Supporting Statement for an Information Collection Request (ICR)
Under the Paperwork Reduction Act (PRA)
Title: Asbestos Part 1: Chrysotile Asbestos; Regulation of Certain Conditions of Use Under the Toxic Substances Control Act (TSCA) (Final Rule; RIN 2070-AK86)
EPA ICR No.: 2707.02
OMB Control No.: 2070-0220
Docket ID No.: EPA-HQ-OPPT-2021-0057
The Environmental Protection Agency (EPA) is promulgating a rule to address unreasonable risks to human health from chrysotile asbestos under section 6 of the Toxic Substances Control Act (TSCA). The rule prohibits certain uses of chrysotile asbestos. It also requires each person who disposes of chrysotile asbestos or any chrysotile asbestos-containing products or articles related to those uses to adhere to requirements described in the OSHA Asbestos General Standard at 29 CFR 1910.1001(k) (or the OSHA Safety and Health Regulations for Construction Standard at 29 CFR 1926.1101 for sheet gaskets for chemical production) regarding asbestos waste disposal. Additionally, EPA is cross-referencing the disposal requirements of Asbestos National Emission Standards for Hazardous Air Pollutants (NESHAP) (40 CFR Part 61, Subpart M) at 40 CFR section 61.150 for the following conditions of use: chrysotile asbestos diaphragm for use in chlor-alkali facilities; oilfield brake blocks; other vehicle friction products; and any non-consumer use of other gaskets and aftermarket automotive brakes and linings. The rule also requires each person who disposes of chrysotile asbestos or any chrysotile asbestos-containing products or articles subject to the rule to retain at the headquarters of the company, or at the facility for which the records were generated, documentation showing compliance with the disposal requirements as well as any documentation, such as invoices or bills of lading, related to compliance with the prohibitions in the rule.
Chlor-alkali plants using asbestos diaphragms and titanium dioxide producers using asbestos sheet gasket are required to develop information about exposures and plans to control exposures, and to disclose this information to potentially exposed persons.
EPA is promulgating this rule under section 6(a) of TSCA in response to a finding that chrysotile asbestos presents an unreasonable risk to human health when used in certain ways. The portions of the rule that trigger this Information Collection Request (ICR) are the third-party disclosure and recordkeeping requirement. The records must be retained for 5 years from the date of generation.
Summary Total Burden and Costs
Activity |
Number of Responses |
Responses per Respondent |
Average Annual Burden per Response |
Average Annual Total Labor Burden |
Average Annual Total Labor Costs |
Average Annual Total Non-Labor Costs |
Average Annual Total Costs |
IC #1: Exposure control plan |
12 |
1 |
1.33 |
16 |
$1,141 |
- |
$1,141 |
IC #2: Exposure monitoring |
12 |
1 |
162.95 |
1,955 |
$112,118 |
$233,425 |
$345,544 |
IC #3: Exposure notification and recordkeeping |
12 |
1 |
18.69 |
224 |
$21,247 |
- |
$21,247 |
IC #4: Disposal recordkeeping (midpoint of range) |
712 |
1 |
0.10 |
73 |
$3,041 |
- |
$3,041 |
Total (midpoint of range) |
721 |
1 |
3.1 |
2,269 |
$137,547 |
$233,425 |
$370,973 |
Agency |
- |
- |
- |
- |
- |
- |
- |
The Environmental Protection Agency (EPA) is promulgating a rule under section 6 of the Toxic Substances Control Act (TSCA) to address unreasonable risk of injury to health it has identified for certain uses of chrysotile asbestos following completion of the Risk Evaluation for Asbestos, Part 1: Chrysotile Asbestos. While chrysotile asbestos is used primarily in the chlor-alkali industry, EPA is also addressing other identified categories of use. EPA has determined that chrysotile asbestos presents an unreasonable risks of injury to health for the following conditions of use: processing and industrial use of chrysotile asbestos diaphragms in the chlor-alkali industry; processing and industrial use of chrysotile asbestos-containing sheet gaskets in chemical production; industrial use and disposal of chrysotile asbestos-containing brake blocks in the oil industry; commercial use, consumer use, and disposal of aftermarket automotive chrysotile asbestos-containing brakes/linings; commercial use and disposal of other chrysotile asbestos-containing vehicle friction products, excluding for use on the NASA Super Guppy; commercial use, consumer use, and disposal of other asbestos-containing gaskets. To address these unreasonable risks, EPA is prohibiting manufacture (import), processing, distribution-in-commerce and commercial use of chrysotile asbestos, including products or articles containing chrysotile asbestos, pursuant to TSCA section 6(d)(1). EPA is also promulgating disposal and recordkeeping requirements for these conditions of use, as well as interim workplace controls for chrysotile asbestos diaphragms in the chlor-alkali industry, and chrysotile asbestos-containing sheet gaskets in chemical production.
Legal authority: The Toxic Substances Control Act (TSCA), 15 U.S.C. § 2605(a).
Respondents/affected entities: Entities potentially affected by this ICR include persons that manufacture, process, or distributes in commerce chrysotile asbestos or products or articles containing chrysotile asbestos.
Respondent’s obligation to respond: Respondents are not obligated to respond or report to EPA. However, they are required to retain records, and to develop information and disclose it to potentially exposed persons.
Confidentiality of responses: Not applicable.
Estimated total number of potential respondents: 721
Frequency of response: On occasion/as necessary
Estimated total annual burden: 2,269 hours. Burden is defined at 5 CFR 1320.3(b).
Estimated total annual costs: $370,973
Changes in the estimate: Not applicable. This is a request for a new OMB Control Number.
Under section 6(a) of TSCA (15 U.S.C. § 2605(a)), if EPA determines after risk evaluation that a chemical substance presents an unreasonable risk of injury to health or the environment, without consideration of costs or other non-risk factors, including an unreasonable risk to a potentially exposed or susceptible subpopulation identified as relevant to the risk evaluation, under the conditions of use, EPA must by rule apply one or more requirements to the extent necessary so that the chemical substance or mixture no longer presents such risk. Section 6(a) authorizes EPA to:
Prohibit or restrict manufacture, processing, or distribution in commerce,
Prohibit or restrict the manufacture, processing, or distribution in commerce of the chemical substance above a specified concentration,
Require minimum warnings or instructions with respect to use, distribution, or disposal,
Require manufacturers or processors to make and retain records,
Prohibit or regulate any manner of commercial use,
Prohibit or regulate any manner of disposal, and/or
Require manufacturers or processors to give notice of the unreasonable risk of injury, and to recall products if required.
This rule:
Prohibits the manufacturing (import) of chrysotile asbestos for diaphragms in the chlor-alkali industry after 60 days.
Prohibits the processing, distribution in commerce and commercial use of chrysotile asbestos for diaphragms in the chlor-alkali industry after 5 years, but allows a person converting multiple facilities to membrane technology to continue these activities at a second facility for 8 years and at a third facility for 12 years, if they certify that certain conditions are met.
Prohibits the manufacture, processing, distribution in commerce and industrial use of sheet gaskets in chemical production facilities after 2 years; except for chemical production facilities manufacturing titanium dioxide or processing nuclear materials, where the industrial use of sheet gaskets is prohibited after 5 years (provided that persons processing nuclear materials have in place exposure controls).
Requires interim workplace controls (including developing an exposure control plan, conducting exposure monitoring, and notifying potentially exposed persons of the monitoring results) for diaphragms in the chlor-alkali industry and chemical production facilities using sheet gaskets to manufacture titanium dioxide.
Prohibits all persons from manufacturing, processing, distributing in commerce, and commercial use of chrysotile asbestos after 180 days from the effective date of this rule for the following conditions of use:
Industrial use and disposal of oilfield brake blocks.
Commercial and consumer use and disposal of aftermarket automotive brakes and linings.
Commercial use and disposal of other vehicle friction products, excluding brake system components used on the NASA “Super-Guppy” Turbine (SGT) aircraft.
Commercial and consumer use and disposal of other gaskets.
Requires persons who dispose of any chrysotile asbestos and any chrysotile asbestos-containing products or articles subject to the disposal provisions to retain any records generated pursuant to, or otherwise documenting compliance with specified disposal regulations. These records must be retained in one location at the headquarters of the company, or at the facility for which the records were generated, and they must be retained for five years from the date of generation.
Requires that disposal adhere to requirements described in the OSHA Asbestos General Standard in 29 CFR 1910.1001(k) (or the OSHA Safety and Health Regulations for Construction Standard at 29 CFR 1926.1101 for sheet gaskets for chemical production) regarding asbestos waste disposal. Additionally, for the chrysotile asbestos diaphragm condition of use, as well as oilfield brake blocks, other vehicle friction products, and any non-consumer use of other gaskets and aftermarket automotive brakes and linings, the rule cross-references the disposal requirements of Asbestos National Emission Standards for Hazardous Air Pollutants (NESHAP) (40 CFR Part 61, Subpart M) at 40 CFR section 61.150.
EPA. This information collection will provide EPA with information only upon inspection of such materials. There are no reporting requirements to submit information to EPA under this information collection activity.
Regulated Entities. The regulated entities will compile and retain records that are necessary as a reference for EPA. These records demonstrate that regulated entities are in compliance with the requirements in this rule, including general provisions, certification of compliance, interim workplace controls, and disposal requirements. Compliance with the rule is required to mitigate the unreasonable risks to human health identified in EPA’s risk evaluation for chrysotile asbestos. These recordkeeping requirements are also necessary to permit the EPA to conduct its enforcement activities and to ensure compliance within the regulated community.
There will be no information collection by EPA. Therefore, there is no need for any technological facilitation under the rule related to the information collection activities. The recordkeeping requirement does not specify a particular technology or method of retaining the required information.
EPA’s information collection pursuant to the TSCA section 6(a) regulations does not duplicate any other collection. There is no other Federal program that requires the information collection activities related to the prohibitions and disposal requirements under the rule.
The information collection activities covered by this ICR are necessary in order to enhance the mitigation of unreasonable risks identified in certain uses of chrysotile asbestos. Due to EPA’s finding that chrysotile asbestos presents an unreasonable health risk under the specified conditions of use, EPA is promulgating a rule that involves information collection activities that mitigate the unreasonable health risks and do not present unreasonable burdens to the regulated entities. Such records are necessary for effective enforcement of the section 6 rule. Due to the nature of the triggering events that initiate information collection activities under the rule, less frequent collection is not feasible. The rule does not require reporting information to EPA.
This rulemaking and information collection activity will require that regulated entities retain records for a duration of 5 years. EPA has tailored this timeframe to coincide with the statute of limitations for civil penalty enforcement (28 U.S.C. 2842). Though EPA does not require that regulated entities retain their records for 30 years as OSHA does in their asbestos standards, EPA expects that 5-year retention of records is necessary for effective implementation and enforcement of this rulemaking.
The proposed rule was published on April 12, 2022 (87 FR 21706). See https://www.govinfo.gov/content/pkg/FR-2022-04-12/pdf/2022-07601.pdf. The request for comments on the information collection was at 87 FR 21734. EPA did not receive comments on the cost or hour burden of the information collection.
While not specifically commenting on the information collection, one commenter (EPA-HQ-OPPT-2021-0057-0497) claimed that EPA’s Existing Chemical Exposure Limit (ECEL) value of 0.005 f/cc is an order of magnitude below the limit of quantification, and that setting threshold values at or below the limit of quantification will not yield information that has any practical utility because the data will likely fail validation tests. The commenter stated that the practicability of measuring below the proposed action level (0.0025 f/cc) will obviously present even more significant challenges.
EPA disagrees that the ECEL value is below the limit of quantification. While there may be practical sampling and analytical challenges measuring to the ECEL, EPA has concluded that monitoring at the ECEL level is feasible based on current analytical methods. EPA believes that current analytical methods and modern air sampling equipment allow for air monitoring with a detection limit that allows for comparison with the ECEL level. This is demonstrated by the personal air monitoring data submitted to EPA by the chlor-alkali industry. However, for instances in which a sufficient limit of detection cannot be reached for comparison to the ECEL, owners and operators may elect to use an alternative lowest concentration possible as their basis for the selection of the respirators, and use an increased respiratory protection with an appropriate assigned protection factor (APF) to demonstrate compliance with the ECEL as an interim control measure. For example, if the lowest concentration an owner or operator can measure is 0.1 f/cc, then, they should assume that the measured exposure concentration is above 0.05 f/cc and less than or equal to 0.125 f/cc or 25 times the ECEL, and provide a loose fitting facepiece supplied-air respirator (SAR) or airline respirator in continuous flow mode. (However, after public comments regarding the difficulties of measuring asbestos at the proposed action level, EPA has decided not to finalize an ECEL-action level in the final rule.) Therefore, EPA does not agree that the information collected under this rule lacks practical utility.
This collection does not provide any payment or gift to respondents.
EPA will not be collecting any information. Therefore, confidential information will not be submitted to EPA.
The information collection activities do not include questions of a sensitive nature.
The respondents, the information collection activities and related estimates for burden and costs related with those activities are described below for each respondent category. EPA’s Economic Analysis of the TSCA Section 6 Final Rule for Asbestos Risk Management, Part 1 (U.S. EPA, 2024) provides the detailed methodology for estimating the number of respondents, burden, and cost for the information collection activities that are summarized here. The information collection activities that may generate additional burden and cost include:
Interim Workplace Controls: Chlor-alkali plants using asbestos diaphragms and titanium dioxide producers using asbestos sheet gasket are required to develop exposure control plans; monitor exposure levels; maintain records of monitoring; provide potentially exposed persons with information about how they can access the exposure control plans, exposure monitoring records, PPE program implementation documentation, and respirator program documentation; and obtain an acknowledgment from potentially exposed persons that they have received the information. The respondents are also required to retain records of these activities and make them available to EPA for inspection. This analysis does not account for the fact that some respondents may already be engaging in at least some of these activities, so the actual burden and cost may be less than estimated here.
Disposal Recordkeeping: Companies that manufacture (including import), process, distribute in commerce or use chrysotile asbestos are required to retain records related to the disposal of chrysotile asbestos or chrysotile asbestos-containing products or articles. Not all companies may be retaining such records in the absence of this requirement.
There are no forms or other required instruments for any of the information collection activities required by the rule. This rule requires entities to retain records for five years but does not require reporting information to EPA. However, persons subject to the rule must make the records that must be maintained under the rule available to EPA for inspection.
All persons who manufacture (including import), process, or distribute in commerce or engage in commercial use of chrysotile asbestos are required by 40 CFR 751.515 to retain ordinary business records, such as invoices and bills-of-lading related to compliance with the prohibitions, and other restrictions related to chrysotile asbestos. EPA expects that firms already retain such records as part of their customary business practices. Therefore, the burden and cost of keeping ordinary business records are not included in these estimates.
While 40 CFR 751.515 requires chlor-alkali facilities to submit a certification of compliance to EPA if they will be using asbestos diaphragms between 5 and 12 years after the effective date of the final rule, these reporting requirements are not included here because they will not be incurred within the next three years of the program covered by this ICR. However, they will be included in future ICR renewals for this rule.1 Since there are no agency information collection activities during the period covered by this ICR, no costs to the Federal government are estimated.
The table below presents the labor rates used to estimate the costs of the labor burdens under the ICR.
Industry Wage Rates (2022$) |
||||||||
Labor Category |
Data Series |
Date |
Wage ($/hour) |
Fringe Benefit |
Total Compen-sation |
Overhead as % of Total Compen-sation1 |
Overhead |
Hourly Loaded Wages |
(a) |
(b) |
(c) =(b)+(a) |
(d) |
(e)=(c)*(d) |
(f)=(c)+(e) |
|||
Manufacturing – Managerial |
BLS ECEC, Private Manufacturing industries, “Mgt, Business, and Financial” 2 |
Dec-22 |
$54.29 |
$24.66 |
$78.95 |
20% |
$15.79 |
$94.74 |
Manufacturing – Professional / Technical |
BLS ECEC, Private Manufacturing industries, “Professional and related“2 |
Dec-22 |
$46.01 |
$23.27 |
$69.28 |
20% |
$13.86 |
$83.14 |
Manufacturing - Clerical |
BLS ECEC, Private Manufacturing industries, “Office and Administrative Support” 2 |
Dec-22 |
$23.11 |
$10.33 |
$33.44 |
20% |
$6.69 |
$40.13 |
Manufacturing - Production |
BLS ECEC, Private Manufacturing Industries, “Production occupations”2 |
Dec-22 |
$21.79 |
$11.63 |
$33.42 |
20% |
$6.68 |
$40.10 |
Certified Industrial Hygienist4 |
BLS OES, Occupational Health & Safety Specialists (19-5011)3 |
May-22 |
$39.47 |
$19.96 |
$59.43 |
20% |
$11.89 |
$71.32 |
Technical Specialist4 |
BLS OES, Occupational Health & Safety Technicians (19-5012) 3 |
May-22 |
$30.40 |
$15.38 |
$45.78 |
20% |
$9.16 |
$54.94 |
Maintenance and repair |
BLS ECEC, Service Industries, “Installation, maintenance, and repair"2 |
Dec-22 |
$28.39 |
$13.15 |
$41.54 |
20% |
$8.31 |
$49.85 |
1 An overhead rate of 20% is used based on assumptions in the U.S. Environmental Protection Agency’s Handbook on Valuing Changes in Time Use Induced by Regulatory Requirements and Other U.S. EPA Actions. 2 Source: U.S. Bureau of Labor Statistics, Employer Costs for Employee Compensation December 2022. 3 Source: U.S. Bureau of Labor Statistics, Occupational Employment Statistics (Occupational Employment and Wages) for May 2022. 4 Fringe benefits are not reported in the BLS Occupational Employment and Wages). It is therefore assumed that fringes as a percentage of wages are 50.57%, based on the percentage for Private Manufacturing Industries, “Professional and related” in the BLS Employer Costs for Employee Compensation. |
IC #1: Exposure control plan
40 CFR 751.509 requires persons subject to the ECEL requirements at 40 CFR 751.511 to establish a plan to reduce exposures to all potentially exposed persons to below the ECEL. For the purpose of calculating burden and cost, facilities are assumed to prepare an exposure control plan but not to need to update it during the 3-year period covered by this information collection request. There are 4 titanium dioxide plants using asbestos sheet gaskets and 8 chlor-alkali plants using asbestos diaphragms that are estimated to respond for this activity. None of the respondents are small businesses.
IC #1: Establish Exposure Control Plan |
|||||
Activity |
Respondents |
Responses |
Average Burden per Response (hours) |
Total Annualized Burden (hours) |
Total Labor Cost |
Exposure control plan |
12 |
12 |
1.33 |
16 |
$1,141 |
IC #2: Periodic Exposure Monitoring
40 CFR 751.509 requires persons subject to the ECEL requirements at 40 CFR 751.511 to conduct periodic exposure monitoring. This involves labor time to design the sampling plan, prepare for the sampling, collect and manage the samples, and prepare a written report documenting the results. There are 4 titanium dioxide plants using asbestos sheet gaskets and 8 chlor-alkali plants using asbestos diaphragms that are estimated to respond for this activity. None of the respondents are small businesses.
IC #2: Labor Burden and Cost for Periodic Exposure Monitoring |
|||||
Activity |
Respondents |
Responses |
Average Burden per Response (hours) |
Total Annualized Burden (hours) |
Total Labor Cost |
Exposure monitoring |
12 |
12 |
162.95 |
1,955 |
$112,118 |
IC #3: Exposure Monitoring Notification and Recordkeeping
40 CFR 751.509 requires persons subject to the ECEL requirements at 40 CFR 751.511 to notify potentially exposed workers of the exposure monitoring results; provide them with access to exposure control plans, exposure monitoring records, PPE program implementation documentation, and respirator program documentation; and obtain an acknowledgment that potentially exposed workers have received this information. 40 CFR 751.515 requires that such persons retain these records and make them available to EPA for inspection. There are 4 titanium dioxide plants using asbestos sheet gaskets and 8 chlor-alkali plants using asbestos diaphragms that are estimated to respond for this activity. None of the respondents are small businesses.
IC #3: Exposure Monitoring Notification and Recordkeeping |
|||||
Activity |
Respondents |
Responses |
Average Burden per Response (hours) |
Total Annualized Burden (hours) |
Total Labor Cost |
Exposure notification (third-party disclosure) |
12 |
12 |
17 |
203 |
$19,276 |
Exposure recordkeeping |
12 |
12 |
1.7 |
21 |
$1,971 |
Total exposure notification and recordkeeping |
12 |
12 |
18.7 |
224 |
$21,247 |
IC #4: Disposal Recordkeeping
40 CFR 751.515 requires that companies that manufacture (import), process, distribute in commerce or use chrysotile asbestos must retain information related to the disposal of chrysotile asbestos and chrysotile asbestos-containing products or articles at the company headquarters for five years. These information collection activities are necessary to provide EPA with information upon inspection. Not all entities subject to the requirements will incur burden or costs from these activities because they may already be meeting the requirements as part of their usual business practices.
Firms using sheet gasket for chemical production (except for those used for nuclear material processing) and firms replacing aftermarket automotive brakes are not assumed to maintain such records as an ordinary business practice, and will thus incur recordkeeping burdens and costs associated with documenting their disposal activities. It is unknown whether firms disposing of asbestos oilfield brake blocks, other vehicle friction products, or other gaskets maintain the necessary records as an ordinary business practice. Firms in other use categories subject to the rule are assumed to maintain the necessary information as part of their ordinary business records, and thus will not incur additional recordkeeping burdens and costs due to the rule.
IC-#4 presents a range for number of respondents based on two different scenarios (the average estimate and the upper bound estimate) considered in the rulemaking’s economic analysis for the number of asbestos aftermarket automotive brakes firms that will be affected. Since the burden and cost of the recordkeeping requirements are proportional to the number of asbestos brakes replaced, the two scenarios affect the estimated number of firms and the average burden and cost per firm, but not the total burden and cost. This is because the total number of brakes replaced and the recordkeeping cost per brake replacement are the same under both scenarios. The difference in the scenarios is in the number of firms performing asbestos brake replacements and the number of asbestos brakes replaced per firm. Thus, the average burden and cost per respondent differs between the two scenarios. Under the upper bound estimate there are a large number of firms that replace asbestos brakes (and must thus keep records), but each respondent is assumed to replace asbestos brakes on a single automobile. As a result, the burden and cost per respondent are very low since they reflect the records for a single brake change. Under the average estimate there are a small number of firms estimated to replace asbestos brakes and keep records, but each respondent is assumed to replace asbestos brakes on a larger number of automobiles. As a result, the burden and cost per respondent are higher because they reflect the records for multiple brake changes. The actual values may fall between the lower and upper bounds of the number of respondents, and therefore the midpoint is used as a summary statistic.
There are 5 users of sheet gaskets for chemical production expected to be affected (both titanium dioxide plants and other chemical production facilities), and 12 to 1,400 automotive aftermarket brake firms (so the midpoint of the range is 706 firms). The extent to which oilfield brake blocks, other vehicle friction products, or other gaskets contain asbestos is unclear. The burden and cost of recordkeeping for these use categories is included for one firm for illustrative purposes. If there are additional firms subject to the requirements, the total disposal recordkeeping costs will scale proportionally to the number of firms affected by the rule.
None of the firms using sheet gaskets are small businesses. Of the automotive aftermarket brake that may incur recordkeeping costs, 11 are small businesses under the average estimate scenario, and 1,369 are small businesses under the upper bound scenario. Thus, there are 690 small businesses affected when using the midpoint of the range.
IC #4: Disposal Recordkeeping |
|||||
Activity |
Respondents |
Responses |
Average Burden per Response (hours) |
Total Annualized Burden (hours) |
Total Labor Cost |
Disposal recordkeeping (sheet gasket users) |
5 |
5 |
4.42 |
22 |
$974 |
Disposal recordkeeping (automotive aftermarket brakes – average scenario) |
12 |
12 |
4.00 |
47 |
$1,873 |
Disposal recordkeeping (automotive aftermarket brakes –upper bound scenario) |
1,400 |
1,400 |
0.03 |
47 |
$1,873 |
Oilfield Brake Blocks1 |
1 |
1 |
4.42 |
4 |
$195 |
Other Vehicle Friction Products1 |
|||||
Other Gaskets1 |
|||||
Disposal recordkeeping (Range of all respondents) |
18 to 1,406 |
18 to 1,406 |
4.14 to 0.05 |
73 |
$3,041 |
Disposal recordkeeping (Midpoint of range) |
712 |
712 |
0.10 |
73 |
$3,041 |
1 Costs reflect incremental disposal recordkeeping costs for one firm for illustrative purposes. Disposal recordkeeping costs will scale proportionally to the number of firms affected by the rule. |
IC #2: Periodic Exposure Monitoring
40 CFR 751.509 requires persons subject to the ECEL requirements at 40 CFR 751.511 to conduct periodic exposure monitoring. This will result in non-labor costs for items such as personal pumps, a calibrated primary flow meter, tubing, sampling media, shipping samples to a laboratory, and laboratory analysis of the samples.
IC #2: Non-labor Costs for Periodic Exposure Monitoring |
|||||
Activity |
Form |
Respondents |
Responses |
Average Non-Labor Cost per Response |
Total Non-Labor Cost |
Exposure monitoring |
None |
12 |
12 |
$19,452 |
$233,425 |
There will be no agency collection activities during the period covered by this information collection request, although persons subject to the rule must make the records that must be maintained under the rule available to EPA for inspection.
This is a new, rule-related information collection. The total burden requested for this ICR is 2,269 hours per year. The total annual cost burden requested for this ICR is $370,973.
Not applicable.
Not applicable.
EPA does not request an exception to the certification of this information collection.
This collection of information is approved by OMB under the Paperwork Reduction Act, 44 U.S.C. 3501 et seq. (OMB Control No. 2070-0220). Responses to this collection of information are mandatory (40 CFR 751). An agency may not conduct or sponsor, and a person is not required to respond to, a collection of information unless it displays a currently valid OMB control number. The public reporting and recordkeeping burden for this collection of information is estimated to be 3.1 hours per response. Send comments on the Agency’s need for this information, the accuracy of the provided burden estimates and any suggested methods for minimizing respondent burden to the Information Engagement Division Director, U.S. Environmental Protection Agency (2821T), 1200 Pennsylvania Ave., NW, Washington, D.C. 20460. Include the OMB control number in any correspondence. Do not send the completed form to this address.
The attachments listed below can be found in the docket for this ICR or by using the hyperlink that is provided in the list below. The docket for this ICR is accessible electronically through http://www.regulations.gov using Docket ID Number: EPA-HQ-OPPT-2021-0057.
Ref. |
Title (hyperlink) |
1. |
Statutory Authority (15 U.S.C. 2605) |
2. |
Proposed Rule (April 12, 2022) |
1 EPA estimates respondent burden of 0.5 hours for a manager to submit each chlor-alkali certification of compliance (5 and/or 8 years after the effective date of the final rule). Each submission will incur costs currently estimated to be $47.37 in labor costs and $4.35 in non-labor costs.
Page
File Type | application/vnd.openxmlformats-officedocument.wordprocessingml.document |
File Modified | 0000-00-00 |
File Created | 2024-07-22 |