by the Secretary of the Interior is for reference purposes to
map(s) is for
guide Federal agencies and other interested parties in locating the general
informational
boundaries of the critical habitat. The map does not, unless otherwise
purposes only, or (5) indicated, constitute the definition of the boundaries of a critical habitat. Critical
A critical habitat
habitats are described by reference to surveyable landmarks found on
designation
standard topographic maps of the area and to the States and county(ies)
published and
within which all or part of the critical habitat is located. Unless otherwise
effective on or prior indicated within the critical habitat description, the State and county(ies)
to May 31, 2012, that names are provided for informational purposes only.
is set forth at
§17.95(c) or §17.96
[82 FR 49755, Oct. 27, 2017, as amended at 83 FR 18702, Apr. 27, 2018]
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§17.95 Critical habitat—fish and wildlife.
(a) Mammals.
Indiana Bat (Myotis sodalis)
Illinois. The Blackball Mine, La Salle County.
Indiana. Big Wyandotte Cave, Crawford County; Ray's Cave, Greene County.
Kentucky. Bat Cave, Carter County; Coach Cave, Edmonson County.
Missouri. Cave 021, Crawford County; Cave 009, Franklin County; Cave 017, Franklin County; Pilot Knob Mine,
Iron County; Bat Cave, Shannon County; Cave 029, Washington County (numbers assigned by Division of
Ecological Services, U.S. Fish and Wildlife Service, Region 6).
Tennessee. White Oak Blowhole Cave, Blount county.
West Virginia. Hellhole Cave, Pendleton County.
Note: No map.
Mariana Fruit Bat (Pteropus mariannus
mariannus)
(1) The critical habitat unit for the Mariana fruit bat is depicted for the Territory of Guam on the maps below.
(2) Within this area, the primary constituent elements required by the Mariana fruit bat for the biological needs of
foraging, sheltering, roosting, and rearing of young are found in areas supporting limestone, secondary, ravine,
swamp, agricultural, and coastal forests composed of native or introduced plant species. These forest types
provide the primary constituent elements of:
(i) Plant species used for foraging, such as Artocarpus sp. (breadfruit), Carica papaya (papaya), Cycas
circinalis(fadang), Ficus spp. (fig), Pandanus tectorius (kafu), Cocos nucifera (coconut palm), and Terminalia
catappa(talisai); and
(ii) Remote locations, often within 328 ft (100 m) of clifflines that are 260 to 590 ft (80 to 100 m) tall, with limited
exposure to human disturbance; land that contains mature fig, Mammea odorata (chopak), Casuarina
equisetifolia(gago), Macaranga thompsonii (pengua), Guettarda speciosa (panao), Neisosperma
oppositifolia (fagot), and other tree species that are used for roosting and breeding.
(3) Critical habitat does not include existing features and structures within the boundaries of the mapped units,
such as buildings, roads, aqueducts, antennas, water tanks, agricultural fields, paved areas, lawns, and other
urban landscaped areas not containing one or more of the primary constituent elements.
(4) The critical habitat unit is described below. Coordinates are in UTM Zone 55 with units in meters using North
American Datum of 1983 (NAD83)/World Geodetic System 1984 (WGS 84).
(i) Note: Map 1—General Location of the Mariana Fruit Bat Unit follows:
eCFR graphic er28oc04.000.gif
View or download PDF
(ii) Guam, Mariana fruit bat (376 ac; 152 ha).
(A) [Reserved]
(B) Map 2 showing Mariana Fruit Bat Unit follows:
eCFR graphic er28oc04.001.gif
View or download PDF
Virginia Big-eared Bat (Plecotus townsendii
virginianus)
West Virginia. Cave Mountain Cave, Hellhole Cave, Hoffman School Cave, and Sinnit Cave, each in Pendleton
County; Cave Hollow Cave, Tucker County.
Note: The map provided is for informational purposes only. Map follows:
eCFR graphic ec01jn91.009.gif
View or download PDF
Polar Bear (Ursus maritimus) in the United
States
(1) Critical habitat areas are in the State of Alaska, and adjacent territorial and U.S. waters, as described below.
(2) The primary constituent elements of critical habitat for the polar bear in the United States are:
(i) Sea-ice habitat used for feeding, breeding, denning, and movements, which is sea ice over waters 300 m (984.2
ft) or less in depth that occurs over the continental shelf with adequate prey resources (primarily ringed and
bearded seals) to support polar bears.
(ii) Terrestrial denning habitat, which includes topographic features, such as coastal bluffs and river banks, with the
following suitable macrohabitat characteristics:
(A) Steep, stable slopes (range 15.5-50.0°), with heights ranging from 1.3 to 34 m (4.3 to 111.6 ft), and with water
or relatively level ground below the slope and relatively flat terrain above the slope;
(B) Unobstructed, undisturbed access between den sites and the coast;
(C) Sea ice in proximity to terrestrial denning habitat prior to the onset of denning during the fall to provide access
to terrestrial den sites; and
(D) The absence of disturbance from humans and human activities that might attract other polar bears.
(iii) Barrier island habitat used for denning, refuge from human disturbance, and movements along the coast to
access maternal den and optimal feeding habitat, which includes all barrier islands along the Alaska coast and
their associated spits, within the range of the polar bear in the United States, and the water, ice, and terrestrial
habitat within 1.6 km (1 mi) of these islands (no-disturbance zone).
(3) Critical habitat does not include manmade structures (e.g., houses, gravel roads, generator plants, sewage
treatment plants, hotels, docks, seawalls, pipelines) and the land on which they are located existing within the
boundaries of designated critical habitat on the effective date of this rule.
(4) Critical habitat map units. Boundaries were derived from GIS data layers of the 1:63,360 scale digital coastline
of the State of Alaska, created by the Alaska Department of Natural Resources from U.S. Geological Survey inchto-the-mile topographic quadrangles. The International Bathymetric Chart of the Arctic Ocean, version 2.3, was
used for the bathymetric data. The maritime boundaries to generate the 3-mile nautical line, U.S. territorial
boundary, and Exclusive Economic Zone were from the National Oceanic and Atmospheric Administration's Office
of Coast Survey Web site. The land status and ownership information at the section level scale was from the
Alaska Department of Natural Resources, and was obtained from the Alaska State Office of the Bureau of Land
Management. The detailed parcel-level land status was created by the U.S. Fish and Wildlife Service, Division of
the Realty, by digitizing U.S. Bureau of Land Management Master Title Plots. The detailed denning habitat maps
and the internal boundaries for the terrestrial denning habitat were provided by the U.S. Geological Survey, Alaska
Science Center. The data were projected into Alaska Standard Albers Conical Equal Area using the North
American Datum of 1983 to estimate the area of each critical habitat unit and determine overlap with land and
water ownership.
(5) Unit 1: Sea-ice habitat.
(i) The critical sea-ice habitat area includes all the contiguous waters from the mean high tide line of the mainland
coast of Alaska to the 300-m (984.2-ft) bathymetry contour. The critical sea-ice habitat is bounded on the east by
the United States-Canada border (69.64892° N, 141.00533° W) and extends along the coastline to a point
southwest of Hooper Bay (61.52859° N, 166.15476° W) on the western coast of Alaska. The eastern boundary
extends offshore approximately 85 km (136 mi) from the coast (70.41526° N, 141.0076° W) at the United StatesCanada border and then follows the 300-m (984.2-ft) bathymetry contour northwest until it intersects with the U.S.
200-nautical-mile EEZ (74.01403° N, 163.52341° W). The boundary then follows the EEZ boundary southwest to
the intersection with the United States-Russian boundary (72.78333° N, 168.97694° W). From this point, the
boundary follows the United States-Russia boundary south and southwest to the intersection with the southern
boundary of the Chukchi-Bering Seas population southwest of Gambell, St Lawrence Island (62.55482° N,
173.68023° W). From this point, the boundary extends southeast to the coast of Alaska (61.52859° N, 166.15476°
W).
(ii) The map of Unit 1, sea-ice habitat, follows:
eCFR graphic er07de10.001.gif
View or download PDF
(6) Unit 2: Terrestrial denning habitat.
(i) The critical terrestrial denning habitat area extends from the mainland coast of Alaska 32 kilometers (20 mi)
landward (primarily south) from the United States-Canada border to the Kavik River to the west. From the Kavik
River to Barrow, the critical terrestrial denning habitat extends landward 8 kilometers (5 mi) south from the
mainland coast of Alaska.
(ii) The village district of Barrow is excluded from the critical terrestrial denning habitat area. The excluded area is
delineated as follows: Beginning at the southeast corner of the northeast 1⁄4 of Section 29, Unsurveyed T22N,
R18W, Umiat Meridian, Alaska; thence North to the southeast corner of the northeast 1⁄4 of Section 17,
Unsurveyed T22N, R18W; thence East to the southeast corner of the northeast 1⁄4 of Section 16, Unsurveyed
T22N, R18W, Umiat Meridian, Alaska; thence North to the northeast corner of Section 16, Unsurveyed T22N,
R18W; thence East to the southeast corner of southwest 1⁄4 of Section 10, Unsurveyed T22N, R18W; thence
North to the northwest corner of the southwest 1⁄4 of northeast 1⁄4 of Section 34, Unsurveyed T23N, R18W;
thence East to the southeast corner of the northeast 1⁄4 of the northeast 1⁄4 of Section 34, Unsurveyed T23N,
R18W; thence North to the point where the section line common to Sections 14 and 15, Unsurveyed T23N, R18W;
intersects the mean low water line of the Chukchi Sea; thence in a southwesterly direction along the mean low
water line of the Chukchi Sea to the point where the mean low water line of the Chukchi Sea intersects the eastwest center line of Section 27, Unsurveyed T22N, R19W; thence East to the point of beginning, containing 21
square miles, more or less. You can view legal descriptions and detailed, colored maps of the exclusions in this
final rule at http://alaska.fws.gov/fisheries/mmm/polarbear/criticalhabitat.htm.
(iii) The village district of Kaktovik is excluded from the critical terrestrial denning habitat area. The excluded area
is delineated as follows: From the P.O.B. (which is also the point of beginning for the U.S. Survey No. 4234) at
approximately 2,828 feet distant on a bearing of N 01° 40′ E from Tri. Sta. U. S. C. and G. S. “Barter Astro”; the
boundary thence shall run West for approximately 325′; thence South approximately 600′; thence West
approximately 500′; thence South approximately 100′; thence West approximately 4,000′; thence South
approximately 3,550′; thence East approximately 4,000′; thence in a northeasterly direction approximately 3,225′ to
a point on the mean high water line of the Kaktovik Lagoon which is approximately 2,478′ distant on a bearing S
78 53′ E from Tri. Sta. U. S. C. and G. S. “Barter Astro”; thence northerly along the meandering mean high water
line of the Kaktovik Lagoon, around Pipsuk Point, and westerly continuing on the meandering mean high water line
to a point on the mean high water line of the Kaktovik Lagoon which is approximately 477′ distant on a bearing of
N 88 58′ E from another point which is approximately 1,503′ distant on a bearing of N 01 24′ W from the point of
beginning; thence approximately 477′ in a westerly direction, a bearing of S 88; 58′ W; thence approximately
1,503′in a southerly direction on a bearing of S 01 24′ E to the point of beginning, containing one square mile,
more or less. You can view legal descriptions and detailed, colored maps of the exclusions in this final rule
at http://alaska.fws.gov/fisheries/mmm/polarbear/criticalhabitat.htm.
(iv) The maps of Unit 2 (east and west), terrestrial denning habitat, follow:
eCFR graphic er07de10.002.gif
View or download PDF
eCFR graphic er07de10.003.gif
View or download PDF
(7) Unit 3: Barrier island habitat.
(i) The critical barrier island habitat includes off-shore islands offset from the mainland coast of Alaska starting at
the United States-Canada border westward to Barrow, southwest to Cape Lisburne, south to Point Hope,
southwest to Wales, southeast to Nome, and ending at Hooper Bay, AK, and water, sea ice, and land habitat within
1.6 kilometers (1 mile) of the barrier islands (no-disturbance zone).
(ii) The map of Unit 3, barrier island habitat, follows:
eCFR graphic er07de10.004.gif
View or download PDF
Woodland Caribou (Rangifer tarandus
caribou), Southern Mountain Distinct
Population Segment (DPS)
(1) A critical habitat unit is depicted for Boundary County, Idaho, and Pend Oreille County, Washington, on the map
below.
(2) Within this area, the primary constituent elements of the physical and biological features essential to the
conservation of the southern mountain caribou DPS consist of five components:
(i) Mature to old-growth western hemlock (Tsuga heterophylla)/western red cedar (Thuja plicata) climax forest, and
subalpine fir (Abies lasiocarpa)/Engelmann spruce (Picea engelmanni) climax forest at least 5,000 ft (1,520 m) in
elevation; these habitats typically have 26-50 percent or greater canopy closure.
(ii) Ridge tops and high elevation basins that are generally 6,000 ft (1,830 m) in elevation or higher, associated
with mature to old stands of subalpine fir (Abies lasiocarpa)/Engelmann spruce (Picea engelmanni) climax forest,
with relatively open canopy.
(iii) Presence of arboreal hair lichens.
(iv) High-elevation benches and shallow slopes, secondary stream bottoms, riparian areas, seeps, and subalpine
meadows with succulent forbs and grasses, flowering plants, horsetails, willow, huckleberry, dwarf birch, sedges,
and lichens. The southern mountain caribou DPS, including pregnant females, uses these areas for feeding during
the spring and summer seasons.
(v) Corridors/Transition zones that connect the habitats described above. If human activities occur, they are such
that they do not impair the ability of caribou to use these areas.
(3) Critical habitat does not include manmade structures (such as buildings, roads, and other paved areas) and the
land on which they are located existing within the legal boundaries on December 28, 2012.
(4) Critical habitat map unit. Data layers defining the map unit were created using a 5,000-ft (1,520-m) elevation
layer derived from 30m USGS DEM plus migration-corridor polygons, and units were then mapped using Universal
Transverse Mercator (UTM) Zone 11N coordinates. The map in this entry establishes the boundaries of the critical
habitat designation. The coordinates or plot points or both on which the map is based are available to the public at
the field office Internet site (http://www.fws.gov/idaho), at http://www.regulations.gov at Docket No. FWS-R1-ES2011-0096, and at the Service's Idaho Fish and Wildlife Office. You may obtain field office location information by
contacting one of the Service regional offices, the addresses of which are listed at 50 CFR 2.2.
(5) Unit 1: Boundary County, Idaho, and Pend Oreille County, Washington. The map of the critical habitat unit
follows:
eCFR graphic er02oc19.003.gif
View or download PDF
Santa Catalina Island Fox (Urocyon littoralis
catalinae)
We have determined that no areas meet the definition of critical habitat under section 3(5)(A) of the Act for Santa
Catalina Island fox. Therefore, no specific areas are designated as critical habitat for this subspecies.
Jaguar (Panthera onca)
(1) Critical habitat units are depicted for Pima, Santa Cruz, and Cochise Counties, Arizona, and Hidalgo County,
New Mexico, on the maps below.
(2) Within these areas, the primary constituent elements of the physical or biological feature essential to the
conservation of jaguar consists of expansive open spaces in the southwestern United States of at least 100
km2(32 to 38.6 mi2) in size which:
(i) Provide connectivity to Mexico;
(ii) Contain adequate levels of native prey species, including deer and javelina, as well as medium-sized prey such
as coatis, skunks, raccoons, or jackrabbits;
(iii) Include surface water sources available within 20 km (12.4 mi) of each other;
(iv) Contain greater than 1 to 50 percent canopy cover within Madrean evergreen woodland, generally recognized
by a mixture of oak (Quercus spp.), juniper (Juniperus spp.), and pine (Pinus spp.) trees on the landscape, or
semidesert grassland vegetation communities, usually characterized by Pleuraphis mutica (tobosagrass)
or Bouteloua eriopoda (black grama) along with other grasses;
(v) Are characterized by intermediately, moderately, or highly rugged terrain;
(vi) Are below 2,000 m (6,562 feet) in elevation; and
(vii) Are characterized by minimal to no human population density, no major roads, or no stable nighttime lighting
over any 1-km2 (0.4-mi2) area.
(3) Critical habitat does not include manmade structures (such as buildings, aqueducts, runways, roads, and other
paved areas) and the land on which they are located existing within the legal boundaries on April 4, 2014.
(4) Critical habitat map units. Data layers defining map units were created using hydrography data, vegetation
biomes, tree cover, terrain ruggedness, elevation, Human Influence Index, and undisputed Class I jaguar records
from 1962 to September 11, 2013, and were then mapped using Universal Transverse Mercator (UTM)
coordinates.
(5) Note: Index map follows:
eCFR graphic er05mr14.002.gif
View or download PDF
(6) Units 1, 2, 3, and 4: Baboquivari, Atascosa, Patagonia, and Whetstone Units, Pima, Santa Cruz, and Cochise
Counties, Arizona. Map of Units 1, 2, 3, and 4 follows:
eCFR graphic er05mr14.003.gif
View or download PDF
(7) Units 5 and 6: Peloncillo and San Luis Units, Cochise County, Arizona, and Hidalgo County, New Mexico. Map
of Units 5 and 6 follows:
eCFR graphic er05mr14.004.gif
View or download PDF
Fresno Kangaroo Rat (Dipodomys
nitratoides exilis)
California. An area of land, water, and airspace in Fresno County, with the following components (Mt. Diablo Base
Meridian): T14S R15E, E 1⁄2 NW 1⁄4 and NE 1⁄4 Sec. 11, that part of W 1⁄2 Sec. 12 north of the Southern Pacific
Railroad, E 1⁄2 Sec. 12; T14S R16E, that part of Sec. 7 south of the Southern Pacific Railroad.
Within this area, the major constituent elements that are known to require special management considerations or
protection are the hummocks and substrate that provide sites for burrow construction, and the natural alkali sinkopen grassland vegetation that provides food and escape cover.
Note: The map provided is for informational purposes only. Map follows:
eCFR graphic ec01jn91.010.gif
View or download PDF
Morro Bay Kangaroo Rat (Dipodomys
heermanni morroensis)
California. An area of land, water, and airspace in San Luis Obispo County, with the following components (Mt.
Diablo Meridian): T30S R10E S 1⁄2 Sec. 14, those portions of Sec. 23-24 west of Pecho Valley Road.
Note: The map provided is for informational purposes only. Map follows:
eCFR graphic ec01jn91.011.gif
View or download PDF
San Bernardino Kangaroo Rat (Dipodomys
merriami parvus)
(1) Critical habitat units are depicted for San Bernardino and Riverside Counties, California, on the maps below.
(2) The PCEs of critical habitat for the San Bernardino kangaroo rat are the habitat components that provide:
(i) Alluvial fans, washes, and associated floodplain areas containing soils consisting predominately of sand, loamy
sand, sandy loam, and loam, which provide burrowing habitat necessary for sheltering and rearing offspring,
storing food in surface caches, and movement between occupied patches;
(ii) Upland areas adjacent to alluvial fans, washes, and associated floodplain areas containing alluvial sage scrub
habitat and associated vegetation, such as coastal sage scrub and chamise chaparral, with up to approximately 50
percent canopy cover providing protection from predators, while leaving bare ground and open areas necessary
for foraging and movement of this subspecies; and
(iii) Upland areas adjacent to alluvial fans, washes, and associated floodplain areas, which may include marginal
habitat such as alluvial sage scrub with greater than 50 percent canopy cover with patches of suitable soils that
support individuals for re-population of wash areas following flood events. These areas may include agricultural
lands, areas of inactive aggregate mining activities, and urban/wildland interfaces.
(3) Critical habitat does not include manmade structures (such as buildings, aqueducts, airports, roads, other
paved areas, and the land on which such structures are located) existing on the effective date of this rule and not
containing one or more of the PCEs.
(4) Data layers defining map units were created on a base of NAIP (USDA) 1:24,000 maps, and critical habitat
units were then mapped using Universal Transverse Mercator (UTM) coordinates.
(5) Note: Index map of critical habitat units for the San Bernardino kangaroo rat follows:
eCFR graphic er17oc08.000.gif
View or download PDF
(6) Unit 1: Santa Ana River Wash, San Bernardino County, California. From USGS 1:24,000 quadrangles San
Bernardino North and Devore.
(i) Unit 1 is shown on the map in paragraph (6)(ii) of this entry, excluding lands bounded by the following Universal
Transverse Mercator (UTM) North American Datum of 1983 (NAD83) coordinates (E, N):
(A) 487253, 3772752; 487254, 3772752; 487290, 3772752; 487290, 3772752; 487290, 3772752; 487589,
3772747; 487589, 3772747; 487778, 3772648; 487787, 3772643; 487790, 3772642; 487808, 3772632; 487808,
3772632; 487808, 3772632; 487808, 3772632; 487838, 3772617; 487842, 3772614; 487978, 3772543; 487996,
3772533; 488008, 3772533; 488010, 3772533; 488122, 3772533; 488122, 3772533; 488230, 3772532; 488230,
3772532; 488351, 3772531; 488390, 3772530; 488404, 3772530; 488405, 3772530; 488471, 3772529; 488608,
3772528; 488608, 3772528; 488812, 3772526; 488812, 3772526; 488812, 3772447; 488811, 3772326; 488811,
3772326; 488803, 3772326; 488614, 3772329; 488614, 3772329; 488614, 3772329; 488614, 3772329; 488607,
3772329; 488409, 3772332; 488403, 3772332; 488403, 3772332; 488144, 3772336; 488139, 3772336; 488140,
3772340; 488139, 3772336; 488139, 3772336; 487995, 3772338; 487995, 3772338; 487849, 3772340; 487849,
3772340; 487828, 3772341; 487806, 3772341; 487790, 3772341; 487775, 3772341; 487768, 3772342; 487763,
3772342; 487758, 3772342; 487726, 3772342; 487674, 3772343; 487586, 3772344; 487310, 3772348; 487309,
3772348; 487303, 3772349; 487303, 3772349; 487302, 3772349; 487233, 3772350; 487232, 3772350; 487229,
3772350; 487229, 3772350; 487227, 3772350; 487226, 3772350; 487223, 3772350; 487214, 3772350; 487213,
3772350; 487178, 3772350; 487178, 3772350; 487177, 3772350; 487173, 3772350; 487167, 3772350; 487117,
3772350; 487117, 3772350; 487118, 3772293; 487118, 3772179; 487119, 3772154; 487032, 3772153; 486981,
3772152; 486935, 3772151; 486896, 3772151; 486587, 3772146; 486580, 3772146; 486556, 3772146; 486534,
3772145; 486434, 3772144; 486380, 3772143; 486380, 3772143; 485983, 3772032; 485982, 3772032; 485983,
3771987; 485983, 3771961; 485983, 3771945; 485983, 3771941; 485983, 3771941; 485653, 3771939; 485651,
3771939; 485650, 3771939; 485594, 3771939; 485585, 3771939; 485586, 3771875; 485595, 3771841; 485595,
3771840; 485595, 3771822; 485595, 3771821; 485595, 3771821; 485577, 3771821; 485334, 3771821; 485184,
3771821; 485184, 3771821; 484918, 3771821; 484852, 3771821; 484782, 3771821; 484782, 3771821; 484693,
3771820; 484693, 3771820; 484482, 3771819; 484482, 3771819; 484383, 3771819; 484381, 3771819; 484381,
3771824; 484381, 3771875; 484381, 3771879; 484381, 3771881; 484381, 3771882; 484381, 3771943; 484381,
3771943; 484381, 3771996; 484445, 3771996; 484782, 3771994; 484782, 3771992; 484782, 3771945; 484782,
3771941; 484909, 3771941; 485184, 3771940; 485184, 3771944; 485184, 3771948; 485183, 3771998; 485182,
3772335; 485573, 3772333; 485582, 3772333; 485582, 3772333; 485981, 3772338; 485981, 3772338; 485980,
3772361; 485976, 3772665; 485975, 3772732; 485975, 3772734; 486377, 3772741; 486380, 3772362; 486380,
3772342; 486463, 3772343; 486779, 3772346; 486778, 3772618; 486778, 3772747; 486778, 3772747; 486887,
3772749; 486908, 3772749; 486925, 3772750; 487178, 3772754; 487178, 3772754; 487184, 3772754; 487184,
3772754; 487202, 3772753; 487205, 3772753; 487209, 3772753; 487213, 3772753 ; thence returning to 487253,
3772752;
(B) 482603, 3772347; 482603, 3772347; 482602, 3772348; 483160, 3772346; 483160, 3772089; 483160,
3772072; 483160, 3771972; 483160, 3771893; 483159, 3771893; 483159, 3771893; 483071, 3771893; 483032,
3771892; 483032, 3771892; 483032, 3771892; 482989, 3771930; 482972, 3771945; 482972, 3771945; 482644,
3772097; 482622, 3772108; 482537, 3772147; 482377, 3772221; 482368, 3772227; 482368, 3772227; 482368,
3772227; 482368, 3772263; 482367, 3772336; 482367, 3772348; 482367, 3772348; 482376, 3772348; 482385,
3772348; 482394, 3772348; thence returning to 482603, 3772347; and
(C) 483188, 3772080; 483211, 3772076; 483211, 3772346; 483211, 3772346; 483374, 3772346; 483600,
3772345; 483969, 3772344; 483970, 3772008; 483970, 3771985; 483971, 3771945; 483971, 3771945; 483914,
3771945; 483913, 3771945; 483902, 3771945; 483848, 3771945; 483409, 3771944; 483272, 3771944; 483215,
3771944; 483210, 3771944; 483210, 3771944; 483210, 3771944; 483210, 3771944; 483200, 3771933; 483200,
3771933; 483200, 3771933; 483187, 3771946; 483185, 3771948; thence returning to 483188, 3772080.
(ii) Map of Unit 1—Santa Ana River Wash follows:
eCFR graphic er17oc08.001.gif
View or download PDF
(7) Unit 2: Lytle/Cajon Creek Wash, San Bernardino County, California. From USGS 1:24,000 quadrangles San
Bernardino South, Redlands, Yucaipa, and Harrison Mountain.
(i) [Reserved]
(ii) Map of Unit 2—Lytle/Cajon Creek Wash follows:
eCFR graphic er17oc08.002.gif
View or download PDF
(8) Unit 3: San Jacinto River Wash, Riverside County, California. From USGS 1:24,000 quadrangles San Jacinto,
Lake Fulmor, and Blackburn Canyon.
(i) Unit 3 is shown on the map in paragraph (8)(ii) of this entry, excluding lands bounded by the following Universal
Transverse Mercator (UTM) North American Datum of 1983 (NAD83) coordinates (E, N):
(A) 506793, 3736955; 506803, 3736965; 506858, 3736912; 506834, 3736888; 506826, 3736879; 506771,
3736932; thence returning to 506793, 3736955;
(B) 506995, 3736726; 507035, 3736768; 507090, 3736715; 507050, 3736673; thence returning to 506995,
3736726;
(C) 507212, 3736516; 507248, 3736554; 507295, 3736509; 507260, 3736471; thence returning to 507212,
3736516; and
(D) 512090, 3734474; 512104, 3734481; 512118, 3734488; 512130, 3734464; 512130, 3734464; 512113,
3734456; 512104, 3734464; 512093, 3734472; thence returning to 512090, 3734474.
(ii) Map of Unit 3—San Jacinto River Wash follows:
eCFR graphic er17oc08.003.gif
View or download PDF
(9) Unit 4: Cable Creek Wash, San Bernardino County, California. From USGS 1:24,000 quadrangles San
Bernardino South, Redlands, Yucaipa, and Harrison Mountain.
(i) [Reserved]
(ii) Map of Unit 4—Cable Creek Wash follows:
eCFR graphic er17oc08.004.gif
View or download PDF
(10) Unit 5: Bautista Creek, Riverside County, California. From USGS 1:24,000 quadrangle Blackburn Canyon.
(i) [Reserved]
(ii) Map of Unit 5—Bautista Creek follows:
eCFR graphic er17oc08.005.gif
View or download PDF
Canada Lynx (Lynx canadensis)
(1) Critical habitat units are depicted on the maps below for the following States and counties:
(i) Idaho: Boundary County;
(ii) Maine: Aroostook, Franklin, Penobscot, Piscataquis, and Somerset Counties;
(iii) Minnesota: Cook, Koochiching, Lake, and St. Louis Counties;
(iv) Montana: Carbon, Flathead, Gallatin, Glacier, Granite, Lake, Lewis and Clark, Lincoln, Missoula, Park,
Pondera, Powell, Stillwater, Sweetgrass, and Teton Counties;
(v) Washington: Chelan and Okanogan Counties; and
(vi) Wyoming: Fremont, Lincoln, Park, Sublette, and Teton Counties.
(2) Within these areas the primary constituent element for the Canada lynx is boreal forest landscapes supporting
a mosaic of differing successional forest stages and containing:
(i) Presence of snowshoe hares and their preferred habitat conditions, which include dense understories of young
trees, shrubs or overhanging boughs that protrude above the snow, and mature multistoried stands with conifer
boughs touching the snow surface;
(ii) Winter conditions that provide and maintain deep fluffy snow for extended periods of time;
(iii) Sites for denning that have abundant coarse woody debris, such as downed trees and root wads; and
(iv) Matrix habitat (e.g., hardwood forest, dry forest, non-forest, or other habitat types that do not support
snowshoe hares) that occurs between patches of boreal forest in close juxtaposition (at the scale of a lynx home
range) such that lynx are likely to travel through such habitat while accessing patches of boreal forest within a
home range.
(3) Critical habitat does not include manmade structures (such as buildings, aqueducts, runways, roads, and other
paved areas) and the land on which they are located existing within the legal boundaries on October 14, 2014.
(4) Critical habitat map units. Data layers defining map units were created using a USA Contiguous Albers Equal
Area Conic projection. The maps in this entry establish the boundaries of the critical habitat designation. The
coordinates or plot points or both on which each map is based are available to the public at the Service's internet
site, http://www.fws.gov/montanafieldoffice/, at http://www.regulations.gov at Docket No. FWS-R6-ES-2013-0101,
and at the field office responsible for this designation. You may obtain field office location information by contacting
one of the Service regional offices, the addresses of which are listed at 50 CFR 2.2.
(5) Note: Index map follows:
eCFR graphic er12se14.000.gif
View or download PDF
(6) Unit 1: Maine—Aroostook, Franklin, Penobscot, Piscataquis, and Somerset Counties, ME. Map of Unit 1,
Maine, follows:
eCFR graphic er12se14.001.gif
View or download PDF
(7) Unit 2: Minnesota—Cook, Koochiching, Lake, and St. Louis Counties, MN.
Map of Unit 2, Minnesota, follows:
eCFR graphic er12se14.002.gif
View or download PDF
(8) Unit 3: Northern Rockies—Boundary County, ID, and Flathead, Glacier, Granite, Lake, Lewis and Clark,
Lincoln, Missoula, Pondera, Powell and Teton Counties, MT. Map of Unit 3, Northern Rockies, follows:
eCFR graphic er12se14.003.gif
View or download PDF
(9) Unit 4: North Cascades—Chelan and Okanogan Counties, WA. Map of Unit 4, North Cascades, follows:
eCFR graphic er12se14.004.gif
View or download PDF
(10) Unit 5: Greater Yellowstone Area—Carbon, Gallatin, Park, Stillwater, and Sweetgrass Counties, MT, and
Fremont, Lincoln, Park, Sublette, and Teton Counties, WY. Map of Unit 5, Greater Yellowstone Area, follows:
eCFR graphic er12se14.005.gif
View or download PDF
Florida Manatee (Trichechus manatus)
Florida. Crystal River and its headwaters known as King's Bay, Citrus County; the Little Manatee River
downstream from the U.S. Highway 301 bridge, Hillsborough County; the Manatee River downstream from the
Lake Manatee Dam, Manatee County; the Myakka River downstream from Myakka River State Park, Sarasota and
Charlotte Counties; the Peace River downstream from the Florida State Highway 760 bridge, De Soto and
Charlotte Counties; Charlotte Harbor north of the Charlotte-Lee County line, Charlotte County; Caloosahatchee
River downstream from the Florida State Highway 31 bridge, Lee County; all U.S. territorial waters adjoining the
coast and islands of Lee County; all U.S. territorial waters adjoining the coast and islands and all connected bays,
estuaries, and rivers from Gordon's Pass, near Naples, Collier County, southward to and including Whitewater
Bay, Monroe County; all waters of Card, Barnes, Blackwater, Little Blackwater, Manatee, and Buttonwood Sounds
between Key Largo, Monroe County, and the mainland of Dade County; Biscayne Bay, and all adjoining and
connected lakes, rivers, canals, and waterways from the southern tip of Key Biscayne northward to and including
Maule Lake, Dade County; all of Lake Worth, from its northernmost point immediately south of the intersection of
U.S. Highway 1 and Florida State Highway A1A southward to its southernmost point immediately north of the town
of Boynton Beach, Palm Beach County; the Loxahatchee River and its headwaters, Martin and West Palm Beach
Counties; that section of the intracoastal waterway from the town of Seawalls Point, Martin County to Jupiter Inlet,
Palm Beach County; the entire inland section of water known as the Indian River, from its northernmost point
immediately south of the intersection of U.S. Highway 1 and Florida State Highway 3, Volusia County, southward
to its southernmost point near the town of Seawalls Point, Martin County, and the entire inland section of water
known as the Banana River and all waterways between Indian and Banana Rivers, Brevard County; the St. Johns
River including Lake George, and including Blue Springs and Silver Glen Springs from their points of origin to their
confluences with the St. Johns River; that section of the Intracoastal Waterway from its confluences with the St.
Marys River on the Georgia-Florida border to the Florida State Highway A1A bridge south of Coastal City, Nassau
and Duval Counties.
Note: No map.
Alabama Beach Mouse (Peromyscus
polionotus ammobates)
(1) Critical habitat units are depicted for Baldwin County, Alabama, on the maps below. The maps provided are for
informational purposes only.
(2) The primary constituent elements of critical habitat for the Alabama Beach Mouse are the habitat components
that provide:
(i) A contiguous mosaic of primary, secondary, and scrub vegetation and dune structure, with a balanced level of
competition and predation and few or no competitive or predaceous nonnative species present, that collectively
provide foraging opportunities, cover, and burrow sites.
(ii) Primary and secondary dunes, generally dominated by sea oats (Uniola paniculata), that despite occasional
temporary impacts and reconfiguration from tropical storms and hurricanes, provide abundant food resources,
burrow sites, and protection from predators.
(iii) Scrub dunes, generally dominated by scrub oaks (Quercus spp.), that provide food resources and burrow sites,
and provide elevated refugia during and after intense flooding due to rainfall and/or hurricane-induced storm surge.
(iv) Unobstructed habitat connections that facilitate genetic exchange, dispersal, natural exploratory movements,
and recolonization of locally extirpated areas.
(v) A natural light regime within the coastal dune ecosystem, compatible with the nocturnal activity of beach mice,
necessary for normal behavior, growth, and viability of all life stages.
(3) Critical habitat does not include manmade structures (such as buildings, aqueducts, airport runways, roads,
other paved areas, and piers) and the land on which they are located existing within the legal boundaries on the
effective date of this rule.
(4) Critical habitat map units. Data layers defining map units were created by delineating habitats that contained
one or more of the PCEs defined in paragraph (2) of this entry, over 2005 Baldwin County, Alabama color
photography (UTM 16, NAD 83).
(5) Note: Index Map (Map 1) follows:
eCFR graphic er30ja07.000.gif
View or download PDF
(6) Unit 1: Fort Morgan, Baldwin County, Alabama.
(i) General Description: Unit 1 consists of 446 ac (180 ha) at the extreme western tip of the Fort Morgan Peninsula
in Baldwin County, Alabama. This unit encompasses essential features of Alabama beach mouse habitat within
the boundary of the Fort Morgan State Historic Site and adjacent properties west of the Bay to Breakers
development. The southern and western extents are the mean high water level (MHWL). The unit extends
northward to either the seaward extent of maritime forest, developed features associated with the Fort Morgan
State Historic Site, or Ft. Morgan Parkway.
(ii) Coordinates: From the Fort Morgan and Saint Andrews Bay USGS 1:24,000 quadrangle maps, Alabama, land
bounded by the following UTM 16 NAD 83 coordinates (E, N): 401473.62, 3344763.21; 401547.57, 3344692.62;
401513.96, 3344669.09; 01503.87, 3344514.47; 401369.42, 3344440.53; 401577.82, 3344356.49; 402008.06,
3344443.89; 402169.41, 3344622.04; 402525.70, 3344682.54; 403820.62, 3344782.93; 404628.95, 3344823.00;
404623.54, 3344330.64; 404288.09, 3344287.36; 403970.48, 3344745.87; 403970.48, 3344230.37; 403292.55,
3344087.17; 402583.77, 3343995.19; 401269.00, 3343995.19; 400971.42, 3344125.04; 400976.83, 3344206.20;
401301.47, 3344628.22; 404286.32, 3344756.22; 402854.33, 3344659.30; 402903.74, 3344669.55; 402929.27,
3344691.88; 403288.24, 3344682.82; 403627.98, 3344721.72; 403654.87, 3344714.12; 403590.33, 3344665.04;
403546.85, 3344641.30; 403501.91, 3344628.03; 403337.34, 3344622.77; 403056.19, 3344638.97
(iii) Note: Map of Unit 1, Fort Morgan (Map 2), follows:
eCFR graphic er30ja07.001.gif
View or download PDF
(7) Unit 2: Little Point Clear, Baldwin County, Alabama.
(i) General Description: Unit 2 consists of 268 ac (108 ha) on the Fort Morgan Peninsula in Baldwin County,
Alabama. This unit encompasses essential features of Alabama beach mouse habitat north of the mean high
water line (MHWL) and south of the Alabama Department of Environmental Management Coastal Construction
Control Line (as defined in Alabama Administrative Code of Regulations 335-8-2-0.8) from the eastern property
boundary of Bay to Breakers eastward to the western boundary of the Surfside Shores subdivision. This unit also
includes essential features of Alabama beach mouse habitat 160 ft south (except where otherwise noted) of the
centerline of Fort Morgan Parkway, from the eastern boundary of Bay to Breakers east to the western boundary of
the Surfside Shores subdivision, and associated areas as depicted on Map 3 in paragraph (7)(iii) of this entry and
in the coordinates provided in paragraph (7)(ii) of this entry.
(ii) Coordinates: From the Saint Andrews Bay USGS 1:24,000 quadrangle map, Alabama, land bounded by the
following UTM 16 NAD 83 coordinates (E, N), except those areas covered by incidental take permits shown in the
maps: 408673.97, 3345088.73; 408690.96, 3345050.98; 408964.63, 3345069.85; 408992.95, 3345115.15;
409098.64, 3345124.59; 409260.96, 3345071.74; 409306.26, 3345047.20; 409421.39, 3345039.65; 409421.39,
3345018.89; 409839.57, 3345038.68; 410450.38, 3345133.36; 410638.20, 3345180.70; 411632.04, 3345331.96;
411819.06, 3345348.96; 411819.06, 3345276.71; 411455.65, 3345227.83; 411423.77, 3345234.20; 411115.62,
3345195.95; 410735.21, 3345138.57; 410735.21, 3345117.32; 410129.52, 3345030.18; 405929.15, 3344870.87;
406790.26, 3344915.69; 406790.26, 3344944.50; 406889.49, 3344986.11; 406915.10, 3344986.11; 406947.11,
3344973.31; 406972.72, 3344998.92; 406998.33, 3344960.50; 407039.95, 3344973.31; 407065.56, 3344950.90;
407148.55, 3344960.50; 407232.02, 3345008.52; 407238.42, 3345034.13; 407289.64, 3344954.10; 407918.85,
3345054.48; 408411.28, 3345026.14; 408414.83, 3345068.65; 408687.61, 3345125.34; 408723.04, 3345107.62;
406397.69, 3344654.51; 408502.15, 3344816.39; 408502.15, 3344974.12; 408369.32, 3344978.29; 408074.61,
3345003.18; 407842.17, 3344994.88; 407194.65, 3344878.65; 406327.13, 3344837.15; 406318.83, 3344720.92;
406181.85, 3344716.77; 406165.25, 3344837.15; 404625.30, 3344770.73; 408639.12, 3344982.42; 408850.81,
3345011.48; 408626.67, 3344828.84; 408904.77, 3345015.63; 409021.00, 3345003.18; 409033.45, 3344837.15;
410127.40, 3344881.42; 409942.50, 3345003.19; 409321.94, 3344964.94; 409122.17, 3344994.69; 409122.17,
3344839.55; 411303.93, 3344704.32; 410054.54, 3344754.13; 410029.64, 3344741.68; 409992.28, 3344745.83;
409963.23, 3344758.28; 408879.87, 3344720.92; 407157.29, 3344642.06; 406011.67, 3344509.23; 405044.53,
3344417.91; 404700.02, 3344343.20; 404624.32, 3344815.46; 404709.17, 3344488.16; 405203.36, 3344433.41;
405813.57, 3344509.70; 406027.79, 3344616.83; 406662.44, 3344675.99; 406677.12, 3344600.23; 407261.66,
3344729.73; 407664.18, 3344758.57; 407637.12, 3344658.32; 408856.44, 3344833.42; 408903.73, 3344832.33;
409944.78, 3344975.70; 409961.53, 3344931.31; 409960.68, 3344885.70; 409940.98, 3344852.55; 410474.83,
3344831.25; 411896.05, 3344778.56; 411897.06, 3344677.82; 411898.98, 3345357.59; 411899.47, 3345349.16;
411899.92, 3345333.36; 411898.69, 3345292.29
(iii) Note: Map of Unit 2, Little Point Clear (Map 3), follows:
eCFR graphic er30ja07.002.gif
View or download PDF
(8) Unit 3: Gulf Highlands, Baldwin County, Alabama.
(i) General Description: Unit 3 consists of 275 ac (111 ha) on the Fort Morgan Peninsula in Baldwin County,
Alabama. This unit encompasses essential features of Alabama beach mouse habitat north of the mean high
water line (MHWL) to the seaward extent of interdunal wetlands as depicted on Map 4 in paragraph (8)(iii) of this
entry and in the coordinates in paragraph (8)(ii) of this entry. This unit also includes essential features of Alabama
beach mouse habitat 160 ft south of the centerline of Fort Morgan Parkway (except some areas to the north as
noted in paragraphs (8)(ii) and (8)(iii) of this entry). Unit 3 is bounded to the west by the eastern property line of the
Morgantown subdivision and to the east by the western property line of Martinique on the Gulf.
(ii) Coordinates: From the Pine Beach and Saint Andrews Bay USGS 1:24,000 quadrangle maps, Alabama, land
bounded by the following UTM 16 NAD 83 coordinates (E, N), except those areas covered by incidental take
permits shown in the maps:
(A) Surfside Shores—412122.39, 3344896.76; 412230.61, 3344952.19; 412407.44, 3344970.66; 412407.44,
3344997.06; 413286.34, 3345139.58; 413283.70, 3344598.52; 411897.20, 3344677.62; 411896.72, 3344778.70;
411901.40, 3344895.52; 412585.68, 3344637.82; 413286.36, 3345090.20; 413224.06, 3345080.28; 413224.52,
3344927.47; 413284.56, 3344937.39
(B) Gulf Highlands—414393.00, 3344536.62; 414393.00, 3344732.11; 414676.12, 3344736.60; 415529.98,
3344440.00; 414671.87, 3344524.00; 414736.29, 3344520.49; 414736.41, 3344546.27; 415324.89, 3344541.53;
415326.46, 3344653.21; 415533.04, 3344653.83; 415290.55, 3345011.54; 415327.74, 3345011.79; 415327.61,
3344980.39; 415290.42, 3344981.38; 415308.84, 3344940.80; 415327.02, 3344940.72; 415327.30, 3344910.13;
415308.70, 3344910.21; 415358.01, 3344940.99; 415376.61, 3344940.91; 415376.48, 3344910.33; 415357.88,
3344910.41; 415291.27, 3345081.38; 415309.04, 3345081.30; 415309.47, 3345085.02; 415291.28, 3345084.28;
415326.74, 3345051.69; 415326.74, 3345039.99; 415181.66, 3345041.16; 415184.00, 3345052.86; 415174.64,
3345051.69; 415174.64, 3345041.16; 414954.68, 3345042.33; 414954.68, 3344655.06; 414920.74, 3344656.23;
414920.74, 3344761.53; 414735.88, 3344762.70; 414735.88, 3344773.23; 414921.91, 3344772.06; 414921.91,
3344831.73; 414737.05, 3344832.90; 414737.05, 3344843.43; 414921.91, 3344842.26; 414923.08, 3344903.10;
414735.88, 3344903.10; 414735.88, 3344915.97; 414924.25, 3344913.63; 414921.91, 3344972.13; 414738.22,
3344974.47; 414738.22, 3344983.83; 414921.91, 3344982.66; 414923.08, 3345043.50; 414738.22, 3345043.50;
414738.22, 3345054.03; 414921.91, 3345054.03; 414921.91, 3345071.59; 414953.51, 3345073.93; 414953.51,
3345052.86; 414953.51, 3344876.19;
(C) Gulf Shores Plantation—414204.25, 3344552.35; 414204.25, 3344725.37; 414343.57, 3344754.58;
414341.32, 3344543.36
(D) Cabana Beach—415938.37, 3344420.63; 416333.53, 3344954.65; 416756.08, 3344395.60; 416750.70,
3344919.13; 415945.72, 3344968.29
(E) ROW—413472.87, 3345602.80; 413767.66, 3345609.58; 413781.21, 3345585.86; 414496.15, 3345582.47;
414760.44, 3345545.20; 414973.90, 3345460.49; 415278.85, 3345487.60; 416224.19, 3345470.66; 415654.96,
3345426.61; 414973.90, 3345402.89; 414533.42, 3345521.48; 413621.96, 3345538.42; 411899.45, 3345292.57;
411899.63, 3345333.23; 411898.97, 3345349.21; 411898.28, 3345357.92; 416599.61, 3345528.80; 416603.89,
3345480.95
(iii) Note: Map of Unit 3, Gulf Highlands (Map 4), follows:
eCFR graphic er30ja07.003.gif
View or download PDF
(9) Unit 4: Pine Beach, Baldwin County, Alabama.
(i) General Description: Unit 4 consists of 30 ac (12 ha) on 27 inholdings within the Perdue Unit of the Bon Secour
National Wildlife Refuge as depicted on Map 5 in paragraph (9)(iii) of this entry and in the coordinates in paragraph
(9)(ii) of this entry.
(ii) Coordinates: From the Pine Beach USGS 1:24,000 quadrangle map, Alabama, land bounded by the following
UTM 16 NAD 83 coordinates (E, N), except those areas covered by incidental take permits shown on the map in
paragraph (9)(iii) of this entry: 419890.08, 3344529.29; 419946.90, 3344389.62; 420406.15, 3344394.35;
420401.42, 3344342.27; 419587.07, 3344320.96; 419589.44, 3344384.88; 419658.09, 3344384.88; 419655.72,
3344503.25; 419636.78, 3344503.25; 419639.15, 3344534.02; 419783.19, 3344531.65; 419783.55, 3344384.88;
419803.49, 3344384.88; 421930.69, 3344448.80; 421895.18, 3344446.43; 422030.12, 3344465.37; 419842.74,
3344635.81; 419797.76, 3344640.55; 419688.86, 3344841.77; 419740.94, 3344841.77; 419688.86, 3344645.28;
419743.31, 3344642.92; 419740.94, 3344593.20; 419688.86, 3344595.57; 420294.50, 3345060.66; 420306.84,
3345060.44; 420306.62, 3345022.12; 420294.28, 3345022.34; 420148.12, 3344725.77; 420190.73, 3344725.77;
420188.36, 3344633.45; 420150.49, 3344633.45; 420046.32, 3344728.14; 420098.40, 3344728.14; 420098.40,
3344635.81; 420046.32, 3344635.81; 420046.32, 3344567.16; 420058.16, 3344567.16; 420058.16, 3344545.86;
420003.71, 3344545.86; 420003.71, 3344638.18; 419906.65, 3344638.18; 419927.96, 3344638.18; 419927.96,
3344545.86; 419906.65, 3344548.22; 419690.90, 3344778.02; 419740.44, 3344772.85; 419801.19, 3344677.57;
419842.01, 3344675.40; 421902.16, 3344854.73; 421932.71, 3344858.24; 421999.30, 3344843.90; 422029.66,
3344830.25; 421996.44, 3344462.00
(iii) Note: Map of Unit 4, Pine Beach (Map 5), follows:
eCFR graphic er30ja07.004.gif
View or download PDF
(10) Unit 5: Gulf State Park, Baldwin County, Alabama.
(i) General Description: Unit 5 consists of 192 ac (78 ha) in Gulf State Park east of the City of Gulf Shores in
Baldwin County, Alabama. This unit encompasses essential features of Alabama beach mouse habitat north of the
mean high water line (MHWL) to the seaward extent of either coastal wetlands, maritime forest, or Alabama beach
mouse habitat managed under the 2004 Gulf State Park habitat conservation plan. Exact boundaries are depicted
on Map 6 in paragraph (10)(iii) of this entry and in the coordinates in paragraph (10)(ii) of this entry.
(ii) Coordinates: From the Gulf Shores USGS 1:24,000 quadrangle map, Alabama, land bounded by the following
UTM 16 NAD 83 coordinates (E, N), except those areas identified as developable in the current incidental take
permit for the Alabama Department of Conservation and Natural Resources: 438247.09, 3347462.61; 438384.26,
3347485.47; 438504.29, 3347456.89; 438738.63, 3347479.75; 438738.63, 3347411.17; 438681.48, 3347405.45;
438675.76, 3347193.97; 437681.24, 3346988.21; 436938.21, 3346702.43; 436349.50, 3346599.55; 435377.85,
3346548.11; 435160.66, 3346490.95; 435166.37, 3346736.72; 435606.47, 3346856.75; 436572.41, 3346828.17;
36572.41, 3346913.91; 436881.06, 3347033.94; 436909.64, 3347068.23; 437612.66, 3347325.43; 437818.42,
3347319.72; 437829.85, 3347251.13; 438035.61, 3347308.29; 438041.33, 3347394.02; 435699.17, 3346883.42;
435754.39, 3346634.94; 435940.75, 3346652.19; 436154.72, 3346638.39; 436368.69, 3346683.25; 436368.69,
3346790.24
(iii) Note: Map of Unit 5, Gulf State Park (Map 6), follows:
eCFR graphic er30ja07.005.gif
View or download PDF
Choctawhatcee Beach Mouse (Peromyscus
polionotus allophrys)
(1) Critical habitat units are depicted for Okaloosa, Walton, and Bay Counties, Florida, on the maps below.
(2) The primary constituent elements of critical habitat for the Choctawhatchee beach mouse are the habitat
components that provide:
(i) A contiguous mosaic of primary, secondary, and scrub vegetation and dune structure, with a balanced level of
competition and predation and few or no competitive or predaceous nonnative species present, that collectively
provide foraging opportunities, cover, and burrow sites;
(ii) Primary and secondary dunes, generally dominated by sea oats (Uniola paniculata), that despite occasional
temporary impacts and reconfiguration from tropical storms and hurricanes, provide abundant food resources,
burrow sites, and protection from predators;
(iii) Scrub dunes, generally dominated by scrub oaks (Quercus spp.), that provide food resources and burrow sites,
and provide elevated refugia during and after intense flooding due to rainfall and/or hurricane-induced storm surge;
(iv) Functional, unobstructed habitat connections that facilitate genetic exchange, dispersal, natural exploratory
movements, and re-colonization of locally extirpated areas; and
(v) A natural light regime within the coastal dune ecosystem, compatible with the nocturnal activity of beach mice,
necessary for normal behavior, growth, and viability of all life stages.
(3) Critical habitat does not include man-made structures existing on the effective date of this rule and not
containing one or more of the primary constituent elements, such as buildings, aqueducts, airports, driveways, and
roads, and the land on which such structures are located.
(4) Critical Habitat Map Units. Data layers defining map units were created by delineating habitats that contained
one or more of the primary constituent elements defined in paragraph (2) of this entry over 1999 and 2004 digital
ortho photography at a scale of at least 1:4000.
(5) Note: Map 1, Index Map of Critical Habitat Units for the Choctawhatchee beach mouse, follows:
eCFR graphic er12oc06.000.gif
View or download PDF
(6) CBM—Unit 1: Henderson Beach Unit, Okaloosa County, Florida.
(i) General Description: This unit encompasses essential features of beach mouse habitat within the boundary of
Henderson Beach State Park from 0.5 mi (0.8 km) east of the intersection of Highway 98 and Scenic Highway 98
to 0.25 mi (0.4 km) west of Matthew Boulevard and the area from the mean high water level (MHWL) north to the
seaward extent of the maritime forest.
(ii) Map of Unit CBM—Unit 1 is provided at paragraph (7)(ii) of this entry.
(7) CBM—Unit 2: Topsail Hill Unit, Walton County, Florida.
(i) General Description: This unit encompasses essential features of beach mouse habitat within the boundary of
Topsail Hill Preserve State Park, as well as adjacent private lands from 0.1 mi (0.2 km) east of Gulf Pines 0.6 mi (1
km) west of the inlet of Oyster Lake and the area from the MHWL north to the seaward extent of human
development or maritime forest.
(ii) Map 2, Units 1 and 2 of Choctowhatchee beach mouse, follows:
eCFR graphic er12oc06.001.gif
View or download PDF
(8) CBM—Unit 3: Grayton Beach Unit, Walton County, Florida.
(i) General Description: This unit encompasses essential features of beach mouse habitat within the boundary of
Grayton Beach State Park, as well as adjacent private lands and inholdings, from 0.3 mi west of the inlet of
Alligator Lake east to 0.8 mi west of Seagrove Beach and the area from the MHWL north to the seaward extent of
human development or maritime forest.
(ii) Map of Unit CBM—Unit 3 is provided at paragraph (9)(ii) of this entry.
(9) CBM—Unit 4: Deer Lake Unit, Walton County, Florida.
(i) General Description: This unit encompasses essential features of beach mouse habitat within the boundary of
Deer Lake State Park as well as adjacent private lands from approximately 1 mi east of the Camp Creek Lake inlet
west to approximately 0.5 mi west of the inlet of Deer Lake and the area from the MHWL north to the seaward
extent of maritime forest or human development. The area excluded within this unit is 0.5 mi west of the Camp
Creek Lake inlet, to 0.5 mi east of the Camp Creek Lake inlet.
(ii) Map 3, Units 3 and 4 of Choctowhatchee beach mouse, follows:
eCFR graphic er12oc06.002.gif
View or download PDF
(10) CBM—Unit 5: West Crooked Island/Shell Island Unit, Bay County, Florida.
(i) General Description: This unit encompasses essential features of beach mouse habitat within the boundaries of
St. Andrew State Park mainland from 0.1 mi (0.2 km) east of trailer park road east to the entrance channel of St.
Andrew Sound, Shell Island east of the entrance of St. Andrew Sound east to East Pass, and West Crooked Island
southwest of East Bay and east of the entrance channel of St. Andrew Sound, and areas from the MHWL north to
the seaward extent of the maritime forest. Shell Island consists of State lands, Tyndall Air Force Base lands, as
well as small private inholdings.
(ii) Map 4, Unit 5 of Choctowhatchee beach mouse, follows:
eCFR graphic er12oc06.003.gif
View or download PDF
New Mexico Meadow Jumping Mouse
(Zapus hudsonius luteus)
(1) Critical habitat units are depicted for Colfax, Mora, Otero, Sandoval, and Socorro Counties in New Mexico; Las
Animas, Archuleta, and La Plata Counties in Colorado; and Greenlee and Apache Counties in Arizona on the
maps below.
(2) Within these areas, the primary constituent elements of the physical or biological features essential to the
conservation of the New Mexico meadow jumping mouse consist of the following:
(i) Riparian communities along rivers and streams, springs and wetlands, or canals and ditches that contain:
(A) Persistent emergent herbaceous wetlands especially characterized by presence of primarily forbs and sedges
(Carex spp. or Schoenoplectus pungens); or
(B) Scrub-shrub riparian areas that are dominated by willows (Salix spp.) or alders (Alnus spp.) with an understory
of primarily forbs and sedges; and
(ii) Flowing water that provides saturated soils throughout the New Mexico meadow jumping mouse's active
season that supports tall (average stubble height of herbaceous vegetation of at least 61 centimeters (24 inches))
and dense herbaceous riparian vegetation composed primarily of sedges (Carex spp. or Schoenoplectus pungens)
and forbs, including, but not limited to, one or more of the following associated species: Spikerush (Eleocharis
macrostachya), beaked sedge (Carex rostrata), rushes (Juncus spp. and Scirpus spp.), and numerous species of
grasses such as bluegrass (Poa spp.), slender wheatgrass (Elymus trachycaulus), brome (Bromus spp.), foxtail
barley (Hordeum jubatum), or Japanese brome (Bromus japonicas), and forbs such as water hemlock (Circuta
douglasii), field mint (Mentha arvense), asters (Aster spp.), or cutleaf coneflower (Rudbeckia laciniata); and
(iii) Sufficient areas of 9 to 24 kilometers (5.6 to 15 miles) along a stream, ditch, or canal that contain suitable or
restorable habitat to support movements of individual New Mexico meadow jumping mice; and
(iv) Adjacent floodplain and upland areas extending approximately 100 meters (330 feet) outward from the
boundary between the active water channel and the floodplain (as defined by the bankfull stage of streams) or
from the top edge of the ditch or canal.
(3) Critical habitat does not include manmade structures (such as buildings, fire lookout stations, runways, roads,
and other paved areas) and the land on which they are located existing within the legal boundaries on April 15,
2016.
(4) Critical habitat map units. Data layers defining map units were created using the USA Contiguous Albers Equal
Area Conic USGS version projection. The maps in this entry, as modified by any accompanying regulatory text,
establish the boundaries of the critical habitat designation. The coordinates or plot points or both on which each
map is based are available to the public at the Service's internet
site http://www.fws.gov/southwest/es/NewMexico/,at http://www.regulations.gov at Docket No. FWS-R2-ES-20130014, and at the New Mexico Ecological Services Field Office. You may obtain field office location information by
contacting one of the Service regional offices, the addresses of which are listed at 50 CFR 2.2.
(5) Note: General Locations of Critical Habitat for the New Mexico Meadow Jumping Mouse—Overview, follows:
eCFR graphic er16mr16.002.gif
View or download PDF
(6) Unit 1—Sugarite Canyon. Map follows:
eCFR graphic er16mr16.003.gif
View or download PDF
(7) Unit 2—Coyote Creek. Map follows:
eCFR graphic er16mr16.004.gif
View or download PDF
(8) Unit 3—Jemez Mountains. Map follows:
eCFR graphic er16mr16.005.gif
View or download PDF
(9) Unit 4—Sacramento Mountains. Map follows:
eCFR graphic er16mr16.006.gif
View or download PDF
(10) Unit 5—White Mountains. Map follows:
eCFR graphic er16mr16.007.gif
View or download PDF
(11) Unit 6—Bosque del Apache National Wildlife Refuge (NWR). Map follows:
eCFR graphic er16mr16.008.gif
View or download PDF
(12) Unit 7—Florida River. Map follows:
eCFR graphic er16mr16.009.gif
View or download PDF
(13) Unit 8—Sambrito Creek. Map follows:
eCFR graphic er16mr16.010.gif
View or download PDF
Perdido Key Beach Mouse (Peromyscus
polionotus trissyllepsis)
(1) Critical habitat units are depicted for Escambia County, Florida, and Baldwin County, Alabama, on the maps
below. The maps provided are for informational purposes only.
(2) The primary constituent elements of critical habitat for the Perdido Key beach mouse are the habitat
components that provide:
(i) A contiguous mosaic of primary, secondary, and scrub vegetation and dune structure, with a balanced level of
competition and predation and few or no competitive or predaceous nonnative species present, that collectively
provide foraging opportunities, cover, and burrow sites;
(ii) Primary and secondary dunes, generally dominated by sea oats (Uniola paniculata), that despite occasional
temporary impacts and reconfiguration from tropical storms and hurricanes, provide abundant food resources,
burrow sites, and protection from predators;
(iii) Scrub dunes, generally dominated by scrub oaks (Quercus spp.), that provide food resources and burrow sites,
and provide elevated refugia during and after intense flooding due to rainfall and/or hurricane-induced storm surge;
(iv) Functional, unobstructed habitat connections that facilitate genetic exchange, dispersal, natural exploratory
movements, and re-colonization of locally extirpated areas; and
(v) A natural light regime within the coastal dune ecosystem, compatible with the nocturnal activity of beach mice,
necessary for normal behavior, growth, and viability of all life stages.
(3) Critical habitat does not include man-made structures existing on the effective date of this rule and not
containing one or more of the primary constituent elements, such as buildings, aqueducts, airports, driveways, and
roads, and the land on which such structures are located.
(4) Critical Habitat Map Units. Data layers defining map units were created by delineating habitats that contained
one or more of the primary constituent elements defined in paragraph (2) of this entry over 1999 and 2004 digital
ortho photography at a scale of at least 1:4000.
(5) Note: Map 1 Index of Critical Habitat Units for the Perdido Key beach mouse, follows:
eCFR graphic er12oc06.004.gif
View or download PDF
(6) PKBM—Unit 1: Gulf State Park Unit, Baldwin County, Alabama.
(i) General Description: This unit encompasses essential features of beach mouse habitat within the boundary of
Gulf State Park from the west tip of Perdido Key at Perdido Pass east to approximately 1 mile (mi) (1.6 kilometers
(km)) west of where the Alabama-Florida State line bisects Perdido Key and the area from the mean high water
line (MHWL) north to the seaward extent of the maritime forest.
(ii) Coordinates: From USGS 1:24,000 quadrangle map Orange Beach, Alabama, land bounded by the following
UTM 16 NAD 83 coordinates (E, N): 447646.90, 3349472.01; 447492.27, 3349555.80; 447493.46, 3349550.54;
447492.60, 3349542.06; 447487.33, 3349540.88; 447466.10, 3349542.49; 447426.82, 3349545.78; 447375.87,
3349549.84; 447340.75, 3349556.40; 447277.86, 3349571.81; 447233.09, 3349583.43; 447195.90, 3349587.83;
447123.74, 3349592.44; 447082.29, 3349597.80; 447078.83, 3349609.34; 447082.64, 3349627.40; 447085.56,
3349638.04; 447109.06, 3349630.15; 447163.55, 3349611.36; 447228.62, 3349592.84; 447286.11, 3349581.52;
447357.41, 3349568.43; 447388.22, 3349564.94; 447403.20, 3349558.95; 447426.52, 3349558.45; 447454.05,
3349559.11; 447492.27, 3349555.80; 447753.29, 3349711.25; 447760.77, 3349736.04; 447763.66, 3349748.00;
447753.63, 3349752.12; 447755.48, 3349774.36; 447753.59, 3349787.00; 447754.47, 3349799.71; 447754.38,
3349820.32; 447753.74, 3349830.21; 447759.54, 3349836.69; 447811.82, 3349827.24; 447838.09, 3349825.09;
447856.72, 3349827.12; 447881.09, 3349821.36; 447907.36, 3349819.61; 447927.64, 3349818.91; 447956.65,
3349818.81; 447976.22, 3349830.77; 447992.63, 3349834.16; 448018.40, 3349831.12; 448037.09, 3349811.22;
448055.79, 3349802.71; 448074.40, 3349792.17; 448096.41, 3349792.70; 448114.76, 3349793.13; 448137.03,
3349782.68; 448148.04, 3349782.94; 448177.22, 3349790.96; 448191.45, 3349809.62; 448209.62, 3349817.37;
448223.94, 3349832.37; 448249.45, 3349840.30; 448279.80, 3349846.35; 448291.40, 3349859.70; 448311.29,
3349863.75; 448329.64, 3349864.19; 448368.33, 3349865.90; 448395.77, 3349862.11; 448408.04, 3349866.45;
448418.04, 3349851.65; 448427.89, 3349850.68; 448440.83, 3349857.72; 448448.65, 3349863.06; 448458.22,
3349861.71; 448474.31, 3349870.02; 448470.39, 3349848.77; 448469.37, 3349841.61; 448469.94, 3349834.09;
448470.06, 3349746.49; 448388.10, 3349722.76; 448274.81, 3349701.74; 448066.73, 3349652.82; 447964.62,
3349624.75; 447754.92, 3349599.15; 447753.29, 3349711.25; 446828.18, 3349177.08; 446788.74, 3349181.69;
446769.28, 3349208.86; 446767.28, 3349247.92; 446775.25, 3349280.06; 446782.18, 3349322.24; 446795.01,
3349350.69; 446801.51, 3349377.80; 446802.73, 3349409.54; 446811.99, 3349454.15; 446837.56, 3349514.61;
446896.76, 3349564.39; 446887.98, 3349582.41; 446896.11, 3349607.97; 446929.73, 3349630.57; 446953.02,
3349637.08; 446969.73, 3349626.62; 446984.14, 3349637.95; 446975.34, 3349650.69; 447000.06, 3349663.57;
447022.45, 3349657.76; 446993.88, 3349639.64; 446978.89, 3349585.37; 447068.47, 3349561.35; 447073.43,
3349586.44; 447084.44, 3349589.07; 447091.86, 3349585.59; 447128.34, 3349583.00; 447157.81, 3349580.13;
447188.50, 3349576.11; 447214.39, 3349573.56; 447263.87, 3349564.83; 447299.49, 3349553.79; 447327.56,
3349543.36; 447355.96, 3349535.32; 447401.54, 3349530.72; 447419.98, 3349527.50; 447464.09, 3349524.89;
447482.44, 3349525.33; 447508.12, 3349525.95; 447511.26, 3349547.99; 447515.63, 3349553.80; 447584.64,
3349549.75; 447669.02, 3349551.76; 447727.64, 3349556.83; 447771.68, 3349563.09; 447773.34, 3349543.71;
447819.71, 3349544.38; 447859.81, 3349556.32; 447908.03, 3349560.00; 447904.75, 3349580.93; 448004.65,
3349606.71; 448136.88, 3349636.19; 448391.19, 3349691.65; 448518.76, 3349723.23; 448524.37, 3349644.98;
448526.52, 3349626.07; 448221.97, 3349557.49; 447946.22, 3349481.14; 447525.39, 3349356.93; 447160.19,
3349255.19; 446914.86, 3349191.20; 446828.18, 3349177.08.
(7) PKBM—Unit 2: West Perdido Key Unit, Escambia County, Florida and Baldwin County, Alabama.
(i) General Description: This unit encompasses essential features of beach mouse habitat from approximately 1 mi
(1.6 km) west of where the Alabama-Florida State line bisects Perdido Key east to 2 mi (3.2 km) east of the State
line and areas from the MHWL north to the seaward extent of human development or maritime forest.
(ii) Coordinates: From USGS 1:24,000 quadrangle maps Orange Beach, Alabama, and Perdido Bay, Florida, land
bounded by the following UTM 16 NAD 83 coordinates (E, N): 449337.40, 3349820.75; 450150.23, 3349948.99;
450150.07, 3349948.96; 450110.12, 3349941.87; 450036.74, 3349928.41; 449865.78, 3349900.01; 449835.15,
3349896.11; 449690.43, 3349877.85; 449581.98, 3349849.89; 449474.18, 3349830.25; 449291.67, 3349805.96;
449065.07, 3349756.15; 448929.16, 3349724.36; 448875.44, 3349711.41; 448743.75, 3349669.31; 448625.71,
3349643.24; 448526.52, 3349626.07; 448524.37, 3349644.98; 448582.14, 3349648.54; 448616.00, 3349650.40;
448613.50, 3349666.20; 448653.71, 3349668.22; 448707.46, 3349680.07; 448743.29, 3349688.33; 448749.74,
3349684.25; 448769.63, 3349694.24; 448784.54, 3349701.88; 448869.86, 3349722.95; 448909.84, 3349734.47;
448934.12, 3349738.22; 449040.54, 3349762.96; 449044.67, 3349767.29; 449126.91, 3349784.05; 449134.20,
3349789.51; 449165.89, 3349793.44; 449202.65, 3349802.14; 449234.33, 3349810.93; 449243.92, 3349809.05;
449309.24, 3349824.35; 449309.24, 3349824.35; 449309.03, 3349832.80; 449303.36, 3349848.52; 449299.95,
3349857.95; 449300.81, 3349866.43; 449296.47, 3349870.55; 449289.06, 3349870.38; 449288.58, 3349890.45;
449323.34, 3349898.68; 449326.60, 3349895.58; 449326.77, 3349888.19; 449328.04, 3349879.76; 449327.05,
3349876.57; 449322.97, 3349870.13; 449323.12, 3349863.79; 449324.31, 3349858.53; 449326.55, 3349853.30;
449327.79, 3349845.93; 449327.99, 3349837.48; 449328.02, 3349827.71; 449349.32, 3349831.65; 449351.57,
3349826.42; 449405.37, 3349835.22; 449424.38, 3349838.73; 449471.57, 3349851.46; 449471.73, 3349857.40;
449598.16, 3349884.71; 449597.83, 3349942.84; 449467.18, 3349912.24; 449415.42, 3349902.99; 449412.39,
3349896.58; 449407.02, 3349899.62; 449400.21, 3349918.48; 449467.76, 3349932.33; 449630.01, 3349967.31;
449632.67, 3349947.90; 449633.28, 3349922.55; 449635.69, 3349907.20; 449651.69, 3349906.08; 449655.72,
3349914.63; 449657.84, 3349914.68; 449659.22, 3349900.97; 449671.93, 3349901.28; 449704.63, 3349909.34;
449701.77, 3349935.20; 449697.15, 3349950.95; 449693.77, 3349959.32; 449695.36, 3349981.56; 449749.08,
3349994.47; 449749.23, 3349988.13; 449750.02, 3349955.38; 449752.10, 3349914.61; 449752.10, 3349914.61;
449784.74, 3349920.41; 449810.13, 3349923.00; 449829.12, 3349929.34; 449908.19, 3349946.03; 449906.59,
3349965.47; 449916.14, 3349964.64; 449939.36, 3349968.36; 449973.07, 3349976.57; 449987.92, 3349975.87;
449997.55, 3349971.87; 450020.80, 3349974.54; 450046.16, 3349979.98; 450059.87, 3349979.70; 450073.54,
3349984.26; 450083.98, 3349993.57; 450150.23, 3350009.73; 450150.42, 3350009.76; 450150.23, 3349948.99;
449645.50, 3350072.32; 449649.58, 3350078.76; 449664.33, 3350082.29; 449686.52, 3350084.93; 449692.67,
3350093.53; 449689.18, 3350106.13; 449699.78, 3350109.11; 449698.49, 3350118.59; 449711.15, 3350121.01;
449718.69, 3350115.91; 449720.88, 3350112.79; 449727.18, 3350115.05; 449729.43, 3350109.82; 449734.72,
3350109.95; 449734.85, 3350104.67; 449741.20, 3350104.82; 449747.35, 3350110.70; 449746.11, 3350118.07;
449753.17, 3350133.03; 449766.51, 3350154.04; 449770.74, 3350154.14; 449780.27, 3350154.37; 449784.41,
3350158.70; 449796.06, 3350158.98; 449800.19, 3350163.30; 449820.20, 3350165.29; 449836.95, 3350176.87;
449846.83, 3350162.31; 449864.86, 3350161.68; 449863.00, 3350151.07; 449862.95, 3350106.06; 449864.06,
3350059.58; 449858.12, 3350045.25; 449809.57, 3350037.75; 449792.67, 3350035.23; 449777.98, 3350029.59;
449740.99, 3350025.54; 449731.61, 3350018.97; 449682.10, 3350007.22; 449656.73, 3350001.77; 449645.50,
3350072.32; 449183.65, 3349894.89; 449180.35, 3349900.10; 449183.30, 3349909.68; 449185.19, 3349919.24;
449179.33, 3349942.35; 449179.68, 3349971.96; 449179.67, 3350016.35; 449190.00, 3350024.44; 449202.63,
3350027.92; 449213.17, 3350030.28; 449223.76, 3350030.53; 449233.19, 3350034.99; 449238.23, 3350045.68;
449241.18, 3350057.99; 449257.92, 3350066.84; 449259.39, 3350049.96; 449254.17, 3350046.67; 449254.54,
3350028.10; 449267.25, 3350028.40; 449268.11, 3350039.60; 449263.72, 3350045.84; 449259.99, 3350069.00;
449277.86, 3350074.72; 449287.31, 3350075.39; 449288.07, 3350043.70; 449290.42, 3350034.24; 449299.15,
3350026.60; 449319.22, 3350029.20; 449321.96, 3350044.51; 449322.67, 3350062.05; 449322.39, 3350073.67;
449345.66, 3350075.28; 449348.49, 3350001.36; 449370.76, 3350000.83; 449371.24, 3349980.76; 449347.99,
3349978.09; 449347.49, 3349954.83; 449369.78, 3349953.25; 449376.54, 3349936.50; 449337.51, 3349929.22;
449285.77, 3349918.92; 449284.24, 3350026.69; 449282.88, 3350039.35; 449277.26, 3350052.95; 449273.32,
3350040.17; 449280.01, 3350026.59; 449280.53, 3349916.68; 449270.02, 3349913.26; 449264.66, 3350004.03;
449267.50, 3350017.84; 449259.94, 3350024.00; 449254.80, 3350017.54; 449259.36, 3350003.90; 449263.66,
3349913.10; 449247.89, 3349911.22; 449183.65, 3349894.89; 448986.63, 3349848.96; 448984.08, 3349866.87;
449010.37, 3349874.89; 449009.13, 3349882.33; 449009.48, 3349911.87; 449010.16, 3349938.64; 449016.10,
3349942.07; 449029.89, 3349941.34; 449042.45, 3349947.98; 449046.24, 3349955.61; 449053.79, 3349960.94;
449059.04, 3349963.18; 449067.58, 3349960.21; 449076.03, 3349961.47; 449077.94, 3349969.97; 449069.29,
3349977.16; 449064.14, 3349984.23; 449069.97, 3349993.03; 449086.10, 3350002.68; 449090.98, 3350014.29;
449118.25, 3350020.49; 449121.70, 3349992.83; 449110.55, 3349982.99; 449119.27, 3349972.63; 449113.69,
3349962.12; 449144.10, 3349936.68; 449142.83, 3349923.57; 449123.43, 3349920.73; 449110.13, 3349912.16;
449097.12, 3349924.53; 449083.32, 3349919.77; 449081.13, 3349911.79; 449094.43, 3349903.79; 449091.08,
3349894.59; 449091.44, 3349879.54; 449082.50, 3349871.33; 448986.63, 3349848.96; 449534.56, 3349974.10;
449526.69, 3349990.21; 449526.10, 3350014.51; 449526.92, 3350027.82; 449526.03, 3350064.79; 449532.28,
3350069.17; 449536.21, 3350081.95; 449540.37, 3350085.22; 449542.44, 3350087.38; 449541.22, 3350093.70;
449560.26, 3350095.21; 449570.72, 3350100.74; 449573.97, 3350097.65; 449581.27, 3350058.71; 449605.57,
3350061.41; 449606.37, 3350069.27; 449620.16, 3350068.55; 449629.69, 3350068.78; 449639.30, 3350065.83;
449648.06, 3350010.02; 449650.38, 3350001.62; 449644.16, 3349998.91; 449534.56, 3349974.10; 449635.33,
3349966.38; 449660.57, 3349974.38; 449661.78, 3349968.07; 449662.01, 3349958.56; 449658.02, 3349947.90;
449656.26, 3349933.06; 449654.53, 3349917.16; 449647.99, 3349924.40; 449646.35, 3349948.68; 449638.84,
3349952.72; 449635.33, 3349966.38; 449152.59, 3349861.83; 449172.61, 3349866.53; 449175.94, 3349860.27;
449177.25, 3349849.73; 449179.67, 3349837.11; 449177.68, 3349831.78; 449172.41, 3349830.59; 449166.16,
3349826.22; 449167.32, 3349822.01; 449163.16, 3349818.74; 449158.75, 3349826.04; 449156.37, 3349836.55;
449152.87, 3349850.21; 449151.63, 3349857.58; 449152.59, 3349861.83; 449086.18, 3349847.56; 449106.25,
3349850.15; 449110.69, 3349841.80; 449110.92, 3349832.29; 449108.17, 3349814.26; 449107.32, 3349805.78;
449103.21, 3349800.40; 449098.97, 3349800.30; 449097.74, 3349807.67; 449093.37, 3349812.85; 449089.01,
3349818.03; 449086.18, 3349847.56; 448967.14, 3349819.34; 448986.09, 3349824.03; 448991.44, 3349822.04;
448991.67, 3349812.53; 448992.93, 3349804.11; 448994.24, 3349793.57; 448994.50, 3349783.00; 448988.25,
3349778.63; 448983.71, 3349791.20; 448981.41, 3349798.55; 448972.66, 3349809.96; 448967.14, 3349819.34;
449331.74, 3349902.05; 449345.48, 3349903.43; 449351.21, 3349885.60; 449348.28, 3349874.96; 449350.63,
3349865.50; 449353.86, 3349863.47; 449355.04, 3349858.21; 449346.57, 3349858.01; 449343.11, 3349869.55;
449341.95, 3349873.75; 449334.54, 3349873.58; 449331.74, 3349902.05; 448994.54, 3349825.28; 449008.23,
3349828.78; 449012.67, 3349820.43; 449016.15, 3349807.83; 449018.52, 3349797.32; 449015.60, 3349786.68;
449008.21, 3349785.45; 449003.80, 3349792.74; 448998.33, 3349800.01; 448995.85, 3349814.75; 448994.54,
3349825.28; 449019.80, 3349832.23; 449034.60, 3349833.64; 449036.95, 3349824.18; 449039.24, 3349816.84;
449035.13, 3349811.46; 449032.11, 3349805.04; 449032.24, 3349799.76; 449037.81, 3349788.27; 449031.48,
3349787.06; 449023.79, 3349798.50; 449018.22, 3349810.00; 449017.96, 3349820.56; 449019.80, 3349832.23;
449133.68, 3349855.03; 449137.84, 3349858.31; 449145.35, 3349854.26; 449148.66, 3349849.05; 449152.06,
3349839.62; 449154.38, 3349831.22; 449153.50, 3349823.80; 449150.50, 3349816.33; 449146.40, 3349810.94;
449139.99, 3349812.91; 449141.83, 3349824.58; 449141.68, 3349830.91; 449139.48, 3349834.03; 449137.21,
3349840.32; 449134.89, 3349848.72; 449133.68, 3349855.03; 449369.71, 3349909.30; 449383.37, 3349913.85;
449387.96, 3349899.16; 449388.27, 3349886.49; 449389.53, 3349878.06; 449383.33, 3349871.57; 449383.51,
3349864.18; 449379.27, 3349864.08; 449378.01, 3349872.50; 449382.09, 3349878.94; 449377.73, 3349884.12;
449372.26, 3349891.39; 449369.71, 3349909.30; 449115.70, 3349853.55; 449123.12, 3349853.73; 449128.59,
3349846.46; 449135.12, 3349839.21; 449135.27, 3349832.88; 449135.40, 3349827.59; 449129.12, 3349824.27;
449124.89, 3349824.17; 449120.73, 3349820.90; 449124.06, 3349814.64; 449124.18, 3349809.36; 449117.83,
3349809.21; 449115.51, 3349817.61; 449115.41, 3349821.83; 449118.48, 3349826.13; 449117.27, 3349832.45;
449117.07, 3349840.90; 449115.70, 3349853.55; 449350.70, 3349906.73; 449360.15, 3349910.13; 449360.38,
3349900.62; 449362.65, 3349894.33; 449368.02, 3349891.29; 449367.14, 3349883.87; 449366.13, 3349881.73;
449370.80, 3349863.87; 449365.50, 3349863.75; 449363.01, 3349879.54; 449356.60, 3349881.50; 449354.36,
3349886.73; 449350.70, 3349906.73; 449065.16, 3349840.71; 449077.79, 3349844.19; 449082.30, 3349832.67;
449084.73, 3349820.04; 449082.81, 3349811.54; 449081.93, 3349804.12; 449082.08, 3349797.78; 449076.79,
3349797.65; 449074.49, 3349805.00; 449069.02, 3349812.27; 449067.86, 3349816.47; 449065.39, 3349831.21;
449065.16, 3349840.71; 449043.05, 3349834.90; 449054.59, 3349839.40; 449060.12, 3349830.02; 449061.38,
3349821.60; 449061.66, 3349809.98; 449057.55, 3349804.59; 449057.83, 3349792.97; 449055.71, 3349792.92;
449053.26, 3349806.61; 449049.96, 3349811.81; 449045.67, 3349813.82; 449043.28, 3349825.39; 449043.05,
3349834.90; 449264.32, 3349885.64; 449272.72, 3349889.01; 449282.27, 3349888.18; 449282.35, 3349885.01;
449284.67, 3349876.61; 449284.77, 3349872.39; 449281.67, 3349869.14; 449278.60, 3349864.84; 449279.78,
3349859.58; 449281.00, 3349853.27; 449281.10, 3349849.04; 449276.78, 3349852.11; 449272.45, 3349856.24;
449267.98, 3349865.64; 449264.50, 3349878.24; 449264.32, 3349885.64; 448931.31, 3349811.09; 448937.61,
3349813.35; 448944.04, 3349810.34; 448946.26, 3349806.16; 448950.70, 3349797.81; 448950.93, 3349788.30;
448951.16, 3349778.80; 448942.76, 3349775.43; 448935.25, 3349779.47; 448931.82, 3349789.96; 448929.40,
3349802.59; 448931.31, 3349811.09; 449671.10, 3349976.75; 449686.94, 3349979.24; 449687.39, 3349960.23;
449680.41, 3349942.09; 449675.35, 3349932.46; 449672.70, 3349954.59; 449671.10, 3349976.75; 448952.46,
3349812.65; 448956.65, 3349814.87; 448959.83, 3349814.94; 448969.56, 3349806.72; 448975.03, 3349799.45;
448976.19, 3349795.25; 448975.34, 3349786.77; 448966.92, 3349784.46; 448959.35, 3349790.62; 448952.77,
3349799.98; 448952.46, 3349812.65; 449216.88, 3349876.05; 449226.36, 3349878.39; 449229.96, 3349860.51;
449231.33, 3349847.86; 449234.76, 3349837.37; 449229.46, 3349837.24; 449230.47, 3349839.38; 449227.04,
3349849.87; 449222.76, 3349851.88; 449220.36, 3349863.45; 449216.88, 3349876.05; 449197.94, 3349870.31;
449206.34, 3349873.68; 449208.53, 3349870.56; 449213.83, 3349870.69; 449215.27, 3349854.87; 449215.52,
3349844.31; 449214.69, 3349834.77; 449209.40, 3349834.65; 449208.26, 3349837.79; 449206.87, 3349851.50;
449198.35, 3349853.41; 449197.94, 3349870.31; 448919.34, 3349780.15; 448913.94, 3349784.25; 448910.54,
3349793.68; 448910.31, 3349803.19; 448913.36, 3349808.55; 448922.89, 3349808.77; 448925.21, 3349800.37;
448927.74, 3349783.52; 448927.84, 3349779.30; 448919.34, 3349780.15; 449181.03, 3349868.85; 449188.39,
3349871.14; 449192.10, 3349849.03; 449187.86, 3349848.93; 449188.37, 3349827.80; 449185.19, 3349827.73;
449181.03, 3349868.85; 449249.53, 3349884.23; 449259.06, 3349884.46; 449260.29, 3349877.09; 449262.56,
3349870.80; 449262.71, 3349864.46; 449261.83, 3349857.04; 449259.89, 3349849.60; 449256.62, 3349853.74;
449251.07, 3349864.18; 449250.84, 3349873.69; 449249.53, 3349884.23; 448901.31, 3349780.78; 448893.77,
3349785.88; 448891.45, 3349794.28; 448891.28, 3349801.68; 448896.47, 3349806.03; 448903.93, 3349804.09;
448906.25, 3349795.69; 448906.53, 3349784.07; 448901.31, 3349780.78; 449233.74, 3349879.62; 449242.16,
3349881.94; 449244.41, 3349876.71; 449246.73, 3349868.31; 449240.53, 3349861.82; 449234.12, 3349863.78;
449231.80, 3349872.18; 449233.74, 3349879.62; 451993.83, 3350371.03; 452703.05, 3350634.99; 452704.03,
3350638.18; 452710.36, 3350639.39; 452712.53, 3350637.33; 452713.66, 3350634.18; 452713.79, 3350628.90;
452714.04, 3350618.34; 452713.24, 3350607.75; 452706.89, 3350607.60; 452702.62, 3350608.55; 452703.05,
3350634.99; 453782.71, 3350897.59; 453793.28, 3350898.90; 453796.56, 3350894.75; 453795.98, 3350874.65;
453797.45, 3350857.78; 453794.37, 3350853.47; 453785.62, 3350864.89; 453784.28, 3350876.49; 453782.71,
3350897.59; 450607.54, 3350204.19; 450615.96, 3350206.51; 450619.29, 3350200.25; 450619.64, 3350185.46;
450620.07, 3350167.50; 450618.16, 3350159.00; 450611.83, 3350157.79; 450608.58, 3350160.88; 450606.26,
3350169.28; 450608.12, 3350179.90; 450608.93, 3350190.49; 450608.77, 3350196.82; 450607.54, 3350204.19;
451881.55, 3350474.76; 451896.33, 3350477.22; 451896.60, 3350465.60; 451895.88, 3350451.84; 451894.09,
3350438.06; 451890.91, 3350437.98; 451891.01, 3350433.76; 451890.13, 3350426.34; 451883.80, 3350425.13;
451884.13, 3350455.79; 451882.76, 3350468.44; 451881.55, 3350474.76; 450624.43, 3350206.71; 450631.79,
3350209.00; 450631.94, 3350202.66; 450633.10, 3350198.46; 450633.38, 3350186.84; 450633.56, 3350179.45;
450632.65, 3350173.08; 450635.96, 3350167.88; 450645.46, 3350169.16; 450645.64, 3350161.77; 450640.50,
3350155.30; 450635.23, 3350154.12; 450629.86, 3350157.16; 450624.41, 3350163.37; 450622.51, 3350198.21;
450624.43, 3350206.71; 451488.80, 3350547.04; 451486.14, 3350528.67; 451481.23, 3350526.18; 451480.66,
3350531.56; 451479.21, 3350574.06; 451443.72, 3350573.86; 451444.14, 3350574.42; 451446.66, 3350577.81;
451450.92, 3350580.50; 451452.58, 3350585.93; 451485.88, 3350587.38; 451486.86, 3350582.65; 451496.61,
3350582.02; 451499.58, 3350575.62; 451488.80, 3350547.04; 450383.09, 3350287.25; 450382.53, 3350310.49;
450397.20, 3350317.18; 450408.85, 3350317.46; 450423.63, 3350319.93; 450436.31, 3350321.29; 450455.24,
3350327.02; 450458.47, 3350324.99; 450459.75, 3350315.50; 450444.98, 3350313.04; 450440.75, 3350312.94;
450440.97, 3350303.43; 450399.93, 3350291.88; 450383.09, 3350287.25; 453015.92, 3350797.85; 453023.26,
3350800.16; 453023.39, 3350794.88; 453031.86, 3350795.08; 453034.25, 3350783.51; 453044.87, 3350783.75;
453046.03, 3350735.15; 453019.66, 3350730.29; 453015.92, 3350797.85; 450422.77, 3350179.33; 450422.23,
3350201.51; 450422.66, 3350227.94; 450422.12, 3350250.13; 450427.19, 3350259.76; 450432.21, 3350271.51;
450430.89, 3350282.05; 450439.29, 3350285.42; 450443.57, 3350283.41; 450440.36, 3350196.66; 450435.07,
3350196.53; 450435.42, 3350181.74; 450422.77, 3350179.33; 451937.55, 3350481.38; 451958.60, 3350487.17;
451971.25, 3350489.58; 451970.75, 3350466.32; 451969.27, 3350439.86; 451966.58, 3350419.71; 451956.01,
3350418.40; 451947.52, 3350419.26; 451944.19, 3350425.52; 451942.98, 3350431.83; 451943.55, 3350451.93;
451942.21, 3350463.52; 451937.55, 3350481.38; 451666.83, 3350567.39; 451674.24, 3350567.57; 451679.69,
3350561.36; 451689.19, 3350562.64; 451695.14, 3350580.68; 451703.51, 3350585.10; 451713.63, 3350561.04;
451713.17, 3350534.68; 451713.83, 3350507.21; 451703.07, 3350515.33; 451696.06, 3350522.11; 451685.44,
3350522.91; 451684.18, 3350531.34; 451680.27, 3350538.04; 451669.53, 3350543.15; 451666.83, 3350567.39;
451405.16, 3350583.71; 451417.86, 3350584.41; 451419.36, 3350571.37; 451417.02, 3350536.43; 451418.01,
3350478.98; 451411.54, 3350466.94; 451392.65, 3350470.91; 451392.01, 3350497.32; 451394.32, 3350532.34;
451403.43, 3350540.07; 451403.22, 3350548.79; 451400.78, 3350551.11; 451403.84, 3350555.94; 451403.19,
3350561.01; 451395.73, 3350562.95; 451394.72, 3350571.57; 451403.42, 3350573.37; 451405.16, 3350583.71;
451930.48, 3350526.11; 451932.49, 3350530.13; 451942.72, 3350534.34; 451947.14, 3350537.71; 451946.11,
3350546.44; 451943.92, 3350552.70; 451936.14, 3350553.73; 451932.25, 3350554.05; 451930.93, 3350558.29;
451936.10, 3350561.93; 451943.31, 3350559.33; 451940.80, 3350564.42; 451940.69, 3350569.17; 451944.88,
3350576.41; 451940.48, 3350576.85; 451941.12, 3350584.24; 451944.29, 3350584.72; 451943.23, 3350589.74;
451940.89, 3350593.75; 451944.82, 3350595.43; 451948.30, 3350599.48; 451947.29, 3350607.76; 451951.96,
3350612.65; 451952.18, 3350620.18; 451954.10, 3350622.61; 451959.36, 3350618.77; 451956.28, 3350614.73;
451957.21, 3350609.20; 451960.13, 3350608.47; 451963.53, 3350610.54; 451964.55, 3350617.70; 451969.34,
3350617.03; 451970.22, 3350613.48; 451967.17, 3350607.86; 451973.20, 3350605.23; 451977.53, 3350606.92;
451977.63, 3350602.56; 451977.04, 3350594.22; 451976.76, 3350589.06; 451972.82, 3350581.69; 451966.97,
3350578.91; 451971.96, 3350573.88; 451971.11, 3350567.81; 451966.44, 3350566.68; 451962.15, 3350567.19;
451955.89, 3350564.78; 451956.52, 3350555.28; 451959.38, 3350551.78; 451966.62, 3350548.39; 451969.80,
3350554.34; 451973.17, 3350556.87; 451979.53, 3350556.62; 451980.50, 3350549.12; 451976.29, 3350542.67;
451970.01, 3350539.35; 451965.40, 3350532.90; 451963.55, 3350527.31; 451959.28, 3350525.17; 451952.32,
3350526.02; 451952.14, 3350533.35; 451948.67, 3350533.47; 451948.85, 3350527.35; 451944.13, 3350525.26;
451941.54, 3350524.34; 451937.84, 3350522.33; 451928.95, 3350521.59; 451930.48, 3350526.11; 453147.41,
3350803.69; 453142.42, 3350788.61; 453137.09, 3350787.42; 453139.57, 3350854.72; 453138.43, 3350865.43;
453144.36, 3350874.24; 453150.85, 3350885.10; 453157.00, 3350893.57; 453164.77, 3350900.89; 453169.90,
3350902.60; 453170.14, 3350892.69; 453168.94, 3350876.41; 453167.40, 3350857.75; 453168.67, 3350805.06;
453167.49, 3350795.14; 453158.12, 3350801.82; 453147.41, 3350803.69; 452001.33, 3350604.46; 452004.74,
3350595.03; 452006.03, 3350585.55; 452002.95, 3350581.24; 451999.85, 3350578.00; 452003.10, 3350574.91;
452007.24, 3350579.23; 452013.64, 3350577.27; 452021.08, 3350576.39; 452025.34, 3350575.44; 452029.68,
3350571.31; 452028.77, 3350564.95; 452031.97, 3350563.97; 452032.08, 3350559.74; 452033.39, 3350549.21;
452033.57, 3350541.81; 452035.68, 3350541.86; 452038.78, 3350545.11; 452035.33, 3350556.65; 452036.18,
3350565.13; 452033.84, 3350574.58; 452036.86, 3350581.00; 452042.13, 3350582.18; 452049.59, 3350580.25;
452053.85, 3350579.29; 452054.03, 3350571.90; 452054.21, 3350564.50; 452050.08, 3350560.17; 452050.20,
3350554.89; 452052.47, 3350548.61; 452052.75, 3350536.99; 452049.73, 3350530.57; 452041.26, 3350530.37;
452030.82, 3350523.78; 452027.42, 3350533.21; 452022.93, 3350543.67; 452011.30, 3350542.34; 452011.46,
3350536.00; 452020.00, 3350533.03; 452024.29, 3350531.02; 452023.38, 3350524.66; 452016.07, 3350520.25;
452009.77, 3350517.99; 452002.36, 3350517.81; 451994.97, 3350516.58; 451985.44, 3350516.35; 451983.98,
3350533.23; 451982.76, 3350583.93; 451982.38, 3350599.78; 451992.91, 3350602.14; 452001.33, 3350604.46;
450499.59, 3350334.35; 450512.17, 3350339.93; 450518.65, 3350334.80; 450527.20, 3350331.83; 450534.43,
3350339.41; 450544.01, 3350336.54; 450543.28, 3350322.79; 450545.04, 3350205.50; 450514.49, 3350199.41;
450515.08, 3350262.84; 450515.68, 3350326.27; 450502.94, 3350327.03; 450499.59, 3350334.35; 451834.39,
3350514.14; 451832.67, 3350519.45; 451838.51, 3350522.33; 451843.31, 3350521.26; 451842.63, 3350526.22;
451845.91, 3350528.85; 451852.11, 3350528.03; 451855.80, 3350530.28; 451855.17, 3350524.74; 451859.95,
3350523.86; 451862.44, 3350519.17; 451869.59, 3350518.95; 451868.38, 3350528.22; 451862.42, 3350528.47;
451860.99, 3350530.02; 451864.40, 3350536.64; 451868.09, 3350540.29; 451870.15, 3350545.29; 451873.10,
3350546.15; 451871.53, 3350537.20; 451875.72, 3350536.51; 451879.49, 3350536.21; 451881.87, 3350536.46;
451885.51, 3350541.70; 451892.21, 3350543.64; 451892.29, 3350548.59; 451891.79, 3350553.73; 451884.93,
3350558.33; 451877.73, 3350560.13; 451873.56, 3350560.02; 451872.89, 3350569.53; 451866.85, 3350566.33;
451862.15, 3350566.63; 451862.53, 3350576.21; 451863.56, 3350584.17; 451860.26, 3350594.07; 451865.05,
3350598.66; 451867.19, 3350602.99; 451869.47, 3350606.31; 451869.79, 3350609.49; 451865.78, 3350610.90;
451864.82, 3350618.09; 451863.90, 3350623.22; 451866.58, 3350627.25; 451870.94, 3350627.75; 451876.22,
3350623.12; 451882.58, 3350622.88; 451885.86, 3350618.60; 451888.63, 3350619.06; 451893.39, 3350619.57;
451895.77, 3350619.76; 451898.84, 3350619.22; 451902.86, 3350622.17; 451906.52, 3350618.69; 451912.14,
3350616.45; 451919.16, 3350621.77; 451921.66, 3350617.07; 451918.37, 3350613.58; 451919.30, 3350600.37;
451915.40, 3350601.29; 451914.63, 3350595.50; 451917.50, 3350591.61; 451925.21, 3350592.37; 451925.74,
3350587.29; 451924.27, 3350580.33; 451921.16, 3350573.94; 451919.29, 3350566.97; 451913.66, 3350569.71;
451908.32, 3350560.47; 451912.40, 3350555.81; 451912.92, 3350550.67; 451913.87, 3350544.35; 451911.04,
3350536.37; 451906.11, 3350536.63; 451903.04, 3350538.75; 451899.67, 3350538.87; 451898.42, 3350541.41;
451888.52, 3350540.38; 451889.01, 3350536.43; 451884.88, 3350535.15; 451885.38, 3350522.29; 451880.28,
3350520.16; 451876.73, 3350519.28; 451877.23, 3350514.94; 451871.13, 3350512.65; 451865.71, 3350515.29;
451866.05, 3350509.36; 451857.34, 3350508.36; 451857.81, 3350513.72; 451855.05, 3350513.06; 451854.13,
3350518.38; 451849.84, 3350515.31; 451845.06, 3350514.56; 451839.94, 3350514.08; 451834.39, 3350514.14;
452962.77, 3350805.04; 452964.66, 3350813.56; 452970.74, 3350825.33; 452974.90, 3350828.60; 452982.44,
3350823.50; 452984.73, 3350816.15; 452995.45, 3350811.12; 453004.98, 3350811.35; 453013.47, 3350811.53;
453014.37, 3350730.17; 452985.98, 3350721.03; 452963.85, 3350716.27; 452962.77, 3350805.04; 450352.08,
3350300.17; 450360.45, 3350303.62; 450368.97, 3350302.68; 450368.35, 3350284.70; 450380.02, 3350283.92;
450383.57, 3350267.18; 450398.82, 3350269.80; 450396.94, 3350240.01; 450396.42, 3350173.41; 450390.95,
3350180.68; 450384.57, 3350181.58; 450358.25, 3350174.61; 450355.43, 3350205.12; 450381.72, 3350213.14;
450376.82, 3350240.51; 450355.80, 3350233.66; 450354.46, 3350245.26; 450359.58, 3350252.78; 450358.29,
3350262.26; 450345.53, 3350264.07; 450341.58, 3350252.35; 450350.25, 3350244.10; 450351.70, 3350183.89;
450345.34, 3350183.74; 450344.01, 3350195.33; 450345.31, 3350229.19; 450323.18, 3350224.43; 450323.73,
3350245.58; 450325.41, 3350263.59; 450351.68, 3350272.67; 450352.08, 3350300.17; 452961.76, 3350715.17;
452944.84, 3350712.67; 452926.94, 3350708.01; 452896.41, 3350700.92; 452897.21, 3350711.51; 452900.22,
3350717.94; 452898.39, 3350749.61; 452897.86, 3350771.79; 452904.06, 3350778.28; 452916.67, 3350782.81;
452916.57, 3350787.04; 452927.13, 3350788.35; 452927.96, 3350797.88; 452936.43, 3350798.08; 452947.02,
3350798.34; 452952.14, 3350805.86; 452959.70, 3350800.73; 452960.37, 3350728.87; 452961.76, 3350715.17;
452779.43, 3350674.87; 452757.35, 3350668.00; 452750.92, 3350671.01; 452746.48, 3350679.36; 452744.77,
3350706.28; 452754.34, 3350710.66; 452782.86, 3350717.62; 452805.09, 3350724.81; 452810.67, 3350737.88;
452807.62, 3350780.18; 452803.63, 3350813.91; 452808.72, 3350822.49; 452806.34, 3350847.86; 452821.98,
3350851.37; 452825.42, 3350838.90; 452840.06, 3350840.30; 452840.17, 3350792.59; 452811.60, 3350790.85;
452811.91, 3350778.17; 452840.55, 3350776.53; 452839.30, 3350740.78; 452816.00, 3350740.22; 452816.84,
3350726.27; 452830.71, 3350721.50; 452839.75, 3350721.76; 452842.48, 3350696.46; 452838.42, 3350688.96;
452779.43, 3350674.87; 450547.49, 3350324.92; 450561.28, 3350324.19; 450566.35, 3350333.83; 450559.77,
3350343.18; 450586.16, 3350346.99; 450591.84, 3350331.27; 450603.49, 3350331.54; 450615.34, 3350323.37;
450615.63, 3350222.97; 450549.48, 3350207.56; 450548.25, 3350292.25; 450547.49, 3350324.92; 452716.99,
3350739.66; 452724.84, 3350716.41; 452763.08, 3350728.01; 452752.89, 3350753.28; 452761.35, 3350755.60;
452758.35, 3350791.67; 452779.52, 3350797.50; 452790.15, 3350798.81; 452799.96, 3350789.48; 452801.09,
3350742.74; 452798.15, 3350732.04; 452719.99, 3350707.38; 452701.88, 3350703.16; 452660.61, 3350691.54;
452642.40, 3350689.56; 452628.63, 3350691.84; 452622.04, 3350700.19; 452618.44, 3350717.11; 452617.14,
3350726.64; 452634.16, 3350728.11; 452635.45, 3350718.58; 452640.83, 3350716.58; 452646.20, 3350714.58;
452648.23, 3350718.88; 452654.44, 3350726.47; 452656.34, 3350736.08; 452659.46, 3350739.35; 452663.64,
3350742.64; 452659.25, 3350747.85; 452653.93, 3350747.72; 452650.61, 3350752.95; 452642.21, 3350747.44;
452639.02, 3350747.36; 452639.88, 3350755.89; 452669.47, 3350766.16; 452680.06, 3350768.54; 452683.59,
3350754.81; 452689.43, 3350733.69; 452707.40, 3350739.43; 452697.00, 3350773.20; 452712.87, 3350777.83;
452713.10, 3350768.27; 452709.93, 3350767.13; 452710.19, 3350756.51; 452710.37, 3350749.07; 452716.76,
3350749.22; 452721.12, 3350745.07; 452716.99, 3350739.66; 450916.02, 3350287.31; 450857.03, 3350273.21;
450851.53, 3350281.54; 450849.99, 3350301.58; 450848.47, 3350320.57; 450849.20, 3350334.33; 450849.95,
3350347.03; 450856.83, 3350369.39; 450857.69, 3350377.87; 450866.13, 3350379.13; 450865.98, 3350385.47;
450872.18, 3350391.96; 450873.04, 3350400.43; 450872.61, 3350418.39; 450876.38, 3350437.51; 450883.57,
3350447.19; 450882.98, 3350471.49; 450892.51, 3350471.72; 450897.66, 3350478.18; 450912.48, 3350478.54;
450918.94, 3350474.46; 450918.41, 3350452.25; 450918.62, 3350399.41; 450915.85, 3350382.43; 450916.88,
3350295.78; 450916.02, 3350287.31; 451489.88, 3350479.66; 451489.12, 3350511.35; 451491.85, 3350531.09;
451498.62, 3350557.03; 451504.59, 3350573.03; 451504.26, 3350586.76; 451500.73, 3350601.47; 451503.67,
3350611.06; 451513.82, 3350608.51; 451509.96, 3350554.51; 451505.70, 3350533.40; 451506.09, 3350517.16;
451511.66, 3350500.25; 451521.25, 3350498.10; 451535.17, 3350497.24; 451552.25, 3350497.65; 451568.31,
3350507.15; 451567.25, 3350523.71; 451565.79, 3350540.59; 451565.33, 3350559.60; 451552.29, 3350573.03;
451553.02, 3350586.79; 451555.49, 3350610.69; 451564.55, 3350613.69; 451562.37, 3350605.31; 451569.15,
3350599.87; 451569.42, 3350593.19; 451575.11, 3350593.66; 451579.21, 3350599.04; 451585.03, 3350604.66;
451593.34, 3350606.45; 451603.14, 3350595.19; 451612.97, 3350599.39; 451622.58, 3350602.19; 451631.30,
3350591.83; 451630.60, 3350577.02; 451632.22, 3350553.80; 451647.07, 3350552.64; 451662.92, 3350553.56;
451660.12, 3350449.91; 451629.43, 3350443.61; 451623.63, 3350486.67; 451613.70, 3350486.77; 451596.78,
3350484.33; 451594.84, 3350477.66; 451585.77, 3350475.07; 451583.88, 3350471.06; 451588.07, 3350462.04;
451596.77, 3350463.83; 451604.77, 3350461.25; 451620.99, 3350464.41; 451623.87, 3350443.48; 451598.21,
3350436.92; 451579.63, 3350432.90; 451566.31, 3350429.70; 451553.50, 3350433.62; 451553.32, 3350441.01;
451551.00, 3350449.41; 451545.01, 3350451.50; 451546.65, 3350466.20; 451545.85, 3350482.83; 451539.55,
3350485.08; 451531.06, 3350486.44; 451526.70, 3350485.94; 451518.35, 3350485.63; 451502.99, 3350480.62;
451489.88, 3350479.66; 452229.34, 3350643.46; 452234.37, 3350649.13; 452230.66, 3350671.24; 452227.35,
3350692.96; 452235.69, 3350693.16; 452242.42, 3350694.11; 452241.52, 3350698.45; 452248.23, 3350700.59;
452249.21, 3350692.69; 452255.99, 3350691.66; 452259.76, 3350700.08; 452264.13, 3350700.18; 452271.74,
3350697.59; 452276.79, 3350702.47; 452282.03, 3350699.42; 452291.58, 3350698.46; 452297.38, 3350705.34;
452300.04, 3350710.16; 452305.96, 3350711.88; 452319.45, 3350712.60; 452324.50, 3350717.48; 452332.33,
3350722.42; 452338.68, 3350722.58; 452344.12, 3350727.86; 452352.47, 3350727.27; 452362.30, 3350731.86;
452364.38, 3350727.95; 452359.27, 3350725.45; 452358.68, 3350717.11; 452365.13, 3350696.65; 452365.14,
3350679.61; 452369.46, 3350665.44; 452376.54, 3350651.74; 452382.49, 3350652.28; 452384.51, 3350584.54;
452340.63, 3350575.57; 452342.86, 3350581.96; 452347.58, 3350584.06; 452357.92, 3350583.51; 452364.95,
3350588.44; 452364.02, 3350594.36; 452367.99, 3350600.57; 452362.22, 3350603.04; 452357.33, 3350603.48;
452350.95, 3350604.39; 452343.51, 3350605.27; 452337.22, 3350601.65; 452332.63, 3350594.40; 452329.59,
3350588.38; 452334.89, 3350582.96; 452331.48, 3350576.14; 452319.56, 3350575.86; 452319.86, 3350580.22;
452316.52, 3350586.88; 452310.50, 3350589.12; 452304.52, 3350590.16; 452304.80, 3350594.93; 452295.15,
3350599.85; 452289.63, 3350598.13; 452292.17, 3350591.45; 452295.42, 3350588.76; 452299.46, 3350585.68;
452297.98, 3350581.29; 452304.47, 3350575.50; 452302.20, 3350571.08; 452291.83, 3350572.81; 452288.98,
3350575.52; 452290.43, 3350581.11; 452292.30, 3350586.30; 452282.99, 3350593.21; 452282.31, 3350588.44;
452278.69, 3350590.34; 452274.27, 3350592.21; 452276.44, 3350584.73; 452280.54, 3350579.68; 452283.48,
3350573.01; 452279.52, 3350572.52; 452275.79, 3350578.77; 452271.61, 3350587.39; 452267.97, 3350590.08;
452263.72, 3350585.22; 452257.50, 3350579.52; 452252.02, 3350575.83; 452251.77, 3350569.87; 452247.42,
3350568.98; 452245.16, 3350580.42; 452238.88, 3350593.74; 452229.73, 3350593.92; 452229.99, 3350616.13;
452229.14, 3350635.13; 452229.34, 3350643.46; 452586.29, 3350643.82; 452589.65, 3350636.50; 452594.03,
3350630.27; 452575.48, 3350623.60; 452472.77, 3350598.94; 452465.48, 3350600.76; 452465.76, 3350609.48;
452459.58, 3350625.99; 452456.15, 3350636.48; 452453.40, 3350660.71; 452448.52, 3350689.15; 452449.15,
3350707.13; 452452.10, 3350716.71; 452460.15, 3350710.42; 452462.86, 3350713.65; 452459.90, 3350721.11;
452456.92, 3350729.37; 452459.55, 3350735.38; 452467.52, 3350734.38; 452477.42, 3350735.80; 452484.12,
3350738.34; 452486.13, 3350754.54; 452485.52, 3350762.55; 452492.62, 3350764.71; 452500.13, 3350782.72;
452517.41, 3350791.06; 452522.81, 3350771.28; 452537.48, 3350779.01; 452545.98, 3350778.15; 452548.31,
3350767.56; 452548.13, 3350752.95; 452574.51, 3350746.45; 452575.13, 3350755.60; 452599.62, 3350759.73;
452612.16, 3350757.54; 452610.95, 3350750.89; 452611.29, 3350705.72; 452617.09, 3350684.72; 452624.66,
3350678.56; 452657.41, 3350682.52; 452719.50, 3350699.86; 452729.03, 3350700.09; 452733.47, 3350691.74;
452738.03, 3350678.10; 452739.35, 3350667.57; 452734.15, 3350663.21; 452644.50, 3350646.27; 452636.89,
3350654.54; 452632.17, 3350674.51; 452618.56, 3350667.85; 452618.76, 3350659.40; 452606.10, 3350656.98;
452594.43, 3350657.76; 452585.70, 3350652.75; 452586.29, 3350643.82; 451758.79, 3350379.88; 451764.08,
3350380.01; 451766.61, 3350363.16; 451795.10, 3350368.07; 451792.78, 3350376.47; 451824.52, 3350378.28;
451822.41, 3350465.96; 451871.90, 3350475.19; 451877.52, 3350466.20; 451879.70, 3350419.75; 451869.39,
3350407.87; 451854.66, 3350403.29; 451858.30, 3350384.35; 451875.21, 3350385.82; 451877.08, 3350396.43;
451912.02, 3350397.27; 451911.49, 3350419.45; 451903.95, 3350424.56; 451898.40, 3350434.99; 451901.04,
3350457.25; 451902.65, 3350478.43; 451930.13, 3350481.20; 451934.70, 3350467.57; 451936.09, 3350453.86;
451936.55, 3350434.85; 451923.99, 3350428.21; 451919.98, 3350418.60; 451921.45, 3350401.72; 451941.62,
3350400.09; 451968.07, 3350401.78; 451988.21, 3350401.20; 452030.44, 3350407.50; 452034.35, 3350421.33;
452034.13, 3350474.18; 452045.53, 3350485.02; 452060.02, 3350499.11; 452061.44, 3350484.34; 452056.34,
3350475.77; 452050.14, 3350469.28; 452039.07, 3350467.98; 452039.83, 3350457.40; 452049.39, 3350456.57;
452049.72, 3350442.84; 452046.67, 3350437.48; 452041.63, 3350426.79; 452049.30, 3350416.41; 452062.96,
3350420.96; 452063.59, 3350438.94; 452059.25, 3350443.07; 452057.68, 3350464.17; 452064.82, 3350475.97;
452068.70, 3350490.86; 452070.25, 3350426.42; 452073.58, 3350420.16; 452123.19, 3350427.69; 452122.89,
3350440.36; 452129.37, 3350435.23; 452127.40, 3350428.84; 452149.54, 3350432.56; 452173.79, 3350437.37;
452189.57, 3350441.98; 452218.09, 3350445.83; 452224.29, 3350453.36; 452243.37, 3350451.72; 452270.83,
3350455.55; 452279.25, 3350458.90; 452288.80, 3350457.04; 452293.17, 3350451.86; 452305.72, 3350458.50;
452305.59, 3350463.78; 452327.68, 3350470.65; 452348.90, 3350470.08; 452358.61, 3350462.91; 452401.75,
3350474.54; 452427.06, 3350480.41; 452449.20, 3350484.13; 452469.34, 3350484.59; 452485.20, 3350486.02;
452494.60, 3350490.50; 452513.66, 3350490.95; 452510.99, 3350514.14; 452498.28, 3350513.84; 452490.63,
3350524.21; 452492.26, 3350588.72; 452567.58, 3350605.87; 452565.91, 3350566.17; 452547.96, 3350563.63;
452546.24, 3350523.97; 452558.92, 3350525.33; 452555.02, 3350511.50; 452563.51, 3350510.64; 452565.25,
3350526.54; 452574.73, 3350528.88; 452574.97, 3350607.10; 452607.72, 3350611.06; 452607.38, 3350537.06;
452598.96, 3350534.75; 452601.14, 3350510.99; 452637.56, 3350515.59; 452632.35, 3350535.00; 452613.94,
3350551.47; 452610.58, 3350603.18; 452612.94, 3350614.35; 452637.14, 3350621.28; 452642.65, 3350591.26;
452635.96, 3350582.14; 452636.85, 3350567.87; 452634.79, 3350565.71; 452636.75, 3350549.39; 452643.25,
3350543.20; 452661.13, 3350548.92; 452658.26, 3350558.87; 452654.83, 3350569.36; 452651.87, 3350581.46;
452649.40, 3350596.20; 452643.44, 3350623.54; 452667.64, 3350630.46; 452668.07, 3350612.50; 452682.20,
3350598.04; 452671.42, 3350584.55; 452664.70, 3350576.48; 452666.27, 3350555.38; 452687.37, 3350559.06;
452686.89, 3350579.13; 452689.29, 3350590.26; 452688.50, 3350600.31; 452675.49, 3350612.68; 452672.94,
3350630.59; 452696.08, 3350637.48; 452696.40, 3350603.12; 452692.37, 3350594.57; 452693.00, 3350568.16;
452722.70, 3350566.75; 452724.13, 3350595.33; 452719.62, 3350606.84; 452720.90, 3350641.76; 452763.54,
3350651.78; 452766.63, 3350634.39; 452768.10, 3350617.52; 452766.80, 3350604.30; 452756.34, 3350598.76;
452754.92, 3350592.89; 452748.20, 3350584.82; 452749.59, 3350571.12; 452763.46, 3350567.22; 452769.01,
3350579.49; 452768.63, 3350595.33; 452775.05, 3350614.01; 452773.53, 3350633.00; 452768.81, 3350652.97;
452858.34, 3350675.19; 452861.94, 3350657.31; 452862.83, 3350620.33; 452843.48, 3350610.87; 452842.27,
3350594.47; 452845.72, 3350582.93; 452867.88, 3350586.63; 452866.09, 3350617.24; 452865.45, 3350643.65;
452862.60, 3350674.23; 452872.52, 3350680.29; 452875.35, 3350650.76; 452883.89, 3350647.79; 452887.27,
3350639.42; 452889.11, 3350651.09; 452893.30, 3350653.30; 452888.68, 3350669.05; 452881.27, 3350668.87;
452876.78, 3350679.33; 452983.11, 3350707.24; 452985.16, 3350667.10; 452982.59, 3350641.68; 452970.19,
3350628.70; 452971.71, 3350608.67; 452984.44, 3350607.92; 452989.59, 3350614.38; 452985.97, 3350633.30;
452986.86, 3350640.72; 452988.41, 3350664.01; 452986.29, 3350707.32; 453028.42, 3350717.84; 453029.65,
3350711.51; 453017.07, 3350705.92; 453018.54, 3350689.04; 453017.89, 3350671.08; 453019.41, 3350652.09;
453022.84, 3350641.60; 453026.29, 3350631.09; 453046.26, 3350637.91; 453075.85, 3350640.74; 453078.12,
3350634.45; 453086.59, 3350634.65; 453105.50, 3350641.45; 453133.94, 3350648.47; 453148.74, 3350649.88;
453170.85, 3350655.69; 453184.49, 3350661.30; 453193.86, 3350667.87; 453218.14, 3350671.62; 453257.02,
3350685.24; 453273.86, 3350689.87; 453287.65, 3350689.14; 453293.90, 3350693.52; 453323.40, 3350700.57;
453326.65, 3350697.47; 453344.60, 3350700.02; 453353.98, 3350706.58; 453364.98, 3350710.57; 453370.49,
3350724.95; 453369.72, 3350733.93; 453362.64, 3350742.73; 453365.98, 3350757.10; 453359.38, 3350767.51;
453351.14, 3350780.50; 453343.50, 3350789.83; 453350.24, 3350794.77; 453463.37, 3350827.58; 453465.69,
3350796.48; 453445.20, 3350790.15; 453455.89, 3350763.48; 453479.06, 3350769.32; 453468.42, 3350793.88;
453469.16, 3350828.27; 453512.42, 3350835.65; 453516.18, 3350811.43; 453526.07, 3350796.87; 453521.86,
3350795.71; 453522.93, 3350774.05; 453538.28, 3350773.91; 453535.57, 3350798.15; 453529.22, 3350798.00;
453517.17, 3350814.62; 453515.57, 3350836.78; 453528.23, 3350839.20; 453532.90, 3350821.34; 453537.39,
3350810.88; 453543.87, 3350805.75; 453547.65, 3350780.47; 453558.34, 3350776.50; 453568.36, 3350779.36;
453568.37, 3350799.99; 453562.38, 3350807.76; 453555.49, 3350807.08; 453541.57, 3350813.09; 453531.41,
3350839.27; 453565.80, 3350848.41; 453584.46, 3350853.19; 453586.35, 3350834.15; 453590.14, 3350819.13;
453585.65, 3350809.37; 453583.15, 3350800.73; 453573.20, 3350798.78; 453572.24, 3350794.25; 453575.98,
3350771.09; 453588.66, 3350772.45; 453585.93, 3350797.75; 453591.00, 3350807.38; 453593.88, 3350818.08;
453590.49, 3350828.51; 453588.47, 3350853.01; 453590.71, 3350854.77; 453594.50, 3350838.12; 453602.99,
3350814.56; 453610.55, 3350808.40; 453610.78, 3350798.89; 453605.46, 3350799.82; 453607.05, 3350777.67;
453617.62, 3350778.97; 453620.87, 3350775.88; 453625.08, 3350777.04; 453624.95, 3350782.32; 453632.80,
3350787.24; 453627.23, 3350798.74; 453623.31, 3350806.59; 453610.40, 3350814.74; 453603.77, 3350826.21;
453594.06, 3350856.08; 453664.14, 3350870.99; 453667.03, 3350861.02; 453671.52, 3350850.55; 453672.96,
3350834.73; 453673.19, 3350825.23; 453664.82, 3350820.80; 453666.03, 3350814.49; 453660.84, 3350810.13;
453666.54, 3350793.36; 453671.93, 3350789.26; 453683.56, 3350790.59; 453689.65, 3350802.35; 453681.86,
3350816.98; 453678.46, 3350826.41; 453674.64, 3350852.74; 453668.89, 3350871.63; 453735.29, 3350886.94;
453747.12, 3350878.79; 453747.28, 3350872.45; 453748.74, 3350855.57; 453768.76, 3350860.28; 453763.99,
3350882.36; 453759.70, 3350884.38; 453760.58, 3350891.80; 453776.39, 3350896.38; 453781.44, 3350862.68;
453775.26, 3350854.09; 453775.82, 3350831.89; 453795.89, 3350834.48; 453804.44, 3350830.48; 453822.44,
3350830.91; 453826.52, 3350837.35; 453826.34, 3350845.78; 453830.32, 3350856.45; 453829.97, 3350871.24;
453826.44, 3350884.92; 453824.97, 3350901.79; 453835.77, 3350905.26; 453837.42, 3350781.57; 453760.40,
3350768.10; 453697.23, 3350751.79; 453582.57, 3350717.34; 453497.31, 3350694.16; 453375.32, 3350656.36;
453257.43, 3350623.94; 453175.30, 3350602.95; 453083.60, 3350582.79; 452998.22, 3350564.89; 452884.39,
3350539.97; 452754.93, 3350504.10; 452628.45, 3350476.77; 452524.18, 3350451.02; 452447.21, 3350435.44;
452351.28, 3350415.17; 452237.43, 3350391.31; 452155.65, 3350375.09; 452081.85, 3350359.58; 451991.22,
3350339.44; 451924.69, 3350330.45; 451859.24, 3350320.43; 451769.41, 3350310.89; 451769.41, 3350310.89;
451649.99, 3350298.52; 451523.50, 3350271.18; 451402.47, 3350237.63; 451202.24, 3350192.68; 451034.69,
3350153.10; 450914.58, 3350124.86; 450834.59, 3350102.87; 450737.55, 3350084.69; 450597.48, 3350049.63;
450480.68, 3350016.19; 450366.83, 3349992.32; 450291.95, 3349977.85; 450240.94, 3349965.09; 450150.23,
3349948.99; 450150.42, 3350009.76; 450160.82, 3350011.71; 450213.79, 3350011.92; 450212.02, 3350044.20;
450231.06, 3350045.71; 450230.37, 3350074.23; 450244.09, 3350076.67; 450240.20, 3350106.18; 450247.36,
3350116.92; 450266.24, 3350124.77; 450282.07, 3350127.26; 450349.44, 3350145.78; 450349.94, 3350124.65;
450321.38, 3350122.91; 450318.74, 3350100.65; 450352.57, 3350103.58; 450353.33, 3350071.89; 450317.30,
3350072.08; 450319.85, 3350054.17; 450344.08, 3350060.04; 450345.52, 3350044.22; 450376.28, 3350042.84;
450380.23, 3350051.84; 450380.96, 3350065.59; 450381.85, 3350075.74; 450378.61, 3350122.17; 450370.04,
3350126.19; 450367.33, 3350147.71; 450381.02, 3350151.21; 450380.31, 3350136.40; 450386.58, 3350099.11;
450391.90, 3350098.18; 450393.09, 3350092.92; 450420.41, 3350102.03; 450426.92, 3350095.84; 450415.35,
3350092.39; 450417.70, 3350082.94; 450442.02, 3350081.85; 450486.37, 3350090.92; 450492.42, 3350103.75;
450495.37, 3350113.33; 450519.54, 3350118.59; 450514.22, 3350166.63; 450525.68, 3350171.58; 450527.36,
3350148.98; 450525.82, 3350121.91; 450529.25, 3350111.42; 450571.24, 3350108.28; 450587.05, 3350111.83;
450590.47, 3350145.73; 450587.98, 3350180.47; 450584.60, 3350188.85; 450584.92, 3350200.56; 450601.29,
3350199.82; 450604.72, 3350189.33; 450601.97, 3350171.29; 450603.62, 3350147.02; 450605.28, 3350121.69;
450617.61, 3350118.90; 450625.82, 3350129.66; 450640.65, 3350130.02; 450641.91, 3350121.59; 450671.24,
3350129.95; 450688.61, 3350137.43; 450710.18, 3350146.48; 450735.11, 3350149.57; 450770.80, 3350158.05;
450801.85, 3350167.70; 450804.14, 3350160.35; 450813.67, 3350160.58; 450812.44, 3350167.95; 450850.68,
3350163.58; 450878.14, 3350167.41; 450877.83, 3350180.08; 450901.10, 3350181.70; 450898.37, 3350251.39;
450886.67, 3350253.23; 450878.10, 3350257.25; 450878.95, 3350265.73; 450948.43, 3350284.30; 450951.01,
3350265.34; 450941.45, 3350266.16; 450941.03, 3350239.73; 450947.41, 3350238.83; 450947.62, 3350206.67;
450940.31, 3350202.27; 450942.64, 3350193.87; 450952.29, 3350188.82; 450961.67, 3350195.38; 450959.40,
3350201.67; 450968.31, 3350206.56; 450968.92, 3350225.60; 450996.08, 3350219.38; 451013.00, 3350219.86;
451010.90, 3350264.13; 451005.95, 3350292.64; 451032.32, 3350297.49; 451038.64, 3350211.94; 451066.12,
3350214.71; 451089.29, 3350220.55; 451122.95, 3350230.87; 451138.73, 3350235.47; 451152.52, 3350233.77;
451169.43, 3350238.11; 451176.54, 3350248.08; 451231.43, 3350256.80; 451237.34, 3350254.21; 451250.54,
3350255.14; 451253.56, 3350261.55; 451279.91, 3350267.47; 451314.65, 3350276.75; 451333.31, 3350276.86;
451359.54, 3350283.56; 451376.77, 3350293.04; 451403.31, 3350290.50; 451431.19, 3350300.07; 451482.79,
3350312.93; 451488.83, 3350303.12; 451500.40, 3350306.57; 451505.39, 3350319.37; 451563.40, 3350330.27;
451586.37, 3350345.54; 451591.77, 3350341.44; 451617.05, 3350346.35; 451616.42, 3350373.74; 451604.75,
3350374.51; 451600.33, 3350381.81; 451597.00, 3350388.07; 451601.24, 3350388.17; 451598.87, 3350398.68;
451597.66, 3350405.00; 451595.38, 3350411.29; 451595.16, 3350420.79; 451717.43, 3350446.97; 451723.73,
3350449.24; 451724.67, 3350410.15; 451701.63, 3350399.03; 451699.79, 3350387.36; 451699.16, 3350369.37;
451704.59, 3350364.22; 451736.02, 3350378.71; 451758.79, 3350379.88; 450912.08, 3350186.80; 450914.09,
3350170.38; 450944.72, 3350174.28; 450941.70, 3350188.56; 450912.08, 3350186.80
(8) PKBM—Unit 3: Perdido Key State Park Unit, Escambia County, Florida.
(i) General Description: This unit encompasses essential features of beach mouse habitat within the boundary of
Perdido Key State Park from approximately 2 mi (3.2 km) east of the Alabama-Florida State line to 4 mi (6.4 km)
east of the State line and the area from the MHWL north to the seaward extent of the maritime forest.
(ii) Coordinates: From USGS 1:24,000 quadrangle map Perdido Bay, Florida, land bounded by the following UTM
16 NAD 83 coordinates (E,N): 455621.62, 3351458.88; 453257.58, 3350904.44; 453254.26, 3350917.23;
453243.75, 3350913.81; 453240.29, 3350925.36; 453247.80, 3350930.76; 453266.31, 3350945.01; 453287.10,
3350948.75; 453293.56, 3350957.28; 453304.30, 3350951.20; 453307.22, 3350961.84; 453312.72, 3350973.93;
453318.59, 3350973.74; 453318.26, 3350987.47; 453306.46, 3350993.53; 453320.42, 3351005.30; 453354.81,
3351009.49; 453352.19, 3351030.56; 453343.44, 3351041.98; 453350.93, 3351069.98; 453334.30, 3351069.24;
453335.11, 3351079.83; 453352.32, 3351078.33; 453351.11, 3351095.75; 453383.68, 3351130.67; 453392.08,
3351134.05; 453401.76, 3351127.94; 453398.49, 3351117.04; 453399.11, 3351091.42; 453407.07, 3351065.97;
453425.39, 3351063.44; 453442.62, 3351059.15; 453457.24, 3351067.96; 453455.20, 3351048.81; 453459.35,
3351038.88; 453458.55, 3351022.61; 453468.79, 3351028.07; 453479.38, 3351028.32; 453481.65, 3351022.03;
453488.13, 3351016.90; 453496.35, 3351016.84; 453509.90, 3351018.69; 453515.14, 3350998.97; 453518.96,
3350988.78; 453513.14, 3350983.09; 453523.52, 3350964.71; 453521.52, 3350950.06; 453530.87, 3350939.91;
453531.03, 3350916.53; 453541.83, 3350896.97; 453550.25, 3350901.06; 453554.18, 3350913.84; 453550.50,
3350934.89; 453541.67, 3350949.48; 453545.40, 3350970.71; 453555.76, 3350988.96; 453555.40, 3351003.60;
453550.66, 3351016.29; 453543.61, 3351036.28; 453531.06, 3351038.01; 453520.97, 3351061.03; 453519.56,
3351075.79; 453527.61, 3351090.83; 453541.93, 3351105.82; 453530.48, 3351123.86; 453526.55, 3351134.75;
453515.81, 3351123.51; 453508.38, 3351126.99; 453502.88, 3351152.55; 453502.62, 3351163.12; 453509.93,
3351167.52; 453529.60, 3351160.46; 453537.21, 3351149.66; 453541.05, 3351142.42; 453555.99, 3351131.79;
453560.54, 3351133.85; 453567.88, 3351137.20; 453589.10, 3351128.92; 453600.02, 3351132.85; 453599.58,
3351151.15; 453581.16, 3351157.60; 453569.70, 3351172.41; 453595.20, 3351180.34; 453606.30, 3351176.95;
453610.23, 3351166.05; 453610.41, 3351158.73; 453614.52, 3351140.52; 453613.04, 3351109.74; 453630.16,
3351100.61; 453637.50, 3351100.78; 453652.55, 3351096.94; 453659.33, 3351079.14; 453667.99, 3351053.90;
453666.63, 3351040.20; 453680.62, 3351031.02; 453689.01, 3351038.43; 453705.94, 3351037.47; 453716.32,
3351044.56; 453726.05, 3351036.34; 453744.28, 3351036.58; 453737.36, 3351059.80; 453729.59, 3351085.78;
453723.99, 3351103.88; 453714.19, 3351117.27; 453702.83, 3351131.65; 453698.82, 3351155.13; 453697.00,
3351186.79; 453705.00, 3351193.96; 453720.92, 3351198.14; 453727.28, 3351183.50; 453732.16, 3351177.00;
453729.16, 3351169.40; 453732.67, 3351156.01; 453739.08, 3351150.82; 453757.95, 3351129.30; 453780.31,
3351124.25; 453779.80, 3351112.35; 453789.19, 3351101.87; 453798.84, 3351108.31; 453806.26, 3351104.82;
453810.87, 3351092.48; 453826.85, 3351088.90; 453838.67, 3351076.50; 453847.06, 3351087.49; 453860.52,
3351083.95; 453858.95, 3351105.05; 453870.87, 3351108.98; 453912.75, 3351114.80; 453908.35, 3351122.11;
453893.36, 3351128.07; 453878.61, 3351134.13; 453875.18, 3351139.43; 453873.64, 3351155.08; 453865.09,
3351158.05; 453859.60, 3351166.37; 453867.71, 3351181.37; 453877.22, 3351182.65; 453877.26, 3351205.40;
453866.08, 3351212.46; 453862.15, 3351223.35; 453843.89, 3351219.25; 453840.40, 3351211.85; 453851.93,
3351190.15; 453852.20, 3351179.17; 453843.66, 3351168.11; 453830.93, 3351168.86; 453821.56, 3351176.77;
453816.10, 3351168.50; 453829.12, 3351156.13; 453821.78, 3351152.79; 453813.14, 3351163.48; 453812.54,
3351148.92; 453820.93, 3351144.31; 453816.89, 3351135.76; 453804.14, 3351137.56; 453789.16, 3351143.55;
453783.69, 3351150.82; 453777.03, 3351163.34; 453786.25, 3351173.93; 453786.07, 3351183.64; 453797.70,
3351184.98; 453796.18, 3351203.97; 453810.99, 3351203.47; 453815.94, 3351219.24; 453818.03, 3351225.96;
453838.68, 3351224.74; 453858.30, 3351230.59; 453880.40, 3351227.45; 453906.17, 3351224.41; 453918.44,
3351229.03; 453924.78, 3351213.87; 453926.60, 3351203.46; 453937.24, 3351197.83; 453941.20, 3351209.55;
453950.55, 3351210.82; 453969.07, 3351203.94; 453976.58, 3351196.79; 453980.43, 3351189.56; 453991.70,
3351178.84; 454005.42, 3351182.55; 454020.68, 3351179.16; 454018.85, 3351196.61; 454026.94, 3351212.66;
454038.78, 3351205.61; 454035.25, 3351190.08; 454039.40, 3351179.99; 454047.26, 3351158.20; 454055.13,
3351136.41; 454077.14, 3351136.94; 454088.15, 3351137.21; 454093.16, 3351146.60; 454102.56, 3351152.11;
454117.23, 3351148.89; 454122.61, 3351155.76; 454122.33, 3351167.38; 454135.89, 3351176.16; 454147.64,
3351172.21; 454163.34, 3351179.99; 454152.50, 3351190.30; 454150.08, 3351202.92; 454153.96, 3351217.81;
454149.39, 3351231.44; 454155.90, 3351252.61; 454151.83, 3351262.16; 454158.44, 3351267.07; 454166.31,
3351245.28; 454177.05, 3351226.82; 454185.36, 3351216.44; 454205.74, 3351223.28; 454218.29, 3351220.89;
454229.12, 3351228.47; 454257.45, 3351231.92; 454269.47, 3351229.44; 454276.90, 3351225.96; 454279.11,
3351212.35; 454273.94, 3351196.59; 454268.17, 3351182.50; 454256.12, 3351174.19; 454248.56, 3351160.89;
454260.23, 3351155.97; 454269.01, 3351147.63; 454275.54, 3351140.39; 454289.93, 3351142.03; 454308.10,
3351149.79; 454346.78, 3351173.81; 454344.52, 3351161.65; 454337.54, 3351146.84; 454356.24, 3351132.64;
454370.91, 3351132.99; 454383.06, 3351133.93; 454393.16, 3351050.13; 454259.82, 3351020.46; 454175.97,
3350996.48; 454062.76, 3350971.79; 453927.63, 3350942.92; 453734.15, 3350898.01; 453573.51, 3350861.20;
453456.55, 3350840.09; 453351.02, 3350814.91; 453319.38, 3350808.87; 453284.61, 3350800.63; 453255.17,
3350791.47; 453239.41, 3350785.81; 453240.65, 3350795.13; 453252.80, 3350801.99; 453252.19, 3350827.34;
453240.34, 3350835.51; 453238.90, 3350851.33; 453247.19, 3350858.93; 453257.58, 3350904.44; 453835.77,
3350905.26; 453973.20, 3350936.55; 453981.82, 3350930.42; 453994.73, 3350922.27; 454014.14, 3350907.94;
454040.57, 3350910.68; 454051.65, 3350905.08; 454070.27, 3350909.28; 454079.54, 3350920.07; 454108.94,
3350931.35; 454122.42, 3350943.30; 454130.49, 3350960.40; 454001.89, 3350933.01; 453991.09, 3350941.21;
454110.19, 3350967.31; 454139.71, 3350968.58; 454304.13, 3351008.95; 454388.27, 3351027.14; 454389.15,
3351007.34; 454409.63, 3350998.21; 454434.55, 3351002.88; 454465.72, 3351007.08; 454486.75, 3351012.85;
454489.63, 3351020.21; 454486.81, 3351034.46; 454498.15, 3351051.17; 454742.76, 3351106.18; 454998.00,
3351165.40; 455197.31, 3351203.86; 455211.78, 3351197.08; 455217.88, 3351175.24; 455229.15, 3351164.52;
455243.92, 3351161.21; 455269.42, 3351169.15; 455309.60, 3351177.43; 455316.76, 3351184.93; 455316.78,
3351209.13; 455308.03, 3351220.55; 455302.53, 3351228.87; 455310.51, 3351234.93; 455322.87, 3351236.35;
455704.01, 3351319.87; 456148.85, 3351387.97; 456419.46, 3351431.07; 456428.30, 3351369.03; 456430.63,
3351362.78; 456430.02, 3351338.59; 456424.48, 3351321.01; 456352.66, 3351308.62; 456246.79, 3351284.11;
456176.58, 3351274.11; 456062.92, 3351258.68; 455970.76, 3351241.70; 455830.67, 3351207.69; 455644.19,
3351164.12; 455466.91, 3351134.51; 455231.29, 3351063.33; 455133.43, 3351035.62; 455048.06, 3351016.67;
454963.71, 3350999.85; 454885.53, 3350990.58; 454798.88, 3350981.10; 454731.47, 3350964.69; 454634.86,
3350928.56; 454546.66, 3350917.56; 454464.36, 3350903.31; 454383.22, 3350890.27; 454306.59, 3350877.36;
454225.36, 3350862.73; 454123.01, 3350845.48; 454027.13, 3350823.11; 453939.68, 3350803.05; 453837.42,
3350781.57; 453835.77, 3350905.26; 455298.31, 3351139.98; 455302.68, 3351134.80; 455308.98, 3351137.07;
455304.59, 3351143.30; 455298.31, 3351139.98; 454143.72, 3350909.40; 454135.25, 3350909.20; 454136.48,
3350901.83; 454142.84, 3350901.98; 454143.72, 3350909.40; 454089.94, 3350898.60; 454082.53, 3350898.42;
454083.79, 3350890.00; 454091.18, 3350891.23; 454089.94, 3350898.60; 454036.17, 3350887.80; 454037.38,
3350881.49; 454045.80, 3350883.80; 454044.59, 3350890.12; 454036.12, 3350889.91; 454036.17, 3350887.80;
455261.41, 3351132.76; 455266.83, 3351127.60; 455275.22, 3351130.97; 455267.66, 3351137.14; 455261.41,
3351132.76; 455206.47, 3351126.16; 455206.62, 3351119.82; 455215.17, 3351116.85; 455217.16, 3351122.19;
455211.77, 3351126.28; 455206.47, 3351126.16; 455354.16, 3351152.95; 455359.63, 3351145.68; 455367.97,
3351151.16; 455360.41, 3351157.33; 455354.16, 3351152.95; 453996.99, 3350886.86; 453998.28, 3350877.38;
454008.84, 3350878.69; 454005.41, 3350889.18; 453996.99, 3350886.86; 454871.49, 3351419.62; 454871.23,
3351430.31; 454866.49, 3351437.83; 454884.66, 3351445.59; 454891.91, 3351449.43; 454906.50, 3351453.44;
454924.84, 3351453.88; 454939.60, 3351450.57; 454959.51, 3351443.92; 454978.23, 3351441.60; 454985.01,
3351424.32; 454974.36, 3351420.89; 454980.23, 3351399.31; 454980.01, 3351384.16; 454998.49, 3351389.18;
455013.87, 3351380.62; 455030.67, 3351375.86; 455041.91, 3351371.38; 455040.94, 3351385.97; 455028.71,
3351409.99; 455015.52, 3351429.75; 455003.62, 3351440.04; 455009.77, 3351448.64; 455031.95, 3351451.29;
455026.99, 3351437.43; 455036.80, 3351418.42; 455052.70, 3351418.01; 455050.39, 3351433.76; 455084.74,
3351458.89; 455103.91, 3351455.12; 455114.32, 3351462.77; 455158.84, 3351465.34; 455173.59, 3351465.25;
455199.83, 3351467.79; 455236.04, 3351467.80; 455243.51, 3351463.97; 455258.60, 3351463.77; 455273.98,
3351476.11; 455293.04, 3351485.60; 455297.90, 3351465.10; 455306.20, 3351457.85; 455313.44, 3351465.43;
455310.96, 3351480.16; 455321.35, 3351488.87; 455333.40, 3351472.25; 455347.56, 3351481.75; 455363.81,
3351485.66; 455371.95, 3351499.59; 455374.84, 3351511.29; 455387.35, 3351520.05; 455381.77, 3351531.54;
455383.56, 3351545.32; 455404.70, 3351550.90; 455428.85, 3351561.17; 455466.42, 3351561.49; 455495.81,
3351562.20; 455522.36, 3351564.82; 455557.30, 3351560.53; 455569.73, 3351572.45; 455582.60, 3351587.66;
455658.10, 3351603.74; 455665.53, 3351608.67; 455688.10, 3351618.65; 455720.85, 3351630.42; 455742.69,
3351638.26; 455771.95, 3351642.63; 455793.33, 3351647.01; 455819.65, 3351643.77; 455863.85, 3351637.50;
455887.99, 3351626.69; 455912.77, 3351620.54; 455970.60, 3351611.22; 456003.79, 3351618.88; 456021.77,
3351616.63; 456037.84, 3351623.93; 456051.55, 3351612.05; 456081.88, 3351628.64; 456112.16, 3351639.19;
456131.26, 3351645.67; 456148.88, 3351661.95; 456164.07, 3351670.33; 456178.33, 3351671.11; 456188.89,
3351672.42; 456185.02, 3351649.65; 456188.42, 3351648.10; 456198.90, 3351652.58; 456209.29, 3351648.25;
456220.35, 3351650.90; 456229.21, 3351663.48; 456248.37, 3351658.70; 456258.91, 3351649.84; 456290.20,
3351653.76; 456294.75, 3351676.01; 456313.24, 3351670.56; 456317.05, 3351660.74; 456316.66, 3351644.09;
456317.97, 3351622.71; 456316.08, 3351608.05; 456303.01, 3351596.94; 456301.10, 3351580.69; 456291.11,
3351578.15; 456287.70, 3351567.08; 456295.39, 3351552.62; 456308.39, 3351549.50; 456313.71, 3351548.57;
456329.65, 3351546.84; 456343.53, 3351535.46; 456358.64, 3351517.51; 456374.60, 3351527.83; 456380.04,
3351543.66; 456370.71, 3351557.34; 456357.63, 3351572.88; 456343.61, 3351583.11; 456345.16, 3351606.40;
456341.53, 3351625.34; 456345.28, 3351645.51; 456358.87, 3351660.35; 456358.70, 3351667.67; 456384.38,
3351668.28; 456424.33, 3351669.24; 456426.04, 3351448.96; 456375.17, 3351441.00; 456269.04, 3351427.47;
456027.69, 3351388.73; 455710.94, 3351340.12; 455524.33, 3351301.83; 455128.77, 3351217.05; 454948.99,
3351174.89; 454904.66, 3351164.38; 454896.40, 3351199.07; 454891.99, 3351206.36; 454884.50, 3351209.35;
454868.67, 3351206.86; 454862.99, 3351222.58; 454819.83, 3351210.97; 454820.30, 3351367.66; 454817.20,
3351408.57; 454826.14, 3351416.45; 454856.73, 3351425.89; 454871.49, 3351419.62
(iii) Note: Map 2, Units 1, 2, and 3 of Perdido Key beach mouse, follows:
eCFR graphic er12oc06.005.gif
View or download PDF
(9) PKBM—Unit 4: Gulf Beach Unit, Escambia County, Florida.
(i) General Description: This unit includes essential features of beach mouse habitat between Gulf Islands National
Seashore and Perdido Key State Park from approximately 4 mi (3.2 km) east of the Alabama-Florida State line to
6 mi (9.6 km) east of the State line and areas from the MHWL north to the seaward extent of human development
or maritime forest.
(ii) Coordinates: From USGS 1:24,000 quadrangle map Perdido Bay, Florida, land bounded by the following UTM
16 NAD 83 coordinates (E, N): 457418.45, 3351766.05; 456424.33, 3351669.24; 456454.09, 3351669.95;
456460.85, 3351674.93; 456491.64, 3351678.43; 456523.29, 3351684.34; 456532.43, 3351694.62; 456550.37,
3351698.07; 456566.16, 3351685.76; 456578.84, 3351687.26; 456601.78, 3351691.77; 456612.31, 3351687.85;
456622.42, 3351676.01; 456635.18, 3351673.94; 456644.26, 3351676.53; 456637.88, 3351682.12; 456636.62,
3351690.54; 456647.33, 3351685.52; 456648.56, 3351695.66; 456653.70, 3351696.98; 456671.96, 3351681.16;
456634.44, 3351637.87; 456593.26, 3351588.26; 456571.55, 3351609.94; 456551.71, 3351597.83; 456536.99,
3351593.25; 456516.87, 3351592.77; 456495.54, 3351598.60; 456490.42, 3351591.08; 456473.22, 3351601.24;
456469.17, 3351593.74; 456464.83, 3351597.87; 456459.69, 3351591.40; 456455.40, 3351593.41; 456439.82,
3351580.36; 456444.21, 3351574.12; 456438.99, 3351570.82; 456444.42, 3351565.67; 456432.95, 3351557.99;
456440.54, 3351550.78; 456451.40, 3351547.34; 456442.96, 3351538.15; 456459.10, 3351527.97; 456472.74,
3351533.58; 456496.11, 3351530.97; 456563.03, 3351479.72; 456565.81, 3351469.33; 456524.65, 3351462.80;
456454.15, 3351450.94; 456426.04, 3351448.96; 456424.33, 3351669.24; 456424.48, 3351321.01; 456430.02,
3351338.59; 456430.63, 3351362.78; 456564.50, 3351385.46; 456586.64, 3351390.22; 456587.35, 3351393.63;
456614.78, 3351398.52; 456620.28, 3351390.19; 456648.03, 3351392.74; 456700.47, 3351403.74; 456698.05,
3351416.37; 456719.20, 3351417.93; 456731.86, 3351420.35; 456735.26, 3351410.91; 456769.12, 3351412.78;
456764.43, 3351431.70; 456792.99, 3351433.44; 456800.36, 3351435.73; 456803.68, 3351429.47; 456817.40,
3351431.91; 456821.51, 3351437.29; 456819.91, 3351459.45; 456816.56, 3351466.77; 456807.81, 3351478.19;
456802.34, 3351485.45; 456822.35, 3351490.16; 456824.95, 3351470.14; 456825.56, 3351444.79; 456829.07,
3351431.13; 456847.12, 3351429.45; 456871.67, 3351432.98; 456926.58, 3351440.64; 456935.89, 3351438.97;
456993.19, 3351446.46; 457036.45, 3351453.84; 457029.58, 3351519.21; 457058.09, 3351523.07; 457062.16,
3351486.17; 457070.75, 3351481.09; 457071.02, 3351459.12; 457090.30, 3351461.47; 457117.56, 3351462.35;
457118.42, 3351470.83; 457156.38, 3351478.08; 457159.02, 3351467.35; 457184.62, 3351466.08; 457211.91,
3351471.07; 457248.66, 3351473.95; 457246.95, 3351489.05; 457264.52, 3351491.54; 457266.87, 3351480.21;
457284.42, 3351483.74; 457291.68, 3351483.91; 457294.59, 3351492.26; 457302.89, 3351492.46; 457305.08,
3351487.34; 457316.46, 3351488.64; 457313.72, 3351499.82; 457314.58, 3351508.30; 457335.68, 3351511.97;
457334.42, 3351520.40; 457340.82, 3351518.44; 457358.23, 3351520.69; 457357.79, 3351495.84; 457374.33,
3351498.31; 457365.85, 3351534.89; 457357.33, 3351536.80; 457356.06, 3351556.63; 457352.57, 3351569.23;
457366.02, 3351571.89; 457374.68, 3351520.31; 457378.89, 3351521.46; 457371.32, 3351572.02; 457390.27,
3351576.70; 457392.90, 3351555.62; 457384.51, 3351552.25; 457386.00, 3351534.32; 457427.14, 3351541.65;
457419.82, 3351581.64; 457503.24, 3351593.15; 457502.54, 3351578.33; 457493.19, 3351570.71; 457489.28,
3351556.88; 457496.90, 3351548.60; 457490.70, 3351542.11; 457494.15, 3351530.57; 457516.29, 3351535.33;
457522.54, 3351539.70; 457550.02, 3351542.48; 457561.82, 3351536.42; 457569.00, 3351546.10; 457585.95,
3351546.51; 457608.18, 3351547.04; 457616.73, 3351544.07; 457628.28, 3351548.58; 457709.53, 3351562.15;
457727.48, 3351564.70; 457727.15, 3351578.43; 457725.96, 3351583.69; 457755.51, 3351588.62; 457753.46,
3351629.80; 457764.00, 3351632.16; 457766.35, 3351578.31; 457755.81, 3351575.95; 457758.24, 3351563.32;
457770.94, 3351563.62; 457769.22, 3351591.06; 457783.04, 3351589.28; 457786.39, 3351581.96; 457793.86,
3351580.03; 457799.23, 3351576.99; 457802.28, 3351582.34; 457810.33, 3351577.46; 457814.88, 3351586.87;
457823.48, 3351581.79; 457830.71, 3351589.37; 457845.54, 3351589.72; 457848.64, 3351592.97; 457860.21,
3351596.42; 457863.51, 3351591.21; 457872.99, 3351593.55; 457870.52, 3351608.29; 457869.13, 3351622.00;
457865.32, 3351648.33; 457872.70, 3351649.57; 457874.60, 3351614.73; 457878.39, 3351589.45; 457895.26,
3351593.03; 457911.06, 3351596.58; 457907.40, 3351616.57; 457903.44, 3351649.24; 457909.69, 3351653.62;
457963.51, 3351662.31; 457967.26, 3351616.41; 457969.22, 3351601.14; 458060.19, 3351607.55; 458063.47,
3351597.71; 458097.45, 3351599.99; 458086.80, 3351646.24; 458133.51, 3351653.48; 458139.17, 3351627.41;
458146.71, 3351622.31; 458155.10, 3351625.68; 458187.98, 3351624.35; 458210.11, 3351629.11; 458212.93,
3351643.98; 458210.46, 3351658.72; 458241.12, 3351661.56; 458247.49, 3351660.66; 458260.18, 3351662.02;
458273.89, 3351664.46; 458303.41, 3351670.46; 458301.06, 3351646.92; 458325.37, 3351649.62; 458340.85,
3351655.50; 458353.41, 3351662.14; 458367.17, 3351662.47; 458376.80, 3351658.47; 458389.46, 3351660.89;
458391.78, 3351652.49; 458403.35, 3351655.94; 458406.35, 3351663.41; 458434.76, 3351671.49; 458437.74,
3351680.02; 458479.08, 3351678.89; 458516.02, 3351685.06; 458529.55, 3351694.90; 458538.02, 3351695.11;
458546.60, 3351691.08; 458576.44, 3351694.74; 458581.31, 3351701.43; 458589.58, 3351710.08; 458637.43,
3351709.74; 458676.63, 3351711.18; 458739.60, 3351712.15; 458741.86, 3351730.19; 458756.78, 3351731.19;
458774.55, 3351725.40; 458787.91, 3351730.90; 458801.31, 3351734.33; 458804.24, 3351741.64; 458811.62,
3351745.25; 458821.07, 3351748.65; 458835.16, 3351749.33; 458843.17, 3351754.73; 458850.74, 3351762.39;
458853.87, 3351772.42; 458862.55, 3351776.16; 458874.82, 3351776.89; 458884.32, 3351778.31; 458896.58,
3351780.58; 458902.29, 3351774.38; 458911.71, 3351779.36; 458911.75, 3351794.03; 458909.02, 3351808.63;
458907.68, 3351817.66; 458910.73, 3351823.02; 458921.35, 3351824.38; 458928.70, 3351824.51; 458931.50,
3351815.51; 458934.42, 3351763.34; 458954.48, 3351765.94; 458958.85, 3351760.76; 458989.40, 3351767.83;
459010.48, 3351772.56; 459015.02, 3351759.99; 459080.48, 3351773.10; 459120.76, 3351780.28; 459145.81,
3351784.26; 459188.94, 3351792.26; 459218.91, 3351797.12; 459236.51, 3351798.58; 459235.30, 3351805.79;
459244.63, 3351806.02; 459245.24, 3351823.63; 459268.75, 3351826.32; 459293.03, 3351832.50; 459313.02,
3351835.84; 459337.20, 3351839.28; 459331.34, 3351866.93; 459352.08, 3351871.97; 459360.89, 3351846.06;
459379.43, 3351851.68; 459373.67, 3351875.35; 459398.83, 3351880.17; 459402.12, 3351857.40; 459421.77,
3351859.94; 459427.96, 3351861.13; 459445.51, 3351864.65; 459441.85, 3351887.33; 459466.59, 3351894.14;
459470.25, 3351871.45; 459491.87, 3351878.18; 459494.07, 3351873.06; 459514.71, 3351877.69; 459511.99,
3351861.07; 459522.41, 3351859.25; 459537.96, 3351859.62; 459545.22, 3351859.80; 459572.33, 3351854.24;
459589.44, 3351851.93; 459605.58, 3351851.93; 459622.15, 3351853.36; 459635.52, 3351857.82; 459645.87,
3351859.10; 459651.96, 3351864.43; 459657.25, 3351880.07; 459658.58, 3351848.02; 459574.09, 3351824.26;
459385.17, 3351785.58; 459270.46, 3351767.31; 459167.89, 3351749.83; 459032.84, 3351726.42; 458956.05,
3351714.64; 458903.74, 3351702.63; 458835.68, 3351685.47; 458781.01, 3351679.79; 458679.09, 3351666.62;
458544.51, 3351645.58; 458415.74, 3351625.58; 458289.18, 3351601.41; 458088.68, 3351568.07; 457983.13,
3351551.80; 457839.55, 3351530.39; 457720.33, 3351509.56; 457584.17, 3351488.33; 457400.43, 3351462.79;
457164.03, 3351424.36; 457037.43, 3351402.30; 456936.11, 3351386.13; 456862.21, 3351374.85; 456750.30,
3351358.43; 456606.63, 3351341.24; 456424.48, 3351321.01; 456567.34, 3351537.94; 456569.21, 3351542.74;
456569.90, 3351547.12; 456572.61, 3351549.96; 456620.68, 3351604.45; 456671.15, 3351662.58; 456680.02,
3351659.95; 456681.47, 3351665.53; 456689.38, 3351666.91; 456696.94, 3351666.70; 456704.21, 3351661.72;
456709.69, 3351665.02; 456715.11, 3351671.10; 456737.47, 3351683.13; 456736.02, 3351693.79; 456726.44,
3351700.09; 456724.07, 3351711.35; 456735.32, 3351706.07; 456740.43, 3351714.96; 456739.22, 3351722.17;
456744.31, 3351726.44; 456743.15, 3351731.58; 456732.78, 3351731.33; 456737.79, 3351738.70; 456750.30,
3351735.89; 456754.15, 3351748.41; 456772.82, 3351754.06; 456784.31, 3351760.67; 456799.27, 3351770.19;
456792.35, 3351785.63; 456775.66, 3351788.32; 456801.19, 3351816.68; 456835.61, 3351855.95; 456879.65,
3351907.74; 456882.22, 3351901.55; 456899.30, 3351900.29; 456910.25, 3351891.04; 456923.48, 3351895.22;
456920.88, 3351915.24; 456926.37, 3351920.20; 456939.85, 3351920.52; 456950.24, 3351925.63; 456969.26,
3351932.09; 456991.95, 3351911.66; 457010.15, 3351903.64; 457031.15, 3351911.54; 457040.91, 3351902.26;
457047.30, 3351908.03; 457056.45, 3351903.65; 457068.67, 3351913.26; 457078.01, 3351907.32; 457136.99,
3351916.19; 457160.11, 3351924.15; 457208.74, 3351928.48; 457223.55, 3351929.13; 457254.30, 3351928.52;
457286.00, 3351930.26; 457302.42, 3351929.17; 457368.29, 3351934.61; 457422.58, 3351935.78; 457432.26,
3351929.61; 457449.05, 3351936.35; 457492.39, 3351940.56; 457522.11, 3351938.10; 457548.46, 3351944.02;
457576.65, 3351949.09; 457602.53, 3351945.84; 457609.72, 3351951.83; 457622.55, 3351946.85; 457643.68,
3351949.47; 457653.32, 3351960.86; 457675.77, 3351952.68; 457691.95, 3351957.03; 457704.42, 3351950.99;
457729.54, 3351947.23; 457742.88, 3351937.64; 457756.86, 3351934.41; 457770.55, 3351942.85; 457784.73,
3351931.90; 457793.32, 3351938.45; 457798.29, 3351946.50; 457816.18, 3351939.72; 457831.16, 3351933.73;
457836.20, 3351944.42; 457847.96, 3351946.10; 457860.03, 3351940.05; 457875.85, 3351942.81; 457883.56,
3351936.25; 457898.14, 3351938.36; 457910.91, 3351932.37; 457927.28, 3351934.02; 457937.42, 3351932.38;
457951.32, 3351931.45; 457965.86, 3351930.54; 457978.43, 3351932.73; 457985.49, 3351927.86; 457997.42,
3351930.67; 458014.36, 3351934.85; 458029.83, 3351944.00; 458239.05, 3351933.99; 458242.51, 3351790.33;
458263.59, 3351795.06; 458267.45, 3351766.61; 458254.77, 3351765.25; 458259.54, 3351743.17; 458264.91,
3351740.13; 458269.56, 3351723.33; 458128.10, 3351701.97; 458129.91, 3351714.69; 458129.71, 3351723.15;
458126.33, 3351731.52; 458121.03, 3351731.39; 458116.59, 3351739.74; 458115.41, 3351745.00; 458117.37,
3351751.39; 458117.22, 3351757.73; 458107.65, 3351762.21; 458095.18, 3351762.94; 458075.53, 3351762.24;
458064.97, 3351760.93; 458063.00, 3351754.54; 458055.64, 3351752.25; 458038.85, 3351745.51; 458037.56,
3351754.99; 458040.57, 3351772.80; 458051.11, 3351775.17; 458050.96, 3351781.51; 458040.34, 3351782.31;
458040.06, 3351793.93; 458034.43, 3351823.08; 458026.43, 3351821.31; 458000.03, 3351822.42; 458000.51,
3351828.73; 458021.51, 3351847.49; 458018.93, 3351849.95; 457997.25, 3351833.06; 457983.94, 3351835.26;
457980.63, 3351841.48; 457968.03, 3351840.55; 457967.64, 3351830.46; 457953.15, 3351829.48; 457953.00,
3351809.33; 457944.96, 3351802.84; 457929.08, 3351806.87; 457914.74, 3351806.78; 457849.67, 3351813.90;
457836.04, 3351808.29; 457838.81, 3351780.88; 457838.29, 3351758.67; 457836.60, 3351725.78; 457844.56,
3351659.38; 457813.95, 3351654.42; 457807.99, 3351681.76; 457805.60, 3351693.33; 457796.04, 3351694.16;
457798.99, 3351703.74; 457796.64, 3351713.20; 457780.78, 3351711.76; 457779.15, 3351691.64; 457782.71,
3351675.87; 457787.58, 3351649.56; 457696.16, 3351638.68; 457687.30, 3351704.09; 457655.01, 3351699.24;
457661.93, 3351631.75; 457602.81, 3351622.94; 457592.79, 3351687.17; 457513.60, 3351675.76; 457512.90,
3351660.95; 457476.02, 3351652.67; 457475.68, 3351633.03; 457481.49, 3351627.28; 457484.69, 3351605.11;
457384.89, 3351592.01; 457387.79, 3351603.58; 457382.07, 3351610.18; 457373.34, 3351609.57; 457367.91,
3351604.29; 457370.05, 3351597.60; 457375.76, 3351591.79; 457349.25, 3351587.20; 457286.76, 3351575.39;
457234.66, 3351568.45; 457231.91, 3351596.33; 457228.01, 3351629.35; 457226.08, 3351636.57; 457216.42,
3351635.73; 457203.02, 3351632.89; 457193.63, 3351614.04; 457180.74, 3351610.62; 457183.31, 3351589.99;
457198.81, 3351592.43; 457203.61, 3351565.63; 457160.31, 3351554.25; 457159.05, 3351563.53; 457119.80,
3351556.38; 457114.27, 3351570.74; 457111.72, 3351590.34; 457092.07, 3351587.80; 457082.71, 3351588.61;
457052.79, 3351581.68; 457053.19, 3351565.13; 457063.54, 3351566.42; 457067.22, 3351542.70; 456989.71,
3351530.49; 456978.83, 3351594.40; 456927.16, 3351585.92; 456933.74, 3351528.12; 456879.98, 3351520.62;
456872.46, 3351574.26; 456849.58, 3351576.82; 456828.87, 3351575.29; 456812.35, 3351571.78; 456779.25,
3351567.89; 456751.30, 3351565.15; 456715.12, 3351560.14; 456726.09, 3351492.10; 456701.28, 3351488.40;
456689.39, 3351551.24; 456669.60, 3351554.91; 456657.20, 3351552.54; 456642.81, 3351547.02; 456622.15,
3351543.42; 456631.53, 3351479.23; 456578.06, 3351472.40; 456569.40, 3351518.17; 456567.50, 3351531.21;
456567.34, 3351537.94; 456750.73, 3351718.31; 456750.35, 3351709.20; 456757.50, 3351692.72; 456761.31,
3351682.91; 456770.19, 3351685.66; 456775.57, 3351677.51; 456790.51, 3351674.88; 456802.70, 3351663.29;
456818.67, 3351660.10; 456827.69, 3351667.37; 456832.70, 3351674.73; 456829.46, 3351679.83; 456813.93,
3351678.42; 456810.60, 3351687.66; 456812.50, 3351694.95; 456815.43, 3351702.27; 456804.97, 3351706.15;
456798.50, 3351716.35; 456807.60, 3351725.88; 456814.89, 3351725.02; 456830.51, 3351722.29; 456842.09,
3351715.32; 456854.66, 3351710.45; 456849.60, 3351705.15; 456858.08, 3351689.98; 456863.42, 3351699.22;
456871.60, 3351689.51; 456887.38, 3351694.25; 456887.23, 3351700.59; 456897.06, 3351704.79; 456909.63,
3351710.64; 456917.29, 3351706.06; 456922.98, 3351700.65; 456929.11, 3351693.66; 456942.06, 3351700.32;
456958.19, 3351707.04; 456998.17, 3351713.15; 457019.55, 3351716.44; 457011.86, 3351730.78; 457009.53,
3351741.07; 457015.20, 3351755.81; 457015.23, 3351762.94; 457005.70, 3351770.99; 457003.35, 3351782.32;
456998.81, 3351793.67; 456982.29, 3351795.27; 456976.37, 3351782.71; 456957.72, 3351775.40; 456957.51,
3351783.85; 456949.04, 3351783.64; 456946.07, 3351775.12; 456940.49, 3351774.04; 456926.23, 3351772.11;
456912.86, 3351766.24; 456903.25, 3351760.26; 456891.75, 3351764.12; 456884.20, 3351768.72; 456873.96,
3351764.91; 456858.79, 3351767.72; 456846.32, 3351757.51; 456821.16, 3351763.25; 456815.80, 3351754.80;
456804.99, 3351758.11; 456792.61, 3351745.19; 456781.13, 3351748.02; 456770.10, 3351746.80; 456765.68,
3351743.51; 456764.74, 3351739.35; 456757.64, 3351732.97; 456750.73, 3351718.31; 457025.35, 3351773.53;
457022.49, 3351763.11; 457022.71, 3351753.80; 457028.48, 3351741.23; 457036.59, 3351729.87; 457053.45,
3351733.45; 457058.67, 3351736.74; 457058.39, 3351748.36; 457064.69, 3351750.63; 457065.91, 3351744.31;
457075.49, 3351742.43; 457077.43, 3351749.87; 457084.99, 3351743.71; 457090.29, 3351743.84; 457091.17,
3351751.26; 457100.77, 3351748.32; 457109.29, 3351746.41; 457110.20, 3351752.77; 457117.71, 3351748.73;
457116.71, 3351746.59; 457128.40, 3351744.75; 457132.46, 3351752.25; 457139.02, 3351743.95; 457137.03,
3351738.62; 457146.63, 3351735.68; 457157.27, 3351733.82; 457163.48, 3351740.31; 457177.11, 3351745.92;
457200.20, 3351737.81; 457216.70, 3351729.96; 457227.49, 3351721.76; 457238.28, 3351713.56; 457244.61,
3351714.77; 457247.43, 3351729.64; 457259.35, 3351744.57; 457272.94, 3351752.30; 457282.32, 3351758.86;
457286.27, 3351770.58; 457280.17, 3351777.99; 457283.82, 3351784.27; 457291.03, 3351792.89; 457292.13,
3351799.60; 457278.53, 3351802.26; 457273.99, 3351814.83; 457264.53, 3351811.43; 457256.06, 3351811.23;
457256.24, 3351803.84; 457269.37, 3351796.09; 457247.19, 3351783.54; 457239.65, 3351788.64; 457223.74,
3351789.32; 457216.43, 3351784.91; 457211.34, 3351776.34; 457204.76, 3351785.69; 457196.26, 3351786.55;
457189.13, 3351774.75; 457204.08, 3351769.82; 457217.95, 3351765.92; 457222.36, 3351758.63; 457224.66,
3351751.29; 457199.98, 3351764.44; 457192.67, 3351760.03; 457179.83, 3351765.01; 457170.25, 3351766.90;
457180.56, 3351778.77; 457177.08, 3351791.37; 457171.91, 3351785.96; 457160.11, 3351792.02; 457142.19,
3351788.42; 457123.08, 3351790.08; 457108.35, 3351785.50; 457091.39, 3351786.15; 457072.30, 3351786.75;
457067.49, 3351796.11; 457053.59, 3351795.77; 457041.84, 3351788.75; 457029.00, 3351777.74; 457025.35,
3351773.53; 457066.77, 3351698.78; 457062.96, 3351690.78; 457066.12, 3351683.93; 457073.17, 3351682.12;
457081.08, 3351686.15; 457084.84, 3351696.25; 457088.74, 3351700.30; 457093.70, 3351702.39; 457098.55,
3351708.44; 457093.12, 3351714.31; 457083.56, 3351715.14; 457072.51, 3351709.80; 457066.58, 3351706.69;
457066.77, 3351698.78; 457186.40, 3351712.32; 457184.48, 3351703.82; 457185.80, 3351693.28; 457192.25,
3351689.21; 457204.83, 3351694.79; 457215.24, 3351702.44; 457219.38, 3351706.77; 457218.16, 3351713.08;
457210.63, 3351718.18; 457202.08, 3351721.15; 457193.63, 3351719.89; 457193.76, 3351714.61; 457186.40,
3351712.32; 457724.53, 3351847.82; 457722.64, 3351838.27; 457728.19, 3351827.83; 457743.49, 3351834.39;
457761.49, 3351834.82; 457770.53, 3351844.78; 457781.14, 3351843.97; 457792.33, 3351848.39; 457813.45,
3351851.01; 457817.84, 3351844.77; 457803.19, 3351837.03; 457789.18, 3351837.21; 457784.18, 3351834.46;
457793.57, 3351830.51; 457806.60, 3351827.59; 457823.59, 3351825.89; 457834.99, 3351836.73; 457843.30,
3351843.27; 457836.90, 3351845.23; 457832.66, 3351845.13; 457836.75, 3351851.57; 457849.48, 3351850.82;
457855.58, 3351861.53; 457853.03, 3351879.44; 457850.38, 3351895.03; 457846.85, 3351898.17; 457833.05,
3351898.90; 457828.90, 3351895.63; 457821.44, 3351892.75; 457816.62, 3351894.62; 457812.23, 3351901.72;
457807.94, 3351903.73; 457800.43, 3351890.66; 457793.20, 3351893.66; 457786.09, 3351887.35; 457778.12,
3351892.30; 457770.56, 3351893.51; 457761.61, 3351892.05; 457760.70, 3351885.69; 457754.53, 3351878.14;
457743.21, 3351864.13; 457734.81, 3351860.75; 457724.53, 3351847.82; 457941.53, 3351871.07; 457936.47,
3351861.44; 457939.85, 3351853.06; 457948.32, 3351853.26; 457954.54, 3351858.70; 457965.26, 3351853.67;
457969.65, 3351847.43; 457981.29, 3351847.71; 457987.67, 3351846.81; 457987.47, 3351855.26; 457987.29,
3351862.65; 457984.94, 3351872.11; 457983.71, 3351879.48; 457979.27, 3351887.83; 457972.81, 3351891.90;
457967.60, 3351888.61; 457970.87, 3351884.46; 457967.88, 3351876.99; 457963.59, 3351879.00; 457963.36,
3351888.50; 457959.12, 3351888.40; 457957.13, 3351883.07; 457958.40, 3351874.64; 457961.73, 3351868.38;
457959.68, 3351865.16; 457950.13, 3351865.99; 457941.53, 3351871.07; 458438.95, 3351948.30; 458477.07,
3351949.21; 458477.25, 3351941.82; 458466.13, 3351919.35; 458537.67, 3351929.75; 458533.96, 3351819.73;
458490.00, 3351797.54; 458444.87, 3351779.55; 458442.47, 3351890.25; 458438.95, 3351948.30; 458928.83,
3352050.66; 458933.02, 3352052.88; 458937.36, 3352048.76; 458941.57, 3352049.91; 458947.01, 3352043.70;
458953.37, 3352043.85; 458959.85, 3352038.72; 458965.09, 3352040.96; 458965.04, 3352043.08; 458964.94,
3352047.30; 458969.07, 3352051.63; 458977.59, 3352049.72; 458983.92, 3352050.93; 458988.16, 3352051.03;
458993.45, 3352051.16; 458996.53, 3352055.46; 458999.78, 3352052.37; 459006.13, 3352052.52; 459013.52,
3352053.75; 459020.96, 3352052.87; 459021.06, 3352048.65; 459025.40, 3352044.52; 459031.70, 3352046.79;
459030.43, 3352055.21; 459034.67, 3352055.32; 459040.97, 3352057.58; 459040.82, 3352063.92; 459032.22,
3352069.00; 459023.65, 3352073.02; 459017.32, 3352071.81; 459010.94, 3352072.72; 459006.60, 3352076.84;
459003.35, 3352079.93; 458996.97, 3352080.84; 458989.54, 3352081.72; 458983.26, 3352078.39; 458975.74,
3352082.44; 458971.56, 3352080.23; 458965.31, 3352075.85; 458968.51, 3352074.87; 458970.73, 3352070.70;
458962.26, 3352070.49; 458959.06, 3352071.47; 458954.80, 3352072.43; 458947.38, 3352072.25; 458944.28,
3352069.00; 458936.80, 3352072.00; 458932.53, 3352072.95; 458931.17, 3352085.60; 458938.48, 3352090.01;
458944.88, 3352088.04; 458952.35, 3352086.11; 458959.73, 3352087.34; 458961.73, 3352092.68; 458963.74,
3352096.95; 458966.92, 3352097.03; 458973.40, 3352091.90; 458978.72, 3352090.97; 458983.99, 3352092.15;
458991.50, 3352088.10; 458994.65, 3352089.24; 459000.90, 3352093.62; 459010.46, 3352092.79; 459019.96,
3352094.07; 459021.12, 3352089.87; 459021.20, 3352086.70; 459027.45, 3352091.08; 459034.91, 3352089.15;
459040.31, 3352085.05; 459049.97, 3352079.99; 459056.30, 3352081.20; 459062.52, 3352086.64; 459068.77,
3352091.01; 459075.36, 3352081.66; 459083.83, 3352081.86; 459094.47, 3352080.00; 459107.12, 3352082.42;
459112.44, 3352081.49; 459126.16, 3352083.93; 459129.28, 3352086.12; 459130.19, 3352092.49; 459137.52,
3352095.83; 459143.77, 3352100.21; 459145.71, 3352107.66; 459157.39, 3352106.88; 459168.00, 3352106.08;
459173.22, 3352109.37; 459179.65, 3352106.36; 459192.36, 3352106.66; 459208.29, 3352104.93; 459225.15,
3352108.50; 459239.90, 3352112.03; 459241.87, 3352118.42; 459244.97, 3352121.66; 459255.28, 3352133.54;
459250.89, 3352139.77; 459247.53, 3352147.09; 459233.74, 3352147.82; 459210.40, 3352149.37; 459148.88,
3352152.13; 459134.06, 3352151.77; 459123.42, 3352153.63; 459111.74, 3352154.41; 459103.20, 3352157.37;
459095.76, 3352158.25; 459087.26, 3352159.11; 459073.42, 3352161.94; 459063.84, 3352163.83; 459062.60,
3352171.20; 459069.73, 3352183.00; 459067.49, 3352188.23; 459058.94, 3352191.19; 459057.45, 3352209.13;
459062.52, 3352218.76; 459062.29, 3352228.27; 459055.81, 3352233.40; 459053.13, 3352256.59; 459074.25,
3352259.21; 459084.82, 3352260.52; 459084.03, 3352293.27; 459082.79, 3352300.64; 459089.14, 3352300.79;
459096.58, 3352299.91; 459105.10, 3352298.00; 459110.42, 3352297.07; 459121.99, 3352300.52; 459129.43,
3352299.64; 459132.74, 3352294.43; 459144.46, 3352291.54; 459155.05, 3352291.80; 459163.49, 3352293.06;
459166.82, 3352199.06; 459167.15, 3352185.33; 459179.91, 3352183.52; 459194.73, 3352183.88; 459209.66,
3352180.01; 459223.42, 3352180.34; 459237.09, 3352184.89; 459255.01, 3352188.49; 459266.74, 3352185.60;
459280.55, 3352183.82; 459291.89, 3352196.78; 459548.55, 3352186.02; 459549.82, 3352220.93; 459630.30,
3352222.86; 459651.00, 3352185.21; 459649.57, 3352006.10; 459637.64, 3352006.35; 459626.47, 3352019.28;
459619.86, 3352029.70; 459617.49, 3352040.21; 459630.95, 3352053.22; 459630.59, 3352068.00; 459630.18,
3352084.91; 459621.51, 3352093.15; 459612.84, 3352101.40; 459611.50, 3352113.00; 459619.71, 3352123.76;
459622.38, 3352144.97; 459613.65, 3352155.33; 459622.80, 3352171.40; 459623.48, 3352187.27; 459625.56,
3352199.49; 459615.83, 3352207.91; 459558.63, 3352207.40; 459557.30, 3352174.60; 459486.30, 3352175.01;
459487.23, 3352180.32; 459374.79, 3352186.08; 459295.35, 3352185.23; 459290.23, 3352177.71; 459287.34,
3352166.02; 459295.83, 3352165.16; 459295.08, 3352152.46; 459279.22, 3352151.02; 459279.50, 3352139.40;
459259.36, 3352139.98; 459259.46, 3352135.75; 459258.13, 3352102.95; 459238.04, 3352101.41; 459224.38,
3352096.86; 459186.21, 3352098.06; 459153.30, 3352100.44; 459150.28, 3352094.03; 459149.65, 3352076.04;
459144.49, 3352070.63; 459133.82, 3352073.55; 459124.27, 3352074.38; 459115.97, 3352066.78; 459105.28,
3352070.75; 459099.03, 3352066.37; 459100.27, 3352059.00; 459103.47, 3352058.02; 459103.55, 3352054.85;
459107.89, 3352050.73; 459100.50, 3352049.49; 459103.80, 3352044.29; 459091.07, 3352045.04; 459092.77,
3352018.66; 459091.83, 3352013.35; 459071.72, 3352012.87; 459052.66, 3352012.41; 459053.64, 3352015.60;
459036.67, 3352016.25; 459027.12, 3352017.08; 459006.90, 3352020.83; 459003.77, 3352018.64; 458997.37,
3352020.60; 458989.95, 3352020.42; 458985.77, 3352018.21; 458983.73, 3352014.99; 458981.61, 3352014.94;
458979.36, 3352020.17; 458964.54, 3352019.81; 458963.33, 3352026.12; 458960.20, 3352023.93; 458959.25,
3352019.68; 458952.84, 3352021.64; 458945.25, 3352028.86; 458933.32, 3352040.20; 458928.83, 3352050.66
(10) PKBM—Unit 5: Gulf Islands National Seashore, Escambia County, Florida.
(i) General Description: This unit encompasses essential features of beach mouse habitat within the boundary of
Gulf Islands National Seashore-Perdido Key Area (also referred to as Johnson Beach) from approximately 6 mi
(9.6 km) east of the Alabama-Florida State line to the eastern tip of Perdido Key at Pensacola Bay and the area
from the MHWL north to the seaward extent of the maritime forest.
(ii) Coordinates: From USGS 1:24,000 quadrangle map Perdido Bay, and Fort Barrancas, Florida, land bounded
by the following UTM 16 NAD 83 coordinates (E, N): 464806.54, 3353248.09; 460167.32, 3352161.40; 460112.98,
3352141.46; 460076.54, 3352115.69; 460062.15, 3352097.38; 460032.76, 3352041.24; 460015.51, 3352024.29;
459999.54, 3352012.96; 459981.75, 3352007.62; 459961.62, 3352003.59; 459912.92, 3352002.90; 459885.33,
3352003.88; 459852.28, 3352012.60; 459823.72, 3352011.33; 459799.52, 3352004.41; 459708.84, 3352005.84;
459649.57, 3352006.10; 459651.00, 3352185.21; 459662.18, 3352177.93; 459676.32, 3352192.77; 459689.75,
3352206.83; 459690.56, 3352217.42; 459692.37, 3352230.15; 459701.27, 3352237.54; 459706.13, 3352230.01;
459707.87, 3352201.51; 459715.92, 3352173.67; 459726.90, 3352160.16; 459735.50, 3352155.08; 459753.65,
3352157.93; 459766.21, 3352155.82; 459768.17, 3352162.20; 459764.82, 3352169.52; 459771.02, 3352176.01;
459828.76, 3352173.60; 459847.49, 3352187.53; 459859.01, 3352171.16; 459890.74, 3352190.15; 459920.71,
3352199.20; 459961.02, 3352208.09; 459971.68, 3352244.02; 459986.72, 3352263.01; 459997.45, 3352279.12;
460011.09, 3352290.15; 460029.75, 3352290.60; 460041.81, 3352284.94; 460057.73, 3352267.49; 460066.23,
3352260.95; 460062.89, 3352234.71; 460077.34, 3352228.32; 460081.35, 3352243.48; 460099.25, 3352242.72;
460115.14, 3352209.80; 460127.02, 3352244.18; 460142.28, 3352237.41; 460142.29, 3352204.11; 460168.97,
3352186.72; 460167.32, 3352161.40; 464469.51, 3353268.58; 464465.93, 3353285.40; 464478.53, 3353289.94;
464496.58, 3353288.25; 464510.32, 3353289.64; 464517.47, 3353298.91; 464527.19, 3353293.22; 464538.68,
3353299.84; 464546.16, 3353303.93; 464551.08, 3353312.82; 464565.02, 3353310.56; 464583.88, 3353314.66;
464589.59, 3353306.59; 464608.58, 3353309.82; 464615.42, 3353324.93; 464620.04, 3353309.19; 464628.67,
3353300.39; 464636.93, 3353311.71; 464636.67, 3353322.27; 464655.48, 3353333.29; 464659.38, 3353347.13;
464669.74, 3353356.89; 464682.24, 3353365.65; 464695.60, 3353375.33; 464707.71, 3353364.14; 464724.85,
3353364.93; 464739.01, 3353370.82; 464756.44, 3353364.26; 464776.94, 3353348.89; 464801.65, 3353334.69;
464829.75, 3353355.45; 464822.89, 3353376.42; 464829.74, 3353397.97; 464852.31, 3353417.54; 464891.50,
3353430.92; 464926.62, 3353424.36; 464974.63, 3353410.72; 464999.13, 3353408.38; 465012.11, 3353413.85;
465010.83, 3353420.05; 465000.19, 3353421.91; 464993.74, 3353425.98; 464995.65, 3353434.49; 465008.36,
3353434.79; 465021.06, 3353435.10; 465024.37, 3353429.89; 465041.54, 3353420.79; 465063.75, 3353422.38;
465082.96, 3353416.50; 465106.39, 3353425.23; 465141.26, 3353442.20; 465160.15, 3353448.04; 465168.69,
3353447.09; 465177.29, 3353442.01; 465185.03, 3353428.46; 465205.15, 3353428.94; 465204.97, 3353436.33;
465190.44, 3353465.70; 465196.28, 3353470.59; 465200.62, 3353488.14; 465210.45, 3353476.09; 465228.25,
3353481.29; 465248.17, 3353476.99; 465264.92, 3353474.62; 465275.80, 3353483.04; 465282.37, 3353492.08;
465273.30, 3353505.74; 465268.06, 3353517.13; 465275.24, 3353526.82; 465280.25, 3353538.57; 465288.65,
3353541.94; 465301.66, 3353529.57; 465291.53, 3353510.30; 465320.61, 3353504.50; 465337.73, 3353507.58;
465349.22, 3353520.64; 465369.60, 3353515.98; 465371.35, 3353493.03; 465389.63, 3353492.68; 465403.76,
3353478.50; 465410.11, 3353483.66; 465424.43, 3353499.46; 465432.40, 3353517.01; 465421.97, 3353554.02;
465446.44, 3353560.55; 465460.12, 3353553.75; 465473.41, 3353546.14; 465472.56, 3353531.85; 465491.26,
3353530.71; 465488.14, 3353544.91; 465502.26, 3353552.38; 465526.05, 3353554.54; 465528.75, 3353541.35;
465539.57, 3353532.10; 465549.66, 3353530.93; 465562.07, 3353543.51; 465577.77, 3353553.20; 465591.54,
3353573.52; 465614.86, 3353573.02; 465627.17, 3353545.83; 465643.21, 3353539.88; 465664.99, 3353559.42;
465683.61, 3353577.84; 465708.18, 3353596.97; 465732.10, 3353610.22; 465732.23, 3353626.57; 465741.66,
3353631.03; 465751.75, 3353619.02; 465770.44, 3353618.28; 465776.68, 3353628.70; 465775.84, 3353641.40;
465782.27, 3353654.63; 465791.78, 3353639.40; 465791.73, 3353619.55; 465797.08, 3353617.56; 465812.32,
3353628.01; 465834.71, 3353638.55; 465850.03, 3353645.96; 465870.63, 3353642.58; 465891.18, 3353652.89;
465915.82, 3353652.29; 465926.83, 3353640.76; 465938.27, 3353649.49; 465952.32, 3353638.20; 465959.91,
3353630.99; 465971.40, 3353637.60; 465981.19, 3353627.27; 465991.98, 3353619.07; 466001.48, 3353620.36;
466013.65, 3353632.05; 466014.52, 3353645.55; 466008.11, 3353647.77; 466012.96, 3353660.57; 466023.78,
3353662.12; 466032.18, 3353654.30; 466049.93, 3353659.88; 466081.23, 3353663.75; 466073.30, 3353673.88;
466063.96, 3353670.91; 466058.29, 3353680.91; 466061.86, 3353692.27; 466079.49, 3353702.60; 466101.59,
3353708.68; 466113.75, 3353698.67; 466108.16, 3353677.88; 466115.68, 3353673.84; 466130.29, 3353682.64;
466142.19, 3353672.79; 466154.68, 3353681.81; 466168.50, 3353685.32; 466175.14, 3353690.23; 466187.37,
3353693.70; 466193.66, 3353696.62; 466206.88, 3353694.52; 466214.87, 3353690.00; 466229.18, 3353706.20;
466236.97, 3353696.47; 466248.32, 3353703.49; 466260.66, 3353685.95; 466272.51, 3353689.00; 466272.56,
3353703.28; 466262.24, 3353703.03; 466265.84, 3353718.18; 466285.27, 3353703.58; 466310.61, 3353706.96;
466322.11, 3353708.03; 466344.53, 3353717.39; 466365.55, 3353724.23; 466379.16, 3353730.90; 466388.19,
3353735.39; 466401.99, 3353739.68; 466415.82, 3353742.79; 466441.50, 3353748.95; 466459.61, 3353755.73;
466476.89, 3353747.82; 466486.47, 3353762.32; 466506.51, 3353771.52; 466523.62, 3353770.35; 466537.41,
3353775.04; 466553.99, 3353774.21; 466566.44, 3353785.08; 466570.39, 3353796.80; 466573.45, 3353812.77;
466555.69, 3353824.23; 466556.65, 3353833.77; 466584.79, 3353836.82; 466621.82, 3353817.07; 466637.08,
3353799.46; 466652.64, 3353807.54; 466666.74, 3353799.55; 466687.81, 3353798.87; 466702.66, 3353792.88;
466718.72, 3353802.39; 466731.07, 3353800.70; 466746.08, 3353804.63; 466752.40, 3353822.62; 466746.46,
3353832.74; 466752.45, 3353847.69; 466761.52, 3353866.93; 466775.13, 3353873.60; 466794.22, 3353873.00;
466814.64, 3353860.81; 466830.53, 3353861.19; 466836.34, 3353883.70; 466843.21, 3353878.71; 466860.23,
3353898.14; 466867.04, 3353928.66; 466921.24, 3353921.50; 466966.67, 3353926.82; 467017.94, 3353915.01;
467055.12, 3353905.70; 467090.79, 3353909.23; 467133.09, 3353917.78; 467175.98, 3353918.81; 467205.17,
3353921.99; 467242.29, 3353936.66; 467308.25, 3353952.91; 467315.54, 3353947.14; 467320.22, 3353950.82;
467328.57, 3353950.22; 467341.04, 3353954.85; 467352.74, 3353953.18; 467357.99, 3353955.25; 467369.04,
3353952.78; 467372.51, 3353957.23; 467379.38, 3353957.35; 467380.74, 3353961.78; 467402.21, 3353961.11;
467409.47, 3353956.53; 467419.58, 3353949.34; 467432.16, 3353954.92; 467426.07, 3353960.10; 467428.75,
3353964.13; 467437.54, 3353963.70; 467441.28, 3353972.05; 467448.27, 3353978.47; 467471.81, 3353974.67;
467488.90, 3353974.26; 467497.75, 3353958.61; 467509.87, 3353957.77; 467514.46, 3353968.53; 467515.35,
3353975.95; 467533.32, 3353977.44; 467554.45, 3353980.06; 467575.50, 3353985.85; 467605.55, 3353994.38;
467635.64, 3353998.67; 467647.94, 3353999.37; 467651.35, 3353989.54; 467656.15, 3353980.39; 467666.84,
3353976.42; 467682.94, 3353981.18; 467689.99, 3353985.31; 467694.01, 3353991.87; 467693.88, 3354005.23;
467700.36, 3354016.88; 467710.43, 3354027.43; 467725.79, 3354032.95; 467735.60, 3354037.94; 467744.23,
3354042.51; 467756.80, 3354048.76; 467770.28, 3354049.87; 467787.64, 3354054.65; 467800.89, 3354049.02;
467814.96, 3354058.87; 467830.07, 3354058.05; 467842.99, 3354065.89; 467859.98, 3354050.82; 467875.68,
3354044.87; 467893.20, 3354043.31; 467912.55, 3354048.14; 467927.72, 3354053.51; 467939.14, 3354063.29;
467950.58, 3354072.03; 467965.25, 3354078.72; 467972.74, 3354075.73; 467984.77, 3354068.50; 467990.07,
3354062.69; 467996.75, 3354046.71; 467996.95, 3354038.26; 468004.42, 3354036.32; 468020.25, 3354038.82;
468035.00, 3354042.34; 468047.73, 3354041.59; 468051.86, 3354045.92; 468049.51, 3354055.38; 468034.46,
3354064.53; 468024.60, 3354078.03; 468037.18, 3354083.62; 468051.98, 3354085.03; 468062.44, 3354090.57;
468078.14, 3354098.35; 468085.58, 3354097.47; 468099.47, 3354092.52; 468094.41, 3354082.88; 468100.91,
3354076.70; 468117.62, 3354086.61; 468118.45, 3354096.14; 468113.73, 3354116.11; 468126.34, 3354120.64;
468131.43, 3354129.22; 468137.55, 3354138.88; 468153.23, 3354147.72; 468159.35, 3354160.30; 468172.08,
3354156.63; 468173.97, 3354166.18; 468168.47, 3354174.51; 468183.85, 3354196.02; 468188.63, 3354217.27;
468194.55, 3354235.38; 468200.62, 3354247.16; 468218.65, 3354246.53; 468226.91, 3354257.85; 468238.85,
3354256.95; 468252.50, 3354248.40; 468274.48, 3354259.50; 468281.66, 3354277.40; 468268.60, 3354283.67;
468277.90, 3354293.41; 468287.30, 3354298.92; 468294.45, 3354266.32; 468288.45, 3354251.38; 468262.21,
3354241.24; 468263.40, 3354227.81; 468263.99, 3354211.69; 468248.19, 3354166.40; 468240.30, 3354163.51;
468244.56, 3354152.44; 468239.20, 3354141.33; 468226.19, 3354153.70; 468213.61, 3354148.11; 468207.46,
3354139.51; 468202.39, 3354129.87; 468198.46, 3354120.02; 468204.61, 3354112.24; 468213.51, 3354105.32;
468222.88, 3354112.28; 468225.47, 3354103.62; 468236.36, 3354097.15; 468239.74, 3354105.15; 468248.38,
3354111.95; 468256.13, 3354117.44; 468259.25, 3354100.59; 468269.02, 3354094.61; 468278.44, 3354095.76;
468301.92, 3354063.84; 468321.70, 3354067.49; 468347.45, 3354070.48; 468361.44, 3354066.86; 468374.81,
3354053.68; 468386.26, 3354059.13; 468404.33, 3354051.24; 468421.34, 3354054.42; 468437.05, 3354045.68;
468449.06, 3354058.26; 468471.13, 3354065.53; 468498.47, 3354068.29; 468495.38, 3354081.57; 468512.31,
3354071.28; 468524.93, 3354058.90; 468537.49, 3354065.14; 468542.53, 3354086.67; 468531.56, 3354099.73;
468524.54, 3354127.05; 468531.54, 3354144.13; 468549.35, 3354149.86; 468572.46, 3354146.84; 468588.95,
3354135.99; 468600.60, 3354136.27; 468613.51, 3354128.13; 468612.91, 3354109.09; 468613.24, 3354095.35;
468630.16, 3354096.82; 468645.89, 3354103.54; 468662.85, 3354102.89; 468674.58, 3354100.00; 468668.98,
3354112.55; 468664.41, 3354126.18; 468669.00, 3354147.18; 468677.00, 3354161.25; 468696.91, 3354143.10;
468724.84, 3354124.46; 468752.54, 3354126.20; 468769.17, 3354128.58; 468760.28, 3354148.57; 468763.49,
3354166.50; 468788.18, 3354177.78; 468806.69, 3354157.08; 468804.05, 3354134.82; 468806.94, 3354120.40;
468858.31, 3354139.05; 468886.53, 3354138.54; 468908.54, 3354151.08; 468950.68, 3354204.94; 469007.06,
3354239.06; 469083.64, 3354270.50; 469094.91, 3354294.57; 469127.14, 3354309.22; 469182.44, 3354339.09;
469230.84, 3354358.09; 469236.13, 3354336.42; 469230.78, 3354319.49; 469221.75, 3354307.13; 469218.74,
3354291.72; 469220.19, 3354273.01; 469263.53, 3354271.28; 469288.14, 3354288.91; 469322.59, 3354294.10;
469323.99, 3354301.27; 469295.51, 3354312.47; 469293.37, 3354335.41; 469274.36, 3354357.53; 469262.31,
3354374.16; 469252.55, 3354383.43; 469267.32, 3354385.90; 469269.61, 3354397.87; 469276.22, 3354420.22;
469277.46, 3354434.92; 469288.73, 3354464.64; 469289.30, 3354484.73; 469300.64, 3354494.93; 469319.24,
3354514.41; 469342.46, 3354507.04; 469367.89, 3354539.29; 469372.40, 3354553.32; 469363.99, 3354569.79;
469379.12, 3354582.02; 469388.80, 3354594.96; 469392.50, 3354606.54; 469404.13, 3354602.06; 469412.16,
3354617.70; 469406.56, 3354630.25; 469408.38, 3354639.82; 469425.75, 3354625.43; 469436.13, 3354634.13;
469449.79, 3354638.69; 469455.79, 3354653.63; 469473.81, 3354653.01; 469475.58, 3354637.47; 469489.98,
3354633.46; 469499.33, 3354608.32; 469518.74, 3354594.12; 469524.10, 3354602.57; 469540.31, 3354638.63;
469552.16, 3354641.30; 469569.41, 3354634.58; 469576.15, 3354651.78; 469574.95, 3354668.40; 469582.96,
3354682.07; 469577.81, 3354698.20; 469574.56, 3354717.55; 469578.40, 3354722.79; 469570.96, 3354731.94;
469576.44, 3354746.38; 469593.23, 3354753.12; 469585.37, 3354727.78; 469586.72, 3354723.78; 469602.61,
3354707.52; 469616.52, 3354707.46; 469631.22, 3354756.56; 469659.32, 3354761.20; 469681.48, 3354748.26;
469727.71, 3354742.24; 469732.26, 3354751.46; 469735.29, 3354757.48; 469738.78, 3354777.38; 469719.71,
3354767.20; 469702.04, 3354766.31; 469694.77, 3354773.55; 469708.24, 3354808.36; 469726.98, 3354821.89;
469734.90, 3354839.52; 469754.09, 3354850.69; 469775.73, 3354876.18; 469799.89, 3354881.76; 469803.86,
3354895.88; 469812.25, 3354926.60; 469803.70, 3354951.77; 469790.50, 3354971.66; 469762.33, 3354970.19;
469741.15, 3354975.23; 469733.88, 3354996.46; 469725.95, 3355012.52; 469710.58, 3355023.65; 469705.12,
3355035.81; 469686.34, 3355040.11; 469669.18, 3355027.01; 469658.96, 3355022.41; 469637.52, 3355024.78;
469638.67, 3355007.25; 469650.65, 3354988.12; 469664.12, 3354990.03; 469691.40, 3354962.54; 469670.80,
3354960.07; 469660.41, 3354945.94; 469656.15, 3354925.23; 469637.58, 3354920.82; 469632.08, 3354901.66;
469639.97, 3354887.58; 469619.02, 3354866.86; 469605.25, 3354877.63; 469586.08, 3354865.28; 469586.47,
3354849.43; 469573.47, 3354844.76; 469562.36, 3354827.84; 469551.80, 3354820.85; 469540.97, 3354808.70;
469529.48, 3354804.44; 469512.83, 3354801.34; 469494.50, 3354807.98; 469475.07, 3354820.04; 469461.16,
3354826.05; 469448.63, 3354818.35; 469450.07, 3354802.53; 469463.13, 3354790.97; 469447.30, 3354785.55;
469424.68, 3354800.86; 469417.03, 3354824.35; 469408.76, 3354843.72; 469396.91, 3354851.21; 469386.06,
3354856.50; 469370.44, 3354845.03; 469359.71, 3354845.17; 469355.50, 3354838.72; 469336.96, 3354833.12;
469311.96, 3354832.13; 469305.78, 3354841.09; 469291.25, 3354834.01; 469274.13, 3354818.93; 469259.29,
3354808.27; 469234.18, 3354811.63; 469211.29, 3354821.78; 469186.50, 3354828.32; 469156.59, 3354833.15;
469138.40, 3354845.79; 469124.34, 3354852.19; 469099.52, 3354843.67; 469085.32, 3354839.36; 469076.92,
3354825.29; 469067.68, 3354799.68; 469056.51, 3354779.33; 469049.56, 3354760.13; 469047.78, 3354746.35;
469046.14, 3354726.23; 469034.13, 3354697.40; 469029.55, 3354667.69; 469018.33, 3354649.45; 469000.84,
3354627.89; 468989.70, 3354620.64; 468971.40, 3354618.73; 468952.71, 3354605.88; 468937.30, 3354602.33;
468922.08, 3354607.12; 468906.29, 3354603.17; 468898.58, 3354609.73; 468891.12, 3354605.98; 468877.19,
3354615.41; 468873.84, 3354622.72; 468863.14, 3354626.70; 468848.35, 3354625.28; 468840.85, 3354631.33;
468836.68, 3354639.55; 468830.30, 3354640.19; 468821.96, 3354640.39; 468812.80, 3354641.36; 468806.96,
3354652.71; 468794.41, 3354662.32; 468793.07, 3354668.63; 468787.37, 3354674.04; 468777.68, 3354680.55;
468765.74, 3354681.45; 468758.67, 3354678.11; 468757.53, 3354676.10; 468749.31, 3354670.75; 468747.53,
3354662.38; 468748.51, 3354654.48; 468751.45, 3354648.21; 468754.04, 3354639.55; 468753.03, 3354631.99;
468750.03, 3354624.79; 468742.07, 3354624.99; 468734.46, 3354627.58; 468731.10, 3354635.43; 468725.86,
3354638.47; 468715.01, 3354643.37; 468707.32, 3354649.13; 468702.77, 3354656.95; 468693.23, 3354657.11;
468687.94, 3354662.14; 468681.46, 3354667.14; 468673.28, 3354676.85; 468668.41, 3354681.09; 468658.77,
3354685.62; 468649.48, 3354691.73; 468642.16, 3354698.69; 468632.26, 3354713.91; 468622.51, 3354722.80;
468617.59, 3354729.02; 468616.66, 3354734.55; 468608.91, 3354743.08; 468602.64, 3354756.01; 468600.49,
3354764.78; 468595.52, 3354770.90; 468585.96, 3354785.98; 468580.33, 3354799.59; 468576.92, 3354809.02;
468588.09, 3354815.51; 468597.69, 3354829.22; 468611.00, 3354837.47; 468621.10, 3354846.83; 468637.14,
3354860.15; 468649.56, 3354872.07; 468659.67, 3354879.82; 468678.80, 3354889.69; 468701.42, 3354904.61;
468715.25, 3354915.93; 468741.88, 3354929.01; 468758.78, 3354933.89; 468783.27, 3354942.29; 468802.70,
3354945.31; 468828.46, 3354946.55; 468847.12, 3354947.39; 468867.41, 3354945.90; 468886.73, 3354952.31;
468913.66, 3354955.73; 468953.96, 3354965.03; 468994.70, 3354972.35; 469018.38, 3354978.86; 469042.85,
3354985.79; 469073.96, 3354997.24; 469111.42, 3355008.85; 469132.66, 3355017.68; 469143.73, 3355019.93;
469153.98, 3355023.35; 469181.61, 3355014.50; 469210.14, 3355017.56; 469244.21, 3355021.55; 469263.69,
3355020.83; 469280.00, 3355020.03; 469303.90, 3355017.44; 469322.77, 3355009.17; 469340.76, 3355004.85;
469356.72, 3355002.06; 469399.53, 3354989.61; 469416.96, 3354988.83; 469456.69, 3354975.13; 469477.70,
3354974.43; 469497.54, 3354986.54; 469502.42, 3355003.57; 469497.60, 3355027.76; 469496.96, 3355054.17;
469515.23, 3355087.38; 469575.70, 3355127.94; 469624.95, 3355150.27; 469686.69, 3355190.35; 469709.06,
3355220.99; 469717.07, 3355240.21; 469733.10, 3355275.50; 469745.05, 3355309.59; 469745.37, 3355340.25;
469747.26, 3355349.81; 469758.98, 3355346.92; 469768.90, 3355331.31; 469771.55, 3355309.17; 469777.79,
3355270.21; 469796.74, 3355231.56; 469816.48, 3355203.49; 469825.30, 3355175.84; 469828.22, 3355137.07;
469829.31, 3355108.56; 469835.40, 3355086.51; 469840.15, 3355057.14; 469846.26, 3355023.46; 469862.73,
3354999.55; 469888.76, 3354974.80; 469906.83, 3354972.07; 469937.15, 3354969.64; 469964.79, 3354927.50;
469967.32, 3354904.97; 469963.31, 3354873.55; 469957.47, 3354852.41; 469919.14, 3354712.36; 469904.41,
3354590.43; 469887.91, 3354527.67; 469882.16, 3354458.82; 469879.36, 3354399.56; 469875.67, 3354332.88;
469852.24, 3354294.27; 469829.53, 3354269.41; 469798.15, 3354252.80; 469758.27, 3354237.04; 469620.05,
3354213.64; 469413.30, 3354175.90; 469150.72, 3354125.19; 468897.75, 3354071.54; 468705.93, 3354029.93;
468472.95, 3353982.05; 468354.85, 3353959.13; 468089.73, 3353898.86; 467876.76, 3353855.69; 467795.37,
3353833.66; 467704.10, 3353810.31; 467589.00, 3353794.86; 467465.82, 3353762.31; 467307.82, 3353723.79;
467132.79, 3353689.83; 466939.05, 3353639.72; 466650.36, 3353573.59; 466448.08, 3353526.45; 466253.99,
3353491.14; 466104.53, 3353450.55; 465894.68, 3353409.20; 465744.99, 3353378.49; 465607.97, 3353348.78;
465461.41, 3353319.89; 465387.62, 3353304.37; 465298.13, 3353281.09; 465146.47, 3353243.62; 464951.75,
3353190.32; 464766.29, 3353148.87; 464622.88, 3353112.37; 464474.67, 3353072.11; 464304.10, 3353027.85;
464172.41, 3352997.20; 463970.02, 3352954.29; 463779.90, 3352910.99; 463553.34, 3352865.91; 463397.79,
3352827.46; 463298.84, 3352800.77; 463136.67, 3352759.88; 462972.38, 3352718.94; 462823.02, 3352674.14;
462717.79, 3352644.13; 462580.14, 3352610.68; 462480.38, 3352579.35; 462257.48, 3352514.15; 462033.58,
3352440.60; 461803.27, 3352369.67; 461642.05, 3352322.13; 461476.44, 3352278.22; 461256.30, 3352224.32;
460978.37, 3352151.06; 460797.21, 3352106.55; 460554.30, 3352055.44; 460349.93, 3352012.49; 460270.17,
3351994.55; 460194.24, 3351980.05; 460146.84, 3351968.34; 460060.54, 3351952.83; 459965.56, 3351929.11;
459844.14, 3351898.10; 459658.58, 3351848.02; 459657.25, 3351880.07; 459656.77, 3351891.62; 459649.88,
3351907.84; 459646.27, 3351928.46; 459645.76, 3351992.61; 459728.73, 3351993.57; 459793.00, 3351992.40;
459817.11, 3351985.34; 459838.96, 3351982.76; 459858.63, 3351984.26; 459885.56, 3351992.63; 459928.03,
3351991.63; 459975.63, 3351993.75; 459990.40, 3351997.36; 460025.26, 3352015.41; 460048.20, 3352036.57;
460059.52, 3352061.02; 460075.51, 3352089.94; 460099.95, 3352114.71; 460122.78, 3352131.60; 460144.84,
3352139.53; 460162.73, 3352144.18; 460170.30, 3352138.02; 460169.55, 3352125.32; 460148.36, 3352124.34;
460145.56, 3352108.42; 460131.90, 3352103.86; 460136.52, 3352088.12; 460151.32, 3352089.53; 460155.56,
3352082.35; 460079.80, 3352067.73; 460091.79, 3352009.89; 460131.28, 3352017.95; 460155.04, 3352023.03;
460158.61, 3352007.73; 460163.10, 3351997.27; 460181.15, 3351995.59; 460197.14, 3352005.26; 460198.41,
3352026.66; 460251.63, 3352035.90; 460296.49, 3352044.39; 460288.14, 3352083.30; 460305.65, 3352085.95;
460311.02, 3352094.00; 460297.05, 3352153.28; 460182.10, 3352131.96; 460182.80, 3352146.78; 460221.78,
3352156.17; 460298.91, 3352167.83; 460344.83, 3352174.88; 460383.64, 3352179.78; 460428.92, 3352180.46;
460479.10, 3352175.33; 460548.64, 3352158.36; 460630.44, 3352144.07; 460697.24, 3352141.71; 460781.60,
3352152.85; 460965.17, 3352201.65; 461189.40, 3352261.33; 461407.76, 3352317.30; 461553.98, 3352356.77;
461664.40, 3352391.13; 461861.00, 3352453.98; 462029.11, 3352510.65; 462254.21, 3352583.83; 462475.35,
3352656.12; 462677.24, 3352719.63; 462783.53, 3352756.69; 462837.25, 3352773.02; 462926.04, 3352798.14;
463123.85, 3352849.66; 463248.68, 3352883.47; 463325.01, 3352901.81; 463336.94, 3352890.47; 463354.48,
3352893.00; 463364.47, 3352904.98; 463363.75, 3352920.71; 463356.68, 3352931.35; 463341.11, 3352934.55;
463328.97, 3352927.12; 463321.53, 3352914.41; 463244.68, 3352894.16; 463042.95, 3352843.36; 462928.44,
3352814.05; 462787.39, 3352772.63; 462592.90, 3352707.70; 462371.16, 3352634.75; 462206.12, 3352581.11;
461994.86, 3352510.51; 461849.15, 3352462.15; 461673.57, 3352406.15; 461567.39, 3352371.89; 461476.12,
3352349.07; 461234.72, 3352283.58; 461016.73, 3352228.67; 460873.60, 3352189.30; 460789.34, 3352168.25;
460738.18, 3352157.36; 460687.97, 3352154.19; 460638.87, 3352156.96; 460555.48, 3352171.61; 460497.07,
3352188.04; 460429.47, 3352197.67; 460363.46, 3352193.16; 460287.88, 3352180.25; 460179.52, 3352162.14;
460176.23, 3352185.99; 460256.99, 3352192.59; 460290.69, 3352197.99; 460295.71, 3352209.74; 460302.09,
3352208.83; 460313.58, 3352215.45; 460322.36, 3352202.98; 460343.44, 3352199.42; 460368.30, 3352206.36;
460399.68, 3352223.36; 460420.70, 3352241.31; 460464.71, 3352245.14; 460499.09, 3352252.70; 460530.31,
3352233.92; 460568.66, 3352225.32; 460599.66, 3352234.11; 460631.81, 3352235.27; 460698.45, 3352223.40;
460832.72, 3352240.49; 460886.11, 3352267.14; 460935.43, 3352298.05; 460953.45, 3352292.14; 460971.62,
3352296.54; 460991.32, 3352303.35; 460998.97, 3352315.82; 461013.75, 3352352.27; 461027.32, 3352361.05;
461059.45, 3352390.36; 461104.38, 3352425.77; 461124.79, 3352419.92; 461160.99, 3352385.11; 461228.42,
3352356.60; 461266.85, 3352344.45; 461344.18, 3352350.66; 461395.97, 3352377.67; 461429.40, 3352408.20;
461463.94, 3352442.32; 461495.04, 3352487.07; 461538.56, 3352560.65; 461564.62, 3352567.61; 461587.53,
3352556.67; 461598.67, 3352522.85; 461602.69, 3352488.06; 461618.62, 3352488.80; 461666.99, 3352501.39;
461677.48, 3352507.71; 461693.44, 3352504.92; 461700.76, 3352509.80; 461698.46, 3352517.14; 461681.16,
3352529.19; 461659.67, 3352543.22; 461646.82, 3352549.73; 461639.28, 3352554.83; 461628.23, 3352556.97;
461607.31, 3352562.52; 461601.84, 3352569.79; 461593.14, 3352579.09; 461577.18, 3352581.88; 461567.75,
3352577.43; 461566.49, 3352585.85; 461567.34, 3352594.33; 461573.42, 3352606.10; 461583.90, 3352610.58;
461594.64, 3352604.50; 461610.81, 3352593.26; 461632.44, 3352574.75; 461647.50, 3352565.60; 461665.74,
3352555.00; 461750.00, 3352531.65; 461815.91, 3352522.66; 461852.67, 3352519.78; 461875.97, 3352520.34;
461903.37, 3352526.28; 461933.92, 3352533.35; 461950.64, 3352543.27; 461969.21, 3352563.80; 461990.63,
3352574.34; 462032.13, 3352616.16; 462038.52, 3352633.11; 462051.05, 3352640.81; 462080.11, 3352652.98;
462130.66, 3352665.69; 462173.37, 3352673.85; 462253.74, 3352671.04; 462268.49, 3352674.56; 462304.81,
3352676.61; 462331.23, 3352687.89; 462351.40, 3352707.21; 462371.66, 3352705.16; 462429.54, 3352743.42;
462496.70, 3352759.30; 462548.97, 3352782.75; 462583.14, 3352799.42; 462614.41, 3352804.14; 462649.32,
3352822.81; 462684.81, 3352852.62; 462694.32, 3352862.31; 462705.52, 3352872.14; 462748.01, 3352867.87;
462794.95, 3352854.20; 462845.98, 3352846.97; 462869.17, 3352851.76; 462890.20, 3352858.60; 462901.72,
3352864.16; 462925.87, 3352869.45; 462947.98, 3352879.02; 462973.42, 3352878.57; 463031.07, 3352891.03;
463095.07, 3352922.69; 463217.57, 3352966.46; 463242.04, 3352986.49; 463261.52, 3353013.38; 463286.70,
3353023.50; 463311.13, 3353020.91; 463330.19, 3353021.37; 463358.81, 3353021.00; 463386.51, 3353014.27;
463404.46, 3353016.81; 463430.71, 3353026.95; 463457.66, 3353027.32; 463483.85, 3353019.77; 463510.32,
3353018.67; 463547.36, 3353022.36; 463594.78, 3353033.01; 463638.89, 3353048.86; 463673.30, 3353064.21;
463710.70, 3353078.58; 463743.11, 3353085.70; 463792.29, 3353102.23; 463820.79, 3353109.76; 463853.28,
3353113.71; 463911.48, 3353124.11; 463951.50, 3353126.38; 463988.78, 3353144.01; 464040.73, 3353168.44;
464097.09, 3353203.62; 464114.81, 3353215.67; 464144.60, 3353241.21; 464170.01, 3353241.82; 464189.81,
3353224.87; 464210.38, 3353215.44; 464222.11, 3353190.35; 464232.25, 3353178.32; 464239.58, 3353190.77;
464248.10, 3353184.96; 464247.80, 3353192.44; 464260.56, 3353190.63; 464272.28, 3353193.83; 464278.18,
3353206.91; 464289.53, 3353211.79; 464299.84, 3353212.83; 464308.88, 3353207.64; 464333.68, 3353226.32;
464347.53, 3353230.77; 464339.66, 3353249.61; 464323.77, 3353249.22; 464324.60, 3353258.76; 464334.08,
3353261.10; 464348.96, 3353259.34; 464353.52, 3353242.87; 464357.06, 3353231.00; 464366.51, 3353234.40;
464370.36, 3353250.34; 464375.68, 3353249.41; 464377.07, 3353235.71; 464390.68, 3353234.83; 464401.20,
3353245.80; 464418.06, 3353249.37; 464418.37, 3353236.70; 464427.80, 3353241.15; 464433.62, 3353250.13;
464449.50, 3353250.51; 464463.82, 3353240.96; 464476.00, 3353239.25; 464484.85, 3353247.81; 464473.12,
3353250.70; 464462.46, 3353253.61; 464469.51, 3353268.58; 469439.91, 3354872.05; 469431.24, 3354880.30;
469419.59, 3354880.02; 469413.17, 3354869.04; 469407.35, 3354860.70; 469412.90, 3354850.26; 469425.73,
3354845.28; 469436.72, 3354850.83; 469445.09, 3354863.47; 469439.91, 3354872.05; 469523.43, 3354844.93;
469510.70, 3354845.68; 469498.89, 3354842.81; 469495.01, 3354827.92; 469508.89, 3354810.76; 469526.05,
3354814.93; 469534.24, 3354826.75; 469531.87, 3354837.27; 469523.43, 3354844.93; 466190.53, 3354051.39;
465789.50, 3353888.05; 465774.93, 3353906.49; 465797.81, 3353933.65; 465835.46, 3353937.23; 465867.28,
3353944.38; 465901.69, 3353950.31; 465937.29, 3353960.10; 465969.02, 3353971.08; 466018.28, 3353997.80;
466056.00, 3354025.52; 466094.75, 3354063.47; 466127.55, 3354083.41; 466164.05, 3354108.55; 466186.52,
3354132.07; 466348.00, 3354151.94; 466376.57, 3354104.72; 466418.82, 3354050.83; 466470.73, 3354007.74;
466545.90, 3353928.76; 466605.94, 3353880.41; 466606.12, 3353859.14; 466597.09, 3353843.27; 466568.86,
3353842.59; 466560.42, 3353867.44; 466541.00, 3353892.02; 466504.78, 3353897.41; 466485.35, 3353921.99;
466479.78, 3353957.86; 466444.79, 3353977.37; 466412.75, 3353984.29; 466373.20, 3353979.51; 466323.72,
3353961.73; 466278.86, 3353964.48; 466259.34, 3353978.06; 466199.44, 3353967.68; 466178.83, 3353973.57;
466147.44, 3353948.56; 466125.00, 3353923.76; 466116.54, 3353903.13; 466078.02, 3353908.59; 466024.61,
3353894.54; 465973.36, 3353897.13; 465967.66, 3353909.76; 465939.48, 3353915.14; 465907.95, 3353903.22;
465904.48, 3353887.82; 465878.81, 3353891.03; 465841.94, 3353881.21; 465816.50, 3353874.61; 465789.50,
3353888.05; 465163.51, 3353601.02; 465084.34, 3353682.31; 465112.50, 3353722.06; 465126.95, 3353747.45;
465147.68, 3353804.05; 465160.91, 3353838.44; 465181.85, 3353886.03; 465199.16, 3353900.09; 465228.18,
3353922.21; 465307.99, 3353944.16; 465348.23, 3353941.12; 465378.48, 3353935.84; 465419.06, 3353918.78;
465387.24, 3353905.99; 465346.47, 3353888.98; 465311.40, 3353886.13; 465305.83, 3353866.96; 465294.78,
3353825.62; 465269.69, 3353741.86; 465283.78, 3353699.12; 465281.10, 3353685.03; 465269.01, 3353686.74;
465247.37, 3353668.19; 465241.83, 3353648.02; 465229.74, 3353649.73; 465210.17, 3353628.22; 465217.51,
3353615.37; 465188.51, 3353568.59; 465146.26, 3353571.58; 465158.47, 3353606.94; 465165.65, 3353642.18;
465177.04, 3353669.50; 465168.94, 3353672.31; 465145.38, 3353649.71; 465118.92, 3353664.10; 465085.74,
3353624.23; 465102.02, 3353615.60; 465111.37, 3353602.80; 465106.57, 3353593.67; 465081.96, 3353573.04;
465056.13, 3353561.40; 464968.37, 3353536.25; 464942.78, 3353514.60; 464907.95, 3353542.82; 464910.63,
3353556.91; 464923.31, 3353572.24; 464940.99, 3353588.69; 464978.60, 3353611.64; 465020.27, 3353632.68;
465063.72, 3353662.78; 465084.34, 3353682.31
(iii) Note: Map 3, Units 4 and 5 of Perdido Key beach mouse, follows:
eCFR graphic er12oc06.006.gif
View or download PDF
Preble's Meadow Jumping Mouse (Zapus
hudsonius preblei)
(1) Critical habitat units are depicted for Boulder, Broomfield, Douglas, El Paso, Jefferson, Larimer, and Teller
Counties in Colorado on the maps below. The maps provided are for informational purposes only.
(2) The primary constituent elements of critical habitat for the Preble's meadow jumping mouse are:
(i) Riparian corridors:
(A) Formed and maintained by normal, dynamic, geomorphological, and hydrological processes that create and
maintain river and stream channels, floodplains, and floodplain benches and that promote patterns of vegetation
favorable to the Preble's meadow jumping mouse;
(B) Containing dense, riparian vegetation consisting of grasses, forbs, or shrubs, or any combination thereof, in
areas along rivers and streams that normally provide open water through the Preble's meadow jumping mouse's
active season; and
(C) Including specific movement corridors that provide connectivity between and within populations. This may
include river and stream reaches with minimal vegetative cover or that are armored for erosion control; travel ways
beneath bridges, through culverts, along canals and ditches; and other areas that have experienced substantial
human alteration or disturbance.
(ii) Additional adjacent floodplain and upland habitat with limited human disturbance (including hayed fields, grazed
pasture, other agricultural lands that are not plowed or disked regularly, areas that have been restored after past
aggregate extraction, areas supporting recreational trails, and urban-wildland interfaces).
(3) Critical habitat does not include buildings, roads, parking lots, other paved areas, lawns, other urban and
suburban landscaped areas, regularly plowed or disked agricultural areas, and the land on which they are located
existing within the legal boundaries on the effective date of this rule.
(4) Critical habitat map units. Data layers defining map units were created on a base of USGS digital ortho-photo
quarter-quadrangles, and critical habitat units were then mapped using Universal Transverse Mercator (UTM)
Zone 15N coordinates.
(5) Note: Index map of critical habitat for the Preble's meadow jumping mouse follows:
eCFR graphic er15de10.002.gif
View or download PDF
(6) Unit 1: North Fork Cache la Poudre River, Larimer County, Colorado.
(i) This unit consists of 87.2 mi (140.4 km) of streams and rivers. North Fork Cache la Poudre River from Seaman
Reservoir (40 43 7N 105 14 32W, T.9N., R.70W., Sec. 28) upstream to Halligan Reservoir spillway (40 52 44N 105
20 15W, T.11N., R.71W., Sec. 34) excluding 1.06 mi (1.71 km) of the North Fork Cache la Poudre River within the
Eagles Nest Open Space (from 40 45 44N 105 13 50W, T. 9N, R.70W., Sec. 9 to 40 46 17N 105 13 59W, T. 9N,
R.70W., Sec. 4). Includes Lone Pine Creek from its confluence North Fork Cache la Poudre River (40 47 54N 105
15 30W, T.10N., R.70W., Sec. 32) upstream and continuing upstream into North Lone Pine Creek to 7,600 ft
(2,317 m) elevation (40 49 58N 105 34 09W, T.10N., R.73W., Sec. 15). Includes Columbine Canyon from its
confluence with North Lone Pine Creek (40 49 47N 105 33 31W, T.10N., R.73W., Sec. 15) upstream to 7,600 ft
(2,317 m) elevation (40 49 32N 105 33 58W, T.10N., R.73W., Sec. 15). Also includes Stonewall Creek from its
confluence with North Fork Cache la Poudre River (40 48 19N 105 15 21W, T.10N., R.70W., Sec. 29) upstream to
(40 53 26N 105 15 40W, T.11N., R.70W., Sec. 29). Includes Tenmile Creek from its confluence with Stonewall
Creek (40 51 49N 105 15 32W, T.10N., R.70W., Sec. 5) upstream to Red Mountain Road (40 53 00N 105 16 09W,
T.11N., R.70W., Sec. 31). Also includes Rabbit Creek from its confluence with North Fork Cache la Poudre River
(40 48 30N 105 16 07W, T.10N., R.70W., Sec. 30) upstream to the confluence with North and Middle Forks of
Rabbit Creek (40 49 34N 105 20 49W, T.10N., R 71W., Sec. 21). Also includes South Fork Rabbit Creek from its
confluence with Rabbit Creek (40 48 39N 105 19 45W, T.10N., R.71W., Sec. 27) upstream to (40 49 39N 105 24
40W, T.10N., R.72W., north boundary Sec. 24). Includes an unnamed tributary from its confluence with South Fork
Rabbit Creek (40 47 28N 105 20 47W, T.10N., R.71W., Sec. 33) upstream to (40 47 28N 105 23 12W, T.10N.,
R.71W., Sec. 31). Which in turn has an unnamed tributary from their confluence at (40 47 17N 105 21 48W,
T.10N., R.71W., east boundary Sec. 32) upstream to (40 46 55N 105 22 16W, T.9N., R.71W., Sec. 5). Also
includes Middle Fork Rabbit Creek from its confluence with Rabbit Creek (40 49 34N 105 20 49W, T.10N., R 71W.,
Sec. 21) upstream to 7,600 ft (2,317 m) elevation (40 49 46N 105 26 59W, T.10N., R.72W., Sec. 15). This includes
an unnamed tributary from its confluence with Middle Fork Rabbit Creek (40 49 56N 105 25 51W, T.10N., R.72W.,
Sec. 14) upstream to 7,600 ft (2,317 m) elevation (40 48 48N 105 26 29W, T.10N., R.72W., Sec. 23). This unit
includes North Fork Rabbit Creek from its confluence with Rabbit Creek (40 49 34N 105 20 49W, T.10N., R.71W.,
Sec. 21) upstream to 7,600 ft (2,317 m) elevation (40 49 38N 105 29 19W, T.10N., R.72W., Sec. 17). Includes an
unnamed tributary from its confluence with North Fork Rabbit Creek (40 50 45N 105 27 44W, T.10N., R.72W., Sec.
9) upstream to 7,600 ft (2,317 m) elevation (40 50 57N 105 28 46W, T.10N., R.72W., Sec. 9).
(ii) Note: Map of Unit 1 follows:
eCFR graphic er15de10.003.gif
View or download PDF
(7) Unit 2: Cache la Poudre River, Larimer County, Colorado.
(i) This unit consists of 50.8 mi (81.7 km) of streams and rivers. Cache la Poudre River from Poudre Park (40 41
16N 10 18 2W, T.8N., R.71W., Sec. 2) upstream to (40 42 02N 105 34 04W, T.9N., R.73W., west boundary Sec.
34). Includes Hewlett Gulch from its confluence with Cache la Poudre River (40 41 16N 105 18 24W, T.8N.,
R.71W., Sec. 2) upstream to the boundary of Arapahoe-Roosevelt National Forest (40 43 29N 105 18 51W, T.9N.,
R.71W., Sec. 23). Also includes Young Gulch from its confluence with Cache la Poudre River (40 41 25N 105 20
57W, T.8N., R.71W., Sec. 4) upstream to (40 39 14N 105 20 13W, T.8N., R.71W., south boundary Sec. 15). Also
includes an unnamed tributary from its confluence with Cache la Poudre River at Stove Prairie Landing (40 40 58N
105 23 23W, T.8N., R.71W., Sec. 6) upstream to (40 39 31N 105 22 34W, T.8N., R.71W., Sec. 17). Includes Skin
Gulch from its confluence with the aforementioned unnamed tributary at (40 40 33N 105 23 16W, T.8N., R.71W.,
Sec. 7) upstream to (40 39 40N 105 24 16W, T.8N., R.72W., Sec. 13). Unit 2 also includes Poverty Gulch from its
confluence with Cache la Poudre River (40 40 28N 105 25 44W, T.8N., R.72W., Sec. 11) upstream to 7,600 ft
(2,317 m) elevation (40 39 01N 105 26 40W, T.8N., R.72W., Sec. 22). Also includes Elkhorn Creek from its
confluence with Cache la Poudre River (40 41 50N 105 26 24W, T.9N., R.72W., Sec. 34) upstream to (40 44 03N
105 27 34W, T.9N., R.72W., Sec. 21). Also includes South Fork Cache la Poudre River from its confluence with
Cache la Poudre River (40 41 11N 105 26 50W, T.8N., R.72W., Sec. 3) upstream to 7,600 ft (2,317 m) elevation
(40 38 48N 105 29 22W, T.8N., R.72W., Sec. 20). Includes Pendergrass Creek from its confluence with South Fork
Cache la Poudre River (40 39 56N 105 27 30W, T.8N., R.72W., Sec. 15) upstream to 7,600 ft (2,317 m) elevation
(40 38 34N 105 27 28W, T.8N., R.72W., Sec. 22). Also included in the unit is Bennett Creek from its confluence
with Cache la Poudre River (40 40 26N 105 28 41W, T.8N., R.72W., Sec. 9) upstream to 7,600 ft (2,317 m)
elevation (40 39 19N 105 31 29W, T.8N., R.73W., Sec. 13).
(ii) Note: Map of Unit 2 follows:
eCFR graphic er15de10.004.gif
View or download PDF
(8) Unit 3: Buckhorn Creek, Larimer County, Colorado.
(i) This unit consists of 45.5 mi (73.2 km) of streams. Buckhorn Creek from (40 30 20N 105 13 39W, T.6N.,
R.70W., east boundary Sec. 9) upstream to 7,600 ft (2,317 m) elevation (40 34 17N 105 25 31W, T.7N., R.72W.,
Sec. 14). Includes Little Bear Gulch from its confluence with Buckhorn Creek (40 31 17N 105 15 33W, T.6N.,
R.70W., Sec. 5) upstream to (40 30 43N 105 16 35W, T.6N., R.70W., Sec. 6). Also includes Bear Gulch from its
confluence with Buckhorn Creek (40 31 16N 105 15 52W, T.6N., R.70W., Sec. 5) upstream to 7,600 ft (2,317 m)
elevation (40 29 45N 105 20 4W, T.6N., R.71W., Sec. 10). Also includes Stringtown Gulch from its confluence with
Buckhorn Creek (40 32 21N 105 16 42W, T.7N., R.70W., Sec. 30) upstream to 7,600 ft (2,317 m) elevation (40 30
30N 105 20 50W, T.6N., R.71W., Sec. 4). Also includes Fish Creek from its confluence with Buckhorn Creek (40
32 48N 105 18 20W, T.7N., R.70W., Sec. 30) upstream to 7,600 ft (2,317 m) elevation (40 30 56N 105 21 20W,
T.6N., R.71W., Sec. 4). Includes North Fork Fish Creek from its confluence with Fish Creek (40 32 48N 105 18
20W, T.7N., R.71W., west boundary Sec. 25) upstream and following the first unnamed tributary northwest to (40
33 34N 105 19 45W, T.7N., R.71W., Sec. 22). Also includes Stove Prairie Creek from its confluence with Buckhorn
Creek (40 34 16N 105 19 48W, T.7N., R.71W., Sec. 15) upstream to the dirt road crossing at (40 35 22N 105 20
17W, T.7N., R.71W., Sec. 10). Also includes Sheep Creek from its confluence with Buckhorn Creek (40 34 15N
105 20 53W, T.7N., R.71W., Sec. 16) upstream to 7,600 ft (2,317 m) elevation (40 33 08N 105 21 47W, T.7N.,
R.71W., Sec. 20). Also includes Twin Cabin Gulch from its confluence with Buckhorn Creek (40 34 38N 105 23
13W, T.7N., R.71W., Sec. 18) upstream to 7,600 ft (2,317 m) elevation (40 35 45N 105 23 36W, T.7N., R.71W.,
Sec. 6).
(ii) Note: Map of Units 3 and 4 follows:
eCFR graphic er15de10.005.gif
View or download PDF
(9) Unit 4: Cedar Creek, Larimer County, Colorado.
(i) This unit consists of 7.5 mi (12.1 km) of streams. Cedar Creek from the boundary of Federal land (40 26 46N
105 16 17W, T.6N., R.70W., Sec. 31) upstream to the boundary of Federal land (40 28 15N 105 18 11W, T.6N.,
R.71W., Sec. 24). Includes Dry Creek from its confluence with Cedar Creek (40 27 07N 105 16 16W, T.6N.,
R.70W., Sec. 30) upstream to the boundary of Federal land (40 28 52N 105 16 21W, T.6N., R.70W., Sec. 18). Also
includes Jug Gulch from its confluence with Cedar Creek (40 28 15N 105 17 41W, T.6N., R.71W., Sec. 24)
upstream to the boundary of Federal land (40 29 07N 105 18 28W, T.6N., R.71W., Sec. 14).
(ii) Note: Map of Unit 4 appears at paragraph (8)(ii) of this entry.
(10) Unit 5: South Boulder Creek, Boulder County, Colorado.
(i) This unit consists of 7.6 mi (12.2 km) of streams. Including South Boulder Creek from Baseline Road (40 0 0N
105 12 55W, T.1S., R.70W., Sec. 3) upstream to near Eldorado Springs, Colorado (39 56 7N 105 16 16W, T.1S.,
R.70W., Sec. 30). Unit 5 also includes Spring Brook from the Community Ditch near Eldorado Springs (39 55 59N
105 16 10W, T.1S., R.70W., Sec. 30) upstream to the Denver Water boundary at the South Boulder Diversion
Canal (39 55 13N 105 16 12W, T.1S., R.70W., Sec. 31).
(ii) Note: Map of Units 5, 6, and 7 follows:
eCFR graphic er15de10.006.gif
View or download PDF
(11) Unit 6: Rocky Flats Site, Jefferson County and Broomfield Counties, Colorado.
(i) This unit consists of three subunits including 12.5 mi (20.1 km) of streams as follows:
(A) The Woman Creek Subunit from Indiana Street (39 52 40N 105 9 55W, T.2S., R.70W., east boundary Sec. 13)
upstream to (39 53 3N 105 13 20W, T.2S., R.70W., west boundary Sec. 15). Includes unnamed tributary from
confluence with Woman Creek (39 52 43N 105 10 11W, T.2S., R.70W., Sec. 13) upstream to (39 52 39N 105 12
11W, T.2S., R.70W., west boundary Sec. 14).
(B) The Walnut Creek Subunit from Indiana Street (39 54 5N 105 9 55W, T.2S., R.70W., east boundary Sec. 1)
upstream to (39 53 49N 105 11 59W, T.2S., R.70W., Sec. 11). Includes unnamed tributary from its confluence with
Walnut Creek (39 54 6N 105 10 42W, T.2S., R.70W., Sec. 1) upstream to (39 53 35N 105 11 29W, T.2S., R.70W.,
Sec. 11).
(C) The Rock Creek Subunit from State Highway 128 (39 54 53N 105 11 40W, T.1S., R.70W., Sec. 35) upstream
to (39 54 17N 105 13 20W, T.2S., R.70W., west boundary Sec. 3). Includes an unnamed tributary from its
confluence with Rock Creek (39 54 40N 105 12 11W, T.2S., R.70W., east boundary Sec. 3) upstream to (39 54 42
N 105 13 00W, T.2S., R.70W., Sec. 3). Also includes an unnamed tributary from its confluence with Rock Creek at
(39 54 26N 105 12 34W, T.2S., R.70W., Sec. 3) upstream to (39 54 7N 105 12 52W, T.2S., R.70W., Sec. 3).
Includes another unnamed tributary from its confluence with Rock Creek at (39 54 23N 105 12 56W, T.2S.,
R.70W., Sec. 3) upstream to (39 54 8N 105 13 20W, T.2S., R.70W., west boundary Sec. 3. Includes another
unnamed tributary from its confluence with Rock Creek at (39 54 15N 105 13 5W, T.2S., R.70W., Sec. 3) upstream
to (39 54 08N 105 13 09W, T.2S., R.70W., Sec. 3).
(ii) Note: Map of Unit 6 appears at paragraph (10)(ii) of this entry.
(12) Unit 7: Ralston Creek, Jefferson County, Colorado.
(i) This unit consists of 8.5 mi (13.7 km) of streams. Ralston Creek from 6,065 ft (1,849 m) elevation at the
northern edge of Denver Water property just upstream of Ralston Reservoir (39 49 12N 105 15 35W, T.3S.,
R.70W., Sec. 6) upstream into Golden Gate Canyon State Park to 7,600 ft (2,300 m) elevation (39 50 53 105 21
16W, T.2S., R.71W., Sec. 29).
(ii) Note: Map of Unit 7 appears at paragraph (10)(ii) of this entry.
(13) Unit 8: Cherry Creek, Douglas County, Colorado.
(i) This unit consists of two subunits including 29.8 mi (47.9 km) of streams as follows:
(A) The Lake Gulch Subunit including Cherry Creek from the northern boundary of Castlewood Canyon State
Recreation Area (39 21 44N 104 45 39W, T.8S., R.66W., south boundary Sec. 10) upstream to the confluence with
Lake Gulch (39 20 24N 104 45 36W, T.8S., R.66W., Sec. 23). Lake Gulch from the aforementioned confluence
upstream to (39 15 37N 104 46 05W, T.9S., R.66W., south boundary Sec. 15). Includes Upper Lake Gulch from its
confluence with Lake Gulch (39 17 24N 104 46 11W, T.9S., R.66W., Sec. 3) upstream to (39 13 24N 104 50 21W,
T.9S., R.67W., mid-point Sec. 36).
(B) The Antelope Creek Subunit from its confluence with West Cherry Creek (39 16 11N 104 42 49W, T.9S
R.65W., S18) upstream to the Franktown Parker Reservoir (39 10 20N 104 46 16W, T.10S R.66W., S22). It also
includes Haskel Creek from its confluence with Antelope Creek (39 13 43N, 104 45 5W, T.9S R.66W., S35)
upstream to the Haskel Creek Spring Pond at 7,000 ft (2,134 m) elevation (39 11 60N 104 47 40N, T.10S R.66W.,
S8).
(ii) Note: Map of Unit 8 follows:
eCFR graphic er15de10.007.gif
View or download PDF
(14) Unit 9: West Plum Creek, Douglas County, Colorado.
(i) This unit consists of 90.3 mi (145.3 km) of streams. Plum Creek from Chatfield Lake (39 32 35N 105 03 07W,
T.6S., R.68W., Sec. 7) upstream to its confluence with West Plum Creek and East Plum Creek (39 25 49N 104 58
8W, T.7S., R.68W., Sec. 23), excluding 0.14 mi (0.23 km) of Plum Creek owned by Denver Water at the Highline
Canal crossing (excluding from 39 30 44N 105 01 41W, T.6S., R.68W., Sec. 20 downstream to 39 30 41N 105 01
32W, T.6S., R.68W., Sec. 20). West Plum Creek from the aforementioned confluence (39 25 49N 104 58 8W,
T.7S., R.68W., Sec. 23) upstream to the boundary of Pike-San Isabel National Forest and 7,600 ft (2,317 m)
elevation (39 13 07N 104 59 20W, T.9S., R.68W., Sec. 34). Includes Indian Creek from its confluence with Plum
Creek (39 28 22N 104 59 57W, T.7S., R.68W., Sec. 4) upstream to Silver State Youth Camp (39 22 24N 105 05
13W, T.8S., R.69W., Sec. 11). Indian Creek includes an unnamed tributary from its confluence with Indian Creek at
Pine Nook (39 23 01N 105 04 24W, T.8S., R.69W., Sec. 2) upstream to (39 22 10N 105 04 08W, T.8S., R.69W.,
Sec. 12). Also includes Jarre Creek from its confluence with Plum Creek (39 25 50N 104 58 15W, T.7S., R.68W.,
Sec. 23) upstream to 7,600 ft (2,317 m) elevation (39 21 50N 105 03 20W, T.8S., R.69W., Sec. 12). Jarre Creek
includes an unnamed tributary from its confluence with Jarre Creek (39 22 58N 105 01 52W, T.8S., R.68W., Sec.
5) upstream to (39 22 44N 105 02 14W, T.8S., R.68W., Sec. 8). Also includes an unnamed tributary from its
confluence with West Plum Creek (39 22 20N 104 57 39W, T.8S., R.68W., Sec. 11) upstream to (39 21 36N 104
55 40W, T.8S, R67W., Sec.18). Unit 9 also includes Garber Creek from its confluence with Plum Creek (39 22 10N
104 57 49W, T.8S., R.68W., Sec. 11) upstream to its confluence with South Garber Creek and Middle Garber
Creek (39 21 02N 105 02 13W, T.8S., R.68W., Sec. 18). Including South Garber Creek from its confluence with
Garber Creek (39 21 02N 105 02 13W, T.8S., R.68W., Sec. 18) upstream to 7,600 ft (2,317 m) elevation (39 19
14N 105 03 13W, T.8S., R.69W., Sec. 25). Including Middle Garber Creek from its confluence with Garber Creek
(39 20 55N 105 02 35W, T.8S., R.68W., Sec. 18) upstream to (39 19 48N 105 04 09W, T.8S., R.69W., west
boundary Sec. 25). Including North Garber Creek from its confluence with Middle Garber Creek (39 20 55N 105 02
35W, T.8S., R.68W., Sec. 18) upstream to 7,600 ft (2,317 m) elevation (39 20 47N 105 04 37W, T.8S., R.69W.,
Sec. 23). Includes Jackson Creek from its confluence with Plum Creek (39 21 02N 104 58 30W, T.8S., R.68W.,
Sec. 14) upstream to 7,600 ft (2,317 m) elevation (39 17 59N 105 03 57W, T.9S., R.69W., Sec. 1). Includes Spring
Creek from its confluence with West Plum Creek at (39 19 04N 104 58 26W, T.8S., R.68W., Sec. 35) upstream to
(39 15 21N 105 01 40W, T.9S., R.68W., Sec. 20). Including Dry Gulch from its confluence with Spring Creek (39
17 54N 104 59 58W, T.9S., R.68W., Sec. 4) upstream to 7,600 ft (2,317 m) elevation (39 16 07N 105 02 33W,
T.9S., R.68W., Sec. 18). Including Bear Creek from its confluence with West Plum Creek (39 17 30N 104 58 25W,
T.9S., R.68W., Sec. 2) upstream to the base of the Waconda Lake dam (39 15 43 N, 104 59 09 W, T.9S, R.68W,
Sec.15). Including Gove Creek from its confluence with West Plum Creek (39 14 07N 104 57 42W, T.9S., R.68W.,
Sec. 26) upstream to 7,600 ft (2,317 m) elevation (39 11 50N 104 58 32W, T.10S., R.68W., Sec. 11). Includes Merz
Canyon stream from its confluence with Gove Creek (39 13 05N 104 57 33W, T.9S., R.68W., Sec. 36) upstream to
(39 12 39N 104 57 04 W, T.10S., R.68W., Sec.1). Includes Starr Canyon stream from its confluence with West
Plum Creek (39 13 07N 104 58 41W, T.9S., R.68W., Sec. 35) upstream to 7,600 ft (2,317 m) elevation (39 12 32N
104 59 01W, T.10S., R.68W., Sec. 3).
(ii) Note: Map of Unit 9 follows:
eCFR graphic er15de10.008.gif
View or download PDF
(15) Unit 10: Upper South Platte River, Douglas, Jefferson, and Teller Counties, Colorado.
(i) This unit consists of four subunits including 33.6 mi (54.1 km) of rivers and streams as follows:
(A) The Chatfield Subunit, on the border of Jefferson County and Douglas County entirely within Chatfield State
Park from Chatfield Lake (39 31 32N 105 04 45W, T.6S., R.69W., Sec. 14) upstream to the northern boundary of
the Kassler Center land owned by Denver Water (39 29 35N 105 05 14W, T.6S., R.69W., Sec. 26).
(B) The Bear Creek Subunit, Douglas County from Pike-San Isabel National Forest boundary (39 25 27N 105 07
40W, T.7S., R.69W., west boundary Sec. 21) upstream to (39 22 32N 105 06 40W, T.8S., R.69W., south boundary
Sec. 4). Includes West Bear Creek from its confluence with Bear Creek (39 25 15N 105 07 30W, T.7S., R.69W.,
Sec. 21) upstream to a confluence with an unnamed tributary (39 24 17N 105 07 38W, T.7S., R.69W., Sec. 33).
(C) The South Platte River Subunit, on the border of Jefferson County and Douglas County from the southern
boundary of Denver Water land near Nighthawk (39 21 04N 105 10 28W, T.8S., R.70W., Sec. 13) upstream to the
north eastern boundary of Denver Water land at (39 18 47N 105 11 33W, T.8S., R.70W., Sec. 35), excluding
Denver Water lands along this stretch (39 19 10N 105 11 17W, T.8S., R.70W., Sec. 26), and utilizing the Douglas
County Riparian Conservation Zones on non-Federal lands. Also included in this subunit from the southwestern
boundary of Denver Water property at (39 18 04N 105 12 03W, T.9S., R.70W., Sec. 2) to the north eastern
boundary of Denver Water property at (39 17 27N 105 12 24W, T.9S., R.70W., Sec. 3). Includes Sugar Creek,
within Douglas County from the eastern boundary of Denver Water land near Oxyoke (39 18 24N 105 11 32W,
T.8S., R.70W., Sec. 35) upstream to 7,600 ft (2,317 m) elevation (39 18 31N 105 08 09W, T.8S., R.69W., Sec. 32).
Includes Gunbarrel Creek, within Jefferson County from the western boundary of Denver Water land near Oxyoke
(39 18 27N 105 12 06W, T.8S., R.70W., Sec. 34) upstream to (39 18 41N 105 14 36W, T.8S., R.70W., Sec. 32).
(D) The Trout Creek Subunit, Douglas County upstream into Teller County from (39 13 02N 105 09 31W, T.9S.,
R.69W., Sec. 31) upstream to 7,600 ft (2,317 m) elevation which is 0.8 mi (1.3 km) into Teller County (39 07 13N
105 05 49W, T.11S., R.69W., Sec. 3). Includes Eagle Creek from its confluence with Trout Creek (39 11 52N 105
08 27W, T.10S., R.69W., Sec. 8) upstream to 7,600 ft (2,317 m) elevation (39 12 06N 105 07 12W, T.10S., R.69W.,
Sec. 9). Also including an unnamed tributary from its confluence with Trout Creek (39 11 07N 105 08 05W, T.10S.,
R.69W., Sec. 17) upstream to (39 10 18N 105 08 23W, T.10S., R.69W., Sec. 20). Also including Long Hollow from
its confluence with Trout Creek (39 10 56N 105 08 01W, T.10S., R.69W., Sec. 17) upstream to 7,600 ft (2,317 m)
elevation (39 11 30N 105 06 19W, T.10S., R.69W., Sec. 10).
(ii) Note: Map of Unit 10 follows:
eCFR graphic er15de10.009.gif
View or download PDF
(16) Unit 11: Monument Creek, El Paso County, Colorado.
(i) This unit consists of 38.0 mi (61.1 km) of streams. Monument Creek from its confluence with Cottonwood Creek
(38 55 36N 104 48 55W, T.13S., R66W., Sec. 7) upstream to the southern property boundary of the U.S. Air Force
Academy (38 57 08N 104 49 49W, T.13S., R.66W., Sec. 6), excluding 0.82 ac (0.33 ha) on the Dahle property (38
56 56N 104 49 39W, T.13S., R66W., Sec. 6). Then Monument Creek from the northern property boundary of the
U.S. Air Force Academy (39 02 31N 104 51 05W, T.12S., R.67W., north boundary Sec. 2) upstream to Monument
Lake (39 05 19N 104 52 43W, T.11S., R.67W., Sec. 15). Includes Kettle Creek from the property boundary of the
U.S. Air Force Academy (38 58 33N 104 47 55W, T.12S., R.66W., Sec. 29) upstream to its intersection with a road
at (39 00 07N 104 45 24W, T.12S., R.66W., east boundary Sec. 15). Which includes an unnamed tributary from its
confluence with Kettle Creek (38 59 06N 104 46 55W, T.12S., R.66W., Sec. 21) upstream to (38 59 14N 104 46
19W, T.12S., R.66W., Sec. 22). Also includes Black Squirrel Creek from the property boundary of the U.S. Air
Force Academy (39 00 06N 104 49 00W, T.12S., R.66W., Sec. 18) upstream to (39 02 30N 104 44 38W, T.12S.,
R.66W., north boundary Sec. 2). Including an unnamed tributary from its confluence with Black Squirrel Creek (39
01 19N 104 46 21W, T.12S., R.66W., Sec. 10) upstream to (39 02 30N 104 45 42W, T.12S., R.66W., north
boundary Sec. 3). Which includes another unnamed tributary from (39 01 50N 104 46 20W, T.12S., R.66W., Sec.
3) upstream to (39 02 30N 104 46 03W, T.12S., R.66W., north boundary Sec. 3), excluding approximately 5 ac (2
ha) on the Lefever property (39 00 57N 104 46 33W, T.12S., R.66W., Sec. 9). Also includes an unnamed tributary
from the property boundary of the U.S. Air Force Academy (39 00 14N 104 49 3W, T.12S., R.66W., Sec. 18)
upstream to 6,700 ft (2,043 m) elevation (39 0 29N 104 48 24W, T.12S., R.66W., Sec. 17). Including an unnamed
tributary from (39 0 19N 104 48 55W, T. 12S., R.66W., Sec. 18) upstream to (39 0 30N 104 48 48N, T. 12S.,
R.66W., Sec. 18). Unit 11 also includes Monument Branch from the property boundary of the U.S. Air Force
Academy (39 00 50N 104 49 24W, T.12S., R.66W., Sec. 7) upstream to (39 01 10N 104 48 45W, T.12S., R.66W.,
east boundary Sec. 7). Also includes Smith Creek from the property boundary of the U.S. Air Force Academy (39
01 36N 104 49 46W, T.12S., R.66W., Sec. 7) upstream to (39 02 24N 104 48 00W, T.12S., R.66W., Sec. 5). Also
includes Jackson Creek from its confluence with Monument Creek (39 02 33N 104 51 13W, T.11S., R.67W., Sec.
35) upstream to (39 04 30N 104 49 10W, T.11S., R.66W., Sec. 19). Includes an unnamed tributary from its
confluence with Jackson Creek (39 04 12N 104 50 05W, T.11S., R.67W., Sec. 25) upstream to Higby Road (39 04
42N 104 49 40W, T.11S., R.66W., Sec. 19). Also includes Beaver Creek from its confluence with Monument Creek
(39 02 52N 104 52 02W, T.11S., R.67W., Sec. 35) upstream to 7,600 ft (2,317 m) elevation (39 03 08N 104 55
32W, T.11S., R.67W., Sec. 31). Also includes Teachout Creek from its confluence with Monument Creek (39 03
44N 104 51 53W, T.11S., R.67W., Sec. 26) upstream to Interstate 25 (39 04 19N 104 51 29W, T.11S., R.67W.,
Sec. 23). Also includes Dirty Woman Creek from its confluence with Monument Creek (39 04 55N 104 52 34W,
T.11S., R.67W., Sec. 22) upstream to Highway 105 (39 05 35N 104 51 28 W, T.11S., R.67W., Sec. 14).
(ii) Note: Map of Unit 11 follows:
eCFR graphic er15de10.010.gif
View or download PDF
St. Andrew Beach Mouse (Peromyscus
polionotus peninsularis)
(1) Critical habitat units are depicted for Bay and Gulf Counties, Florida, on the maps below.
(2) The primary constituent elements of critical habitat for the St. Andrew beach mouse are the habitat
components that provide:
(i) A contiguous mosaic of primary, secondary, and scrub vegetation and dune structure, with a balanced level of
competition and predation and few or no competitive or predaceous nonnative species present, that collectively
provide foraging opportunities, cover, and burrow sites;
(ii) Primary and secondary dunes, generally dominated by sea oats (Uniola paniculata), that despite occasional
temporary impacts and reconfiguration from tropical storms and hurricanes, provide abundant food resources,
burrow sites, and protection from predators;
(iii) Scrub dunes, generally dominated by scrub oaks (Quercus spp.), that provide food resources and burrow sites,
and provide elevated refugia during and after intense flooding due to rainfall and/or hurricane-induced storm surge;
(iv) Functional, unobstructed habitat connections that facilitate genetic exchange, dispersal, natural exploratory
movements, and re-colonization of locally extirpated areas; and
(v) A natural light regime within the coastal dune ecosystem, compatible with the nocturnal activity of beach mice,
necessary for normal behavior, growth, and viability of all life stages.
(3) Critical habitat does not include man-made structures existing on the effective date of this rule and not
containing one or more of the primary constituent elements, such as buildings, aqueducts, airports, driveways, and
roads, and the land on which such structures are located.
(4) Critical Habitat Map Units. Data layers defining map units were created by delineating habitats that contained
one or more of the primary constituent elements defined in paragraph (2) of this entry over 1999 and 2004 digital
ortho photography at a scale of at least 1:4000.
(5) Note: Map 1, Index Map of Critical Habitat Units for the St. Andrew beach mouse, follows:
eCFR graphic er12oc06.007.gif
View or download PDF
(6) SABM—Unit 1: East Crooked Island, Gulf County, Florida.
(i) General Description: This unit encompasses essential features of beach mouse habitat on East Crooked Island
from the entrance of St. Andrew Sound to 1 mi west of Mexico Beach, not including Raffield Peninsula, and the
area from the mean high water level (MHWL) to the seaward extent of the maritime forest.
(ii) Map 2, Unit 1 of St. Andrew beach mouse, follows:
eCFR graphic er12oc06.008.gif
View or download PDF
(7) SABM—Unit 2: Palm Point Unit, Gulf County, Florida.
(i) General Description: This unit encompasses habitat from Palm Point 1.25 mi northwest of the inlet of the Gulf
County Canal to St. Joe Beach and the area from the MHWL to the seaward extent of the maritime forest.
(ii) Map of SABM—Unit 2 is provided at paragraph (8)(ii) of this entry.
(8) SABM—Unit 3: St. Joseph Peninsula, Gulf County, Florida.
(i) General Description: This unit encompasses essential features of beach mouse habitat within the boundary of
St. Joseph Peninsula State Park (Park) as well as south of the Park to the peninsula's constriction north of Cape
San Blas (also known as the “stumphole” region) and area from the MHWL to the seaward extent of the maritime
forest.
(ii) Map 3, Units 2 and 3 of St. Andrew beach mouse, follows:
eCFR graphic er12oc06.009.gif
View or download PDF
Northern Sea Otter (Enhydra lutris kenyoni),
Southwest Alaska Distinct Population
Segment:
(1) Critical habitat units are in Alaska, as described below. The index map provided is for informational purposes
only.
(2) The primary constituent elements of critical habitat for the southwest Alaska distinct population segment (DPS)
of the northern sea otter are:
(i) Shallow, rocky areas where marine predators are less likely to forage, which are in waters less than 2 m (6.6 ft)
in depth;
(ii) Nearshore waters within 100 m (328.1 ft) from the mean high tide line;
(iii) Kelp forests, which occur in waters less than 20 m (65.6 ft) in depth; and
(iv) Prey resources within the areas identified in paragraphs (2)(i), (2)(ii), and (2)(iii) of this entry that are present in
sufficient quantity and quality to support the energetic requirements of the species.
(3) Critical habitat does not include manmade structures (including, but not limited to, docks, seawalls, pipelines,
or other structures) and the land on which they are located existing within the boundaries on the effective date of
this rule.
(4) Critical habitat map units. Boundaries of critical habitat were derived from GIS data layers of hydrographic
survey data developed by the National Oceanic and Atmospheric Administration. To estimate the size of each
critical habitat unit, the data were projected into Alaska Standard Albers Conical Equal Area on the North
American Datum of 1983. Given the large geographic range of this DPS, some two-dimensional areas appear as
one-dimensional features at these map scales.
(5) Note: Index map of critical habitat for the southwest Alaska DPS of the northern sea otter follows:
eCFR graphic er08oc09.002.gif
View or download PDF
(6) Unit 1: Western Aleutian. All contiguous waters from the mean high tide line to the 20-m (65.6-ft) depth contour
as well as waters within 100 m (328.1 ft) of the mean high tide line that occur adjacent to the following islands:
Adak, Agattu, Alaid, Amatignak, Amchitka, Amlia, Amukta, Anagaksik, Asuksak, Atka, Attu, Aziak, Bobrof, Buldir,
Carlisle, Chagula, Chuginadak, Chugul, Crone, Davidof, Elf, Gareloi, Great Sitkin, Herbert, Igitkin, Ilak, Kagalaska,
Kagamil, Kanaga, Kanu, Kasatochi, Kavalga, Khvostof, Kiska, Koniuji, Little Kiska, Little Sitkin, Little Tanaga, Nizki,
Ogliuga, Oglodak, Rat, Sadatanak, Sagchudak, Salt, Seguam, Segula, Semisopochnoi, Shemya, Skagul,
Tagadak, Tagalak, Tanaga, Tanaklak, and Ulak.
(7) Unit 2: Eastern Aleutian. All contiguous waters from the mean high tide line to the 20-m (65.6-ft) depth contour
as well as waters within 100 m (328.1 ft) of the mean high tide line that occur adjacent to the following islands:
Aiktak, Akutan, Amaknak, Arangula, Atka, Avatanak, Baby Islands, Bogoslof, Egg, Hog, Kaligagan, Rootok,
Samalga, Sedanka, Tigalda, Ugamak, Umnak, Unalaska, Unalga, and Vsevidof.
(8) Unit 3: South Alaska Peninsula. All contiguous waters from the mean high tide line to the 20-m (65.6-ft) depth
contour as well as waters within 100 m (328.1 ft) of the mean high tide line that occur adjacent to the Alaska
Peninsula from False Pass (54.242° N, 163.363° W) to Castle Cape (56.242° N, 158.117° W), and adjacent to the
following islands: Andronica, Atkins, Big Koniuji, Bird, Brother, Caton, Chankliut, Chernabura, Cherni, Chiachi,
Deer, Dolgoi, Egg, Goloi, Guillemot, Inner Iliask, Jacob, Karpof, Korovin, Little Koniuji, Mitrofania, Nagai, Near,
Outer Iliask, Paul, Peninsula, Pinusuk, Poperechnoi, Popof, Road, Sanak, Shapka, Simeonof, Spectacle, Spitz,
Turner, Ukolnoi, Ukolnoi, Unga, and Unimak Island from Scotch Cap (54.390° N, 164.745° W) to False Pass.
(9) Unit 4: Bristol Bay. This unit contains three subunits:
(i) Subunit 4a: Amak Island. All contiguous waters from the mean high tide line to the 20-m (65.6-ft) depth contour
as well as waters within 100 m (328.1 ft) of the mean high tide line that occur adjacent to Amak Island.
(ii) Subunit 4b: Izembek Lagoon. All waters from mean high tide line that occur within the polygon bounded by
Glen, Operl, and Neumann Islands to the north and the Alaska Peninsula to the south, and further defined by the
following latitude/longitude coordinates: 55.249° N, 162.990° W; 55.255° N, 162.984° W from Cape Glazenap to
Glen Island; 55.324° N, 162.901° W; 55.333° N, 162.888° W from Glen Island to Operl Island; 55.409° N, 162.683°
W; 55.408° N, 162.621° W from Operl Island to Neumann Island; and 55.447° N, 162.582° W; 55.447° N, 162.577°
W from Neumann Island to Moffet Point.
(iii) Subunit 4c: Port Moller/Herendeen Bay. All waters from mean high tide line that occur within the polygon
bounded by Walrus Island to the north and the Alaska Peninsula to the south, and further defined by the following
latitude/longitude coordinates: 56.000° N, 160.877° W; 56.020° N, 160.854° W from Point Edward to Walrus
Island; and 56.020° N, 160.805° W; 55.979° N, 160.584° W from Wolf Point to Entrance Point.
(10) Unit 5: Kodiak, Kamishak, Alaska Peninsula. All contiguous waters from the mean high tide line to the 20-m
(65.6-ft) depth contour as well as waters within 100 m (328.1 ft) of the mean high tide line that occur adjacent to
the Alaska Peninsula from Castle Cape (56° 14.5' N, 158° 7.0' W) eastward to Cape Douglas (58.852° N, 153.250°
W), and northward in Cook Inlet to Redoubt Point (60.285° N, 152.417° W), and adjacent to the following islands:
Afognak, Aghik, Aghiyuk, Aiaktalik, Akhiok, Aliksemit, Amook, Anowik, Ashiak, Atkulik, Augustine, Ban, Bare, Bear,
Central, Chirikof, Chisik, Chowiet, Dark, David, Derickson, Dry Spruce, Eagle, East Amatuli, East Channel,
Garden, Geese, Hartman, Harvester, Hydra, Kak, Kateekuk, Kiliktagik, Kiukpalik, Kodiak, Kumlik, Long, Marmot,
Miller, Nakchamik, Ninagiak, Nord, Nordyke, Poltava, Raspberry, Sally, Shaw, Shuyak, Sitkalidak, Sitkanak,
Spruce, Sud, Sugarloaf, Suklik, Sundstrom, Sutwick, Takli, Terrace, Tugidak, Twoheaded, Ugak, Ugalushik,
Uganik, Unavikshak, Ushagat, West Amatuli, West Augustine, West Channel, Whale, and Woody.
Olympia pocket gopher (Thomomys
mazama pugetensis)
(1) Critical habitat for the Olympia pocket gopher in Thurston County, Washington, is depicted on the map below.
(2) Within this area, the primary constituent elements of the physical or biological features essential to the
conservation of the Olympia pocket gopher consist of two components:
(i) Friable, loamy, and deep soils, some with relatively greater content of sand, gravel, or silt, all generally on
slopes less than 15 percent in the following soil series or soil series complex:
(A) Alderwood;
(B) Cagey;
(C) Everett;
(D) Godfrey;
(E) Indianola;
(F) Kapowsin;
(G) McKenna;
(H) Nisqually;
(I) Norma;
(J) Spana;
(K) Spanaway;
(L) Spanaway-Nisqually complex; and
(M) Yelm.
(ii) Areas equal to or larger than 50 ac (20 ha) in size that provide for breeding, foraging, and dispersal activities,
found in the soil series listed in paragraph (2)(i) of this entry that have:
(A) Less than 10 percent woody vegetation cover;
(B) Vegetative cover suitable for foraging by gophers. Pocket gophers' diets include a wide variety of plant
material, including leafy vegetation, succulent roots, shoots, tubers, and grasses. Forbs and grasses that Mazama
pocket gophers eat are known to include, but are not limited to: Achillea millefolium (common
yarrow), Agoseris spp. (agoseris), Cirsium spp. (thistle), Bromus spp. (brome), Camassia spp. (camas), Collomia
linearis (tiny trumpet), Epilobium spp. (several willowherb spp.), Eriophyllum lanatum (woolly
sunflower), Gayophytum diffusum(groundsmoke), Hypochaeris radicata (hairy cat's ear), Lathyrus spp.
(peavine), Lupinus spp. (lupine), Microsteris gracilis (slender phlox), Penstemon spp. (penstemon), Perideridia
gairdneri (Gairdner's yampah), Phacelia heterophylla (varileaf phacelia), Polygonum
douglasii (knotweed), Potentilla spp. (cinquefoil), Pteridium aquilinum(bracken fern), Taraxacum
officinale (common dandelion), Trifolium spp. (clover), and Viola spp. (violet); and
(C) Few, if any, barriers to dispersal. Barriers to dispersal may include, but are not limited to, forest edges, roads
(paved and unpaved), abrupt elevation changes, Scot's broom thickets, highly cultivated lawns, inhospitable soil
types or substrates, development and buildings, slopes greater than 35 percent, and open water.
(3) Critical habitat does not include manmade structures (such as buildings, aqueducts, runways, roads, railroad
tracks, and other paved areas) and the land on which they are located existing within the legal boundaries on May
9, 2014.
(4) Critical habitat map unit. Data layers defining map units were created on 2010 aerial photography from U.S.
Department of Agriculture, National Agriculture Imagery Program base maps using ArcMap (Environmental
Systems Research Institute, Inc.), a computer geographic information system (GIS) program. The map in this
entry, as modified by any accompanying regulatory text, establishes the boundaries of the critical habitat
designation. The coordinates or plot points or both on which the map is based are available to the public at the
Service's Internet site at http://www.fws.gov/wafwo/mpg.html, at http://www.regulations.gov (Docket No. FWS-R1ES-2013-0021), and at the field office responsible for this designation. You may obtain field office location
information by contacting one of the Service regional offices, the addresses of which are listed at 50 CFR 2.2.
(5) Olympia Airport Unit, Thurston County, Washington. Map follows:
eCFR graphic er09ap14.000.gif
View or download PDF
Tenino Pocket Gopher (Thomomys mazama
tumuli)
(1) Critical habitat for the Tenino pocket gopher in Thurston County, Washington, is depicted on the map below.
(2) Within this area, the primary constituent elements of the physical or biological features essential to the
conservation of Tenino pocket gopher consist of two components:
(i) Friable, loamy, and deep soils, some with relatively greater content of sand, gravel, or silt, all generally on
slopes less than 15 percent in the following soil series or soil series complex:
(A) Alderwood;
(B) Cagey;
(C) Everett;
(D) Indianola;
(E) Kapowsin;
(F) Nisqually;
(G) Norma;
(H) Spanaway;
(I) Spanaway-Nisqually complex; and
(J) Yelm.
(ii) Areas equal to or larger than 50 ac (20 ha) in size that provide for breeding, foraging, and dispersal activities,
found in the soil series listed in paragraph (2)(i) of this entry that have:
(A) Less than 10 percent woody vegetation cover;
(B) Vegetative cover suitable for foraging by gophers. Pocket gophers' diets include a wide variety of plant
material, including leafy vegetation, succulent roots, shoots, tubers, and grasses. Forbs and grasses that Mazama
pocket gophers are known to eat include, but are not limited to: Achillea millefolium (common
yarrow), Agoseris spp. (agoseris), Cirsium spp. (thistle), Bromus spp. (brome), Camassia spp. (camas), Collomia
linearis (tiny trumpet), Epilobium spp. (several willowherb spp.), Eriophyllum lanatum (woolly
sunflower), Gayophytum diffusum(groundsmoke), Hypochaeris radicata (hairy cat's ear), Lathyrus spp.
(peavine), Lupinus spp. (lupine), Microsteris gracilis (slender phlox), Penstemon spp. (penstemon), Perideridia
gairdneri (Gairdner's yampah), Phacelia heterophylla (varileaf phacelia), Polygonum
douglasii (knotweed), Potentilla spp. (cinquefoil), Pteridium aquilinum(bracken fern), Taraxacum
officinale (common dandelion), Trifolium spp. (clover), and Viola spp. (violet); and
(C) Few, if any, barriers to dispersal. Barriers to dispersal may include, but are not limited to, forest edges, roads
(paved and unpaved), abrupt elevation changes, Scot's broom thickets, highly cultivated lawns, inhospitable soil
types or substrates, development and buildings, slopes greater than 35 percent, and open water.
(3) Critical habitat does not include manmade structures (such as buildings, aqueducts, runways, roads, and other
paved areas) and the land on which they are located existing within the legal boundaries on May 9, 2014.
(4) Critical habitat map unit. Data layers defining the map unit were created on 2010 aerial photography from U.S.
Department of Agriculture, National Agriculture Imagery Program base maps using ArcMap (Environmental
Systems Research Institute, Inc.), a computer geographic information system (GIS) program. The map in this entry
establishes the boundaries of the critical habitat designation. The coordinates or plot points or both on which the
map is based are available to the public at the Service's Internet site
at http://www.fws.gov/wafwo/, at http://www.regulations.gov (Docket No. FWS-R1-ES-2013-0021), and at the field
office responsible for this designation. You may obtain field office location information by contacting one of the
Service regional offices, the addresses of which are listed at 50 CFR 2.2.
(5) Rocky Prairie Unit, Thurston County, Washington. Map follows:
eCFR graphic er09ap14.001.gif
View or download PDF
Yelm Pocket Gopher (Thomomys mazama
yelmensis)
(1) Critical habitat for the Yelm pocket gopher in Thurston County, Washington, is depicted on the map below.
(2) Within these areas, the primary constituent elements of the physical or biological features essential to the
conservation of the Yelm pocket gopher consist of two components:
(i) Friable, loamy, and deep soils, some with relatively greater content of sand, gravel, or silt, all generally on
slopes less than 15 percent in the following soil series or soils series complex:
(A) Alderwood;
(B) Cagey;
(C) Everett;
(D) Godfrey;
(E) Indianola;
(F) Kapowsin;
(G) McKenna;
(H) Nisqually;
(I) Norma;
(J) Spanaway;
(K) Spanaway-Nisqually complex; and
(L) Yelm.
(ii) Areas equal to or larger than 50 ac (20 ha) in size that provide for breeding, foraging, and dispersal activities,
found in the soil series listed in paragraph (2)(i) of this entry that have:
(A) Less than 10 percent woody vegetation cover;
(B) Vegetative cover suitable for foraging by gophers. Pocket gophers' diets include a wide variety of plant
material, including leafy vegetation, succulent roots, shoots, tubers, and grasses. Forbs and grasses that Mazama
pocket gophers are known to eat include, but are not limited to: Achillea millefolium (common
yarrow), Agoseris spp. (agoseris), Cirsium spp. (thistle), Bromus spp. (brome), Camassia spp. (camas), Collomia
linearis (tiny trumpet), Epilobium spp. (several willowherb spp.), Eriophyllum lanatum (woolly
sunflower), Gayophytum diffusum(groundsmoke), Hypochaeris radicata (hairy cat's ear), Lathyrus spp.
(peavine), Lupinus spp. (lupine), Microsteris gracilis (slender phlox), Penstemon spp. (penstemon), Perideridia
gairdneri (Gairdner's yampah), Phacelia heterophylla (varileaf phacelia), Polygonum
douglasii (knotweed), Potentilla spp. (cinquefoil), Pteridium aquilinum(bracken fern), Taraxacum
officinale (common dandelion), Trifolium spp. (clover), and Viola spp. (violet); and
(C) Few, if any, barriers to dispersal. Barriers to dispersal may include, but are not limited to, forest edges, roads
(paved and unpaved), abrupt elevation changes, Scot's broom thickets, highly cultivated lawns, inhospitable soil
types or substrates, development and buildings, slopes greater than 35 percent, and open water.
(3) Critical habitat does not include manmade structures (such as buildings, aqueducts, runways, roads, and other
paved areas) and the land on which they are located existing within the legal boundaries on May 9, 2014.
(4) Critical habitat map units. Data layers defining the map units were created on 2010 aerial photography from
U.S. Department of Agriculture, National Agriculture Imagery Program base maps using ArcMap (Environmental
Systems Research Institute, Inc.), a computer geographic information system (GIS) program. The map in this entry
establishes the boundaries of the critical habitat designation. The coordinates or plot points or both on which the
map is based are available to the public at the Service's Internet site
at http://www.fws.gov/wafwo/, at http://www.regulations.gov (Docket No. FWS-R1-ES-2013-0021), and at the field
office responsible for this designation. You may obtain field office location information by contacting one of the
Service regional offices, the addresses of which are listed at 50 CFR 2.2.
(5) Tenalquot Prairie and Rock Prairie Subunits, Thurston County, Washington.
Map follows:
eCFR graphic er09ap14.002.gif
View or download PDF
Silver Rice Rat (Oryzomys palustris
natator(=O. argentatus)).
Monroe County, Florida: Little Pine Key, Water Keys, Big Torch Key, Middle Torch Key, Summerland Key north of
U.S. Highway 1, Cudjoe Key north of U.S. Highway 1, Johnston Key, Raccoon Key, and Lower Saddlebunch Keys,
south of U.S. Highway 1 but not including lands in T. 67 S., R. 27 E., Section 8 and north 1⁄5 of Section 17.
Included are all lands and waters above mean low tide.
Within these areas the major constituent elements that are known to require special management considerations
or protection are mangrove swamps containing red (Rhizophora mangle), black (Avicennia germinans), and white
(Laguncularia racemosa) mangroves, and buttonwood (Conocarpus erectus); salt marshes, swales, and adjacent
transitional wetlands containing saltwort (Batis maritima), perennial glasswort (Salicornia virginica), saltgrass
(Distichlis spicata), sea ox-eye (Borrichia frutescens), keygrass (Monanthochloe littoralis), and coastal dropseed
(Sporobolus virginicus); and fresh water marshes containing cattails (Typha domingensis), saw-grass (Cladium
jamaicense), and cordgrass (Spartina spp.).
Note: The map provided is for informational purposes only. Map follows:
eCFR graphic ec01jn91.018.gif
View or download PDF
(critical habitat map)
Peninsular Bighorn Sheep, a Distinct
Population Segment of Desert Bighorn
Sheep (Ovis canadensis nelsoni)
(1) Critical habitat units are depicted for Riverside, San Diego, and Imperial Counties, California, on the maps
below.
(2) The primary constituent elements of critical habitat for the Peninsular bighorn sheep are:
(i) Moderate to steep, open slopes (20 to 60 percent) and canyons, with canopy cover of 30 percent or less (below
4,600 ft (1,402 m) elevation in Peninsular Ranges) that provide space for sheltering, predator detection, rearing of
young, foraging and watering, mating, and movement within and between ewe groups;
(ii) Presence of a variety of forage plants, indicated by the presence of shrubs
(e.g., Ambrosia spp., Caesalpiniaspp., Hyptis spp., Sphaeralcea spp., Simmondsia spp.), that provide a primary
food source year round, grasses (e.g., Aristida spp., Bromus spp.) and cacti (e.g., Opuntia spp.) that provide a
source of forage in the fall, and forbs (e.g., Plantago spp., Ditaxis spp.) that provide a source of forage in the
spring;
(iii) Steep, rugged slopes (60 percent slope or greater) (below 4,600 ft (1,402 m) elevation in Peninsular Ranges)
that provide secluded space for lambing and terrain for predator evasion;
(iv) Alluvial fans, washes, and valley bottoms that provide important foraging areas where nutritious and digestible
plants can be more readily found during times of drought and lactation, and that provide and maintain habitat
connectivity by serving as travel routes between and within ewe groups, adjacent mountain ranges, and important
resource areas (e.g., foraging areas and escape terrain); and
(v) Intermittent and permanent water sources that are available during extended dry periods and provide relatively
nutritious plants and drinking water.
(3) Critical habitat does not include manmade structures (such as buildings, aqueducts, roads, and other paved
areas) and the land on which they are located existing within the legal boundaries on the effective date of this rule.
(4) Critical habitat map units. Data layers defining map units were created on a base of USGS 1:24,000 maps, and
critical habitat units were then mapped using Universal Transverse Mercator (UTM) coordinates.
(5) Note: Index map of critical habitat units for the Peninsular bighorn sheep follows:
eCFR graphic er14ap09.000.gif
View or download PDF
(6) Unit 1: San Jacinto Mountains, Riverside County, California.
(i) [Reserved]
(ii) Map of Unit 1, San Jacinto Mountains (Map 2) follows:
eCFR graphic er14ap09.001.gif
View or download PDF
(7) Unit 2A: North Santa Rosa Mountains, Riverside County, California.
(i) [Reserved]
(ii) Map of Unit 2A, North Santa Rosa Mountains follows:
eCFR graphic er14ap09.002.gif
View or download PDF
(8) Unit 2B: South Santa Rosa Mountains south to Vallecito Mountains, Riverside, San Diego, and Imperial
Counties, California.
(i) [Reserved]
(ii) Map of Unit 2B, South Santa Rosa Mountains south to Vallecito Mountains follows:
eCFR graphic er14ap09.003.gif
View or download PDF
(9) Unit 3: Carrizo Canyon, San Diego and Imperial Counties, California.
(i) [Reserved]
(ii) Map of Unit 3, Carrizo Canyon follows:
eCFR graphic er14ap09.004.gif
View or download PDF
Sierra Nevada Bighorn Sheep (Ovis
canadensis sierrae)
(1) Critical habitat units are depicted for Mono, Fresno, Inyo, Tulare, and Tuolumne Counties, California, on the
maps below.
(2) The primary constituent elements of critical habitat for the Sierra Nevada bighorn sheep are the habitat
components that provide:
(i) Non-forested habitats or forest openings within the Sierra Nevada from 4,000 ft (1,219 m) to 14,500 ft (4,420 m)
in elevation with steep (greater than or equal to 60 percent slope), rocky slopes that provide for foraging, mating,
lambing, predator avoidance, and bedding and that allow for seasonal elevational movements between these
areas.
(ii) Presence of a variety of forage plants as indicated by the presence of grasses
(e.g., Achnanthera spp.; Elymusspp.) and browse (e.g., Ribes spp.; Artemisia spp., Purshia spp.) in winter, and
grasses, browse, sedges (e.g., Carex spp.) and forbs (e.g., Eriogonum spp.) in summer.
(iii) Presence of granite outcroppings containing minerals such as sodium, calcium, iron, and phosphorus that
could be used as mineral licks in order to meet nutritional needs.
(3) Critical habitat does not include manmade structures, such as buildings, aqueducts, airports, roads, and other
paved areas, and the land on which they are located, existing on the effective date of this rule and not containing
one or more of the primary constituent elements.
(4) Critical Habitat Map Units—Boundaries of designated critical habitat were derived from Sierra Nevada Bighorn
Sheep Herd Units developed by the California Department of Fish and Game for the final Sierra Nevada Bighorn
Sheep recovery plan. The designated critical habitat unit boundaries differ from Sierra Nevada bighorn sheep Herd
Unit polygons by the removal of developed areas and private parcels that are unlikely to contain the primary
constituent elements. The data were projected to Universal Transverse Mercator (UTM), zone 11, on the North
American Datum of 1983.
(5) Note: Index map of Sierra Nevada bighorn sheep critical habitat follows:
eCFR graphic er05au08.000.gif
View or download PDF
(6) Unit 1 (Mount Warren); Mono and Tuolumne Counties, California.
(i) Unit 1 is shown on the map in paragraph (6)(ii) of this entry, excluding land bounded by 304870, 4211718;
304755, 4211663; 304590, 4211666; 304426, 4211699; 304273, 4211615; 304237, 4211614; 304100, 4211575;
304119, 4211576; 304068, 4211562; 304036, 4211567; 303925, 4211593; 303824, 4211552; 303714, 4211495;
303668, 4211501; 303558, 4211486; 303473, 4211423; 303421, 4211366; 303381, 4211308; 303223, 4211322;
303176, 4211295; 303181, 4211202; 303103, 4211161; 303208, 4210962; 303418, 4211073; 303481, 4211022;
303500, 4211020; 303617, 4211098; 303675, 4211109; 303894, 4211096; 303983, 4211127; 304053, 4211125;
304053, 4211124; 304106, 4211121; 304460, 4211207; 304518, 4211250; 304590, 4211261; 304644, 4211303;
304747, 4211336; 304863, 4211395; 304882, 4211457; 305018, 4211524; 305128, 4211543; 305289, 4211677;
305397, 4211739; 305477, 4211807; 305515, 4211863; 305405, 4211903; 305374, 4211907; 305176, 4211813;
305029, 4211770; returning to 304870, 4211718.
(ii) Map of Unit 1 Mount Warren for Sierra Nevada bighorn sheep follows:
eCFR graphic er05au08.001.gif
View or download PDF
(7) Unit 2 (Mount Gibbs); Mono and Tuolumne Counties, California.
(i) [Reserved]
(ii) Map of Unit 2 (Mount Gibbs) for Sierra Nevada bighorn sheep follows:
eCFR graphic er05au08.002.gif
View or download PDF
(8) Unit 3 (Convict Creek); Fresno and Mono Counties, California.
(i) [Reserved]
(ii) Map of Unit 3 (Convict Creek) for Sierra Nevada bighorn sheep follows:
eCFR graphic er05au08.003.gif
View or download PDF
(9) Unit 4 (Wheeler Ridge); Fresno, Inyo and Mono Counties, California.
(i) Unit 4 is shown on the map in paragraph (9)(ii) of this entry, excluding
(A) Land bounded by 352666, 4139452; 352330, 4139197; 352261, 4139018; 352280, 4139004; 352300,
4138988; 352332, 4138964; 352634, 4139235; 352732, 4139417; 352718, 4139424; 352718, 4139425; 352694,
4139437; 352694, 4139437; 352690, 4139439; 352687, 4139441; 352687, 4139441; returning to 352666,
4139452;
(B) Land bounded by 350254, 4136280; 350216, 4136187; 350216, 4136187; 350178, 4136094; 350363,
4136018; 350402, 4136111; 350402, 4136111; 350440, 4136204; 350478, 4136296; 350305, 4136368; 350300,
4136361; 350295, 4136351; 350293, 4136348; 350287, 4136341; 350283, 4136338; 350280, 4136335; 350276,
4136333; 350276, 4136333; returning to 350254, 4136280; and
(C) Land bounded by 349527, 4136002; 349500, 4136201; 349450, 4136194; 349408, 4136200; 349404,
4136201; 349391, 4136206; 349321, 4136238; 349317, 4136223; 349126, 4136278; 349099, 4136181; 349045,
4135990; 349139, 4135963; 349138, 4135962; 349235, 4135934; 349212, 4135851; 349308, 4135823; 349406,
4135799; 349478, 4135988; 349478, 4135995; returning to 349527, 4136002.
(ii) Map of Unit 4 (Wheeler Ridge) for Sierra Nevada bighorn sheep follows:
eCFR graphic er05au08.004.gif
View or download PDF
(10) Unit 5 (Taboose Creek); Fresno and Inyo Counties, California.
(i) [Reserved]
(ii) Map of Unit 5 (Taboose Creek) for Sierra Nevada bighorn sheep follows:
eCFR graphic er05au08.005.gif
View or download PDF
(11) Unit 6 (Sawmill Canyon); Fresno and Inyo Counties, California.
(i) [Reserved]
(ii) Map of Unit 6 (Sawmill Canyon) for Sierra Nevada bighorn sheep follows:
eCFR graphic er05au08.006.gif
View or download PDF
(12) Unit 7 (Mount Baxter); Fresno and Inyo Counties, California.
(i) [Reserved]
(ii) Map of Unit 7 (Mount Baxter) for Sierra Nevada bighorn sheep follows:
eCFR graphic er05au08.007.gif
View or download PDF
(13) Unit 8 (Mount Williamson); Inyo and Tulare Counties, California.
(i) [Reserved]
(ii) Map of Unit 8 (Mount Williamson) for Sierra Nevada bighorn sheep follows:
eCFR graphic er05au08.008.gif
View or download PDF
(14) Unit 9 (Big Arroyo); Tulare County, California.
(i) [Reserved]
(ii) Map of Unit 9 (Big Arroyo) for Sierra Nevada bighorn sheep follows:
eCFR graphic er05au08.009.gif
View or download PDF
(15) Unit 10 (Mount Langley); Inyo and Tulare Counties, California.
(i) [Reserved]
(ii) Map of Unit 10 (Mount Langley) for Sierra Nevada bighorn sheep follows:
eCFR graphic er05au08.010.gif
View or download PDF
(16) Unit 11 (Laurel Creek); Tulare County, California.
(i) [Reserved]
(ii) Map of Unit 11 (Laurel Creek) for Sierra Nevada bighorn sheep follows:
eCFR graphic er05au08.011.gif
View or download PDF
(17) Unit 12 (Olancha Peak); Inyo and Tulare Counties, California.
(i) [Reserved]
(ii) Map of Unit 12 (Olancha Peak) for Sierra Nevada bighorn sheep follows:
eCFR graphic er05au08.012.gif
View or download PDF
Buena Vista Lake Shrew (Sorex ornatus
relictus)
(1) Critical habitat units are depicted for Kings and Kern Counties, California, on the maps below.
(2) Within these areas, the primary constituent elements of the physical or biological features essential to the
conservation of the Buena Vista Lake shrew consist of permanent and intermittent riparian or wetland communities
that contain:
(i) A complex vegetative structure with a thick cover of leaf litter or dense mats of low-lying vegetation. Associated
plant species can include, but are not limited to, Fremont cottonwoods, willows, glasswort, wild-rye grass, and rush
grass. Although moist soil in areas with an overstory of willows or cottonwoods appears to be favored, such
overstory may not be essential.
(ii) Suitable moisture supplied by a shallow water table, irrigation, or proximity to permanent or semipermanent
water.
(iii) A consistent and diverse supply of prey. Although the specific prey species used by the Buena Vista Lake
shrew have not been identified, ornate shrews are known to eat a variety of terrestrial and aquatic invertebrates,
including amphipods, slugs, and insects.
(3) Critical habitat does not include manmade structures (such as buildings, aqueducts, runways, roads, and other
paved areas) and the land on which they are located existing within the legal boundaries on the effective date of
this rule.
(4) Critical habitat map units. Data layers defining map units were created on a base of USGS 7.5′ quadrangles,
and critical habitat units were then mapped using Universal Transverse Mercator (UTM) coordinates. The maps in
this entry, as modified by any accompanying regulatory text, establish the boundaries of the critical habitat
designation. The coordinates or plot points or both on which each map is based are available to the public
at http://criticalhabitat.fws.gov/crithab/, and at http://www.regulations.gov at Docket No. FWS-R8-ES-2009-0062,
and at the field office responsible for this designation. You may obtain field office location information by contacting
one of our regional offices, the addresses of which are listed at 50 CFR 2.2.
(5) Index map of Buena Vista Lake shrew critical habitat units follows:
eCFR graphic er02jy13.002.gif
View or download PDF
(6) Unit 1: Kern National Wildlife Refuge Unit, Kern County, California. Note: Map of Unit 1, Kern National Wildlife
Refuge Unit, follows:
eCFR graphic er02jy13.003.gif
View or download PDF
(7) Unit 2: Goose Lake Unit, Kern County, California. Note: Map of Unit 2, Goose Lake Unit, follows:
eCFR graphic er02jy13.004.gif
View or download PDF
(8) Unit 4: Coles Levee Unit, Kern County, California. Note: Map of Unit 4, Coles Levee Unit, follows:
eCFR graphic er02jy13.005.gif
View or download PDF
(9) Unit 5: Kern Lake Unit, Kern County, California. Note: Map of Unit 5, Kern Lake Unit, follows:
eCFR graphic er02jy13.006.gif
View or download PDF
(10) Unit 6: Semitropic Ecological Reserve Unit, Kern County, California. Note: Map of Unit 6, Semitropic
Ecological Reserve Unit, follows:
eCFR graphic er02jy13.007.gif
View or download PDF
(11) Unit 7: Lemoore Wetland Reserve Unit, Kings County, California. Note: Map of Unit 7, Lemoore Wetland
Reserve Unit, follows:
eCFR graphic er02jy13.008.gif
View or download PDF
Mount Graham Red Squirrel (Tamiasciurus
hudsonicus grahamensis)
Arizona. Areas of land, water, and airspace in the Coronado National Forest, T. 8 S., R. 24 E., and T. 9 S., R. 24 E.
(Gila and Salt River Meridian), Graham County, with the following components:
1. Hawk Peak-Mount Graham Area. The area above the 10,000-foot (3,048-meter) contour surrounding Hawk
Peak and Plain View Peak, plus the area above the 9,800-foot (2,987-meter) contour that is south of lines
extending from the highest point of Plain View Peak eastward at 90° (from true north) and southwestward at 225°
(from true north).
2. Heliograph Peak Area. The area on the north-facing slope of Heliograph Peak that is above the 9,200-foot
(2,804-meter) contour surrounding Heliograph Peak and that is between a line extending at 15° (from true north)
from a point 160 feet (49 meters) due south of the horizontal control station on Heliograph Peak and a line
extending northwestward at 300° (from true north) from that same point.
3. Webb Peak Area. The area on the east-facing slope of Webb Peak that is above the 9,700-foot (2,957-meter)
contour surrounding Webb Peak and that is east of a line extending due north and south through a point 160 feet
(49 meters) due west of the horizontal control station on Webb Peak.
The major constituent element is dense stands of mature spruce-fir forest.
Note: The map provided is for informational purposes only. Map follows:
eCFR graphic ec01jn91.019.gif
View or download PDF
Amargosa Vole (Microtus californicus
scirpensis)
California. Marshes and associated land and water in the following areas of Inyo County (San Bernardino
Meridian): T20N R7E Sec. 4, 5, N 1⁄2 and SE 1⁄4 Sec. 9, NW 1⁄4 Sec. 10, SW 1⁄4 SW 1⁄4 Sec. 15, E 1⁄2 Sec. 16,
NW 1⁄4 Sec. 22; T21N R7E S 1⁄2 Sec. 28, S 1⁄2 and NW 1⁄4 Sec. 29, Sec. 32, 33.
Within these areas, the major constituent elements that are known to require special management considerations
or protection are marsh vegetation (primarily bulrushes of the genus Scirpus), springs, and some open water along
the Amargosa River, which provide escape cover and an adequate food supply.
Note: The map provided is for informational purposes only. Map follows:
eCFR graphic ec01jn91.020.gif
View or download PDF
Gray Wolf (Canis lupus)
Michigan. Isle Royale National Park.
Minnesota. Areas of land, water, and airspace in Beltrami, Cook, Itasca, Koochiching, Lake, Lake of the Woods,
Roseau, and St. Louis Counties, with boundaries (4th and 5th Principal meridians) identical to those of zones 1, 2,
and 3, as delineated in §17.40(d)(l).
[42 FR 47840, Sept. 22, 1977]
Editorial Notes: 1. For Federal Register citations affecting §17.95, see the List of CFR Sections Affected, which
appears in the Finding Aids section of the printed volume and at www.govinfo.gov.
2. The remainder of §17.95 appears in 50 Part 17, §17.95(b), 50 Part 17, §17.95(c) to §17.95(e), and 50 Part 17,
§17.95(f) to end of §17.95.
| File Type | application/pdf |
| File Modified | 0000-00-00 |
| File Created | 0000-00-00 |