SS 0652 Part B 2013 052313

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Marine Recreational Information Program Fishing Effort Survey

OMB: 0648-0652

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SUPPORTING STATEMENT

MARINE RECREATIONAL INFORMATION PROGRAM FISHING EFFORT SURVEY

OMB CONTROL NO. 0648-0652



  1. COLLECTIONS OF INFORMATION EMPLOYING STATISTICAL METHODS


1. Describe (including a numerical estimate) the potential respondent universe and any sampling or other respondent selection method to be used. Data on the number of entities (e.g., establishments, State and local governmental units, households, or persons) in the universe and the corresponding sample are to be provided in tabular form. The tabulation must also include expected response rates for the collection as a whole. If the collection has been conducted before, provide the actual response rate achieved.


1.1. MRIP Fishing Effort Survey


The MRIP Fishing Effort Survey (MFES) is bi-monthly (wave), cross-sectional mail survey designed to estimate the total number of individuals who participate in marine recreational fishing and the total number of private boat and shore-based recreational fishing trips taken by anglers in the study states. The survey consists of two independent components; 1) the Resident Angler Survey (RAS), which estimates saltwater fishing effort by residents of coastal states, and 2) the Nonresident Angler Survey (NAS), which estimates saltwater fishing effort by residents of non-coastal states. The RAS is an address-based sample (ABS) that covers all residential addresses within the study states. The NAS is a list-based sample that covers individuals who are licensed to participate in saltwater fishing in the study states but reside in a different state.


1.2. Resident Angler Survey


The sample universe for the RAS includes all residential addresses within the study area that are serviced by the United States Postal Service (USPS). Sampling is stratified by coastal state and geographic proximity to the coast within each state. Specifically, counties with any border that is within 25 miles of the coast are in the coastal stratum, and all other counties are in the non-coastal stratum1. Geographic stratification within states provides an opportunity to sample different segments of the population at different rates, thereby increasing the efficiency of data collection. For example, historical estimates from the Marine Recreational Fisheries Statistics Survey (MRFSS) demonstrate that 65-90% of recreational saltwater fishing trips are taken by residents of coastal counties. Subsequently, addresses in coastal strata are sampled at a higher rate.


Each wave, a representative sample of addresses is selected for each stratum in a single stage from a comprehensive list of residential addresses maintained by a vendor licensed to distribute the USPS Computerized Delivery Sequence File. In each state, sampled addresses are matched, by address and telephone number, to databases of anglers who are licensed to participate in saltwater fishing in the respective state. License databases are provided to NMFS by state natural resource agencies approximately one month prior to the beginning of data collection for each wave. Prior to matching, addresses within the license databases are formatted to conform to USPS postal addressing standards, and duplicate angler records are identified and removed.


Matching addresses to license databases screens the ABS sample to identify households with (matched) and without (unmatched) licensed anglers, effectively stratifying the sample into matched and unmatched strata (Lohr, 2009). Augmenting the ABS sample in this manner provides an additional opportunity to optimize sampling - previous studies (Andrews et al., 2010, Brick et al., 2012a, MFES pilot study) have demonstrated that residents of households that match to license databases respond to fishing surveys at a higher rate and are more likely to have fished during the reference wave than residents of unmatched households.


Table 1 provides the sample universe, target sample sizes and estimated number of completed household interviews for each stratum within a given reference wave, and Table 2 provides the annual target sample size and expected number of completed interviews for each state. The target sample size is achieved by retaining all matched addresses from an initial ABS sample, and sub-sampling unmatched addresses at a rate of approximately 30%. Within each state, sample is optimally allocated among strata to maximize the precision of estimates of total fishing effort. The allocation and expected response rates are based upon results of the MFES pilot study and will be reassessed following each wave. Target sample sizes are expected to result in a completed number of household surveys that will achieve a coefficient of variation of 15% on estimates of total fishing effort2 for each state and wave.


Table 1. Estimated size of the sample universe, target sample sizes, expected response rates and estimated number of completed household interviews per wave for the Resident Angler Survey.

State

Geographic Stratum

Estimated Number of Households

Target ABS Sample Size3

Expected Response Rates4

Estimated Completed Interviews

AL

Coastal

1,661,055

2,775

43.8%

1,215

AL

Noncoastal

244,831

307

43.8%

135

CT

Coastal

1,376,955

2,842

47.5%

1,350

DE

Coastal

349,794

4,141

32.6%

1,350

FL

Coastal

7,631,375

3,082

43.8%

1,350

GA

Coastal

3,447,326

2,608

46.6%

1,215

GA

Noncoastal

247,113

326

41.2%

135

HI

Coastal

466,705

3,230

41.8%

1,350

LA

Coastal

828,328

2,775

43.8%

1,215

LA

Noncoastal

945,732

307

43.8%

135

MA

Coastal

631,148

2,416

47.5%

1,147

MA

Noncoastal

1,956,720

413

49.1%

203

MD

Coastal

244,923

3,199

32.6%

1,043

MD

Noncoastal

1,954,989

669

45.9%

307

ME

Coastal

97,900

2,415

47.5%

1,147

ME

Noncoastal

462,106

413

49.1%

203

MS

Coastal

948,126

2,775

43.8%

1,215

MS

Noncoastal

180,716

307

43.8%

135

NC

Coastal

3,065,955

2,608

41.1%

1,215

NC

Noncoastal

787,088

327

46.6%

135

NH

Coastal

144,104

2,415

47.5%

1,147

NH

Noncoastal

378,763

413

49.1%

203

NJ

Coastal

142,908

3,199

32.6%

1,043

NJ

Noncoastal

3,095,540

669

45.9%

307

NY

Coastal

2,788,575

3,199

32.6%

1,043

NY

Noncoastal

4,620,155

669

45.9%

307

PR

Coastal

1,181,112

3,230

41.8%

1,350

RI

Coastal

413,196

2,842

47.5%

1,350

SC

Coastal

1,254,690

2,608

41.1%

1,215

SC

Noncoastal

598,096

327

46.6%

135

VA

Coastal

1,744,021

3,199

32.6%

1,043

VA

Noncoastal

1,393,148

669

45.9%

307

Total

 

45,283,193

61,373

41.8%

25,650


Table 2. Annual target sample sizes and estimated number of completed interviews for the Resident Angler Survey.

State

Target ABS Sample Size

Expected Response Rates

Estimated Completed Interviews

AL

18,492

43.8%

8,100

CT

14,210

47.5%

6,750

DE

20,705

32.6%

6,750

FL

18,492

43.8%

8,100

GA

14,670

46.0%

6,750

HI

19,380

41.8%

8,100

LA

18,492

43.8%

8,100

ME

14,145

47.7%

6,750

MD

19,340

34.9%

6,750

MA

14,145

47.7%

6,750

MS

18,492

43.8%

8,100

NH

14,145

47.7%

6,750

NJ

19,340

34.9%

6,750

NY

19,340

34.9%

6,750

NC

17,604

46.0%

8,100

RI

14,210

47.5%

6,750

SC

14,670

46.0%

6,750

VA

19,340

34.9%

6,750

PR

19,980

40.5%

8,100

Total

329,192

41.8%

137,700

1.3. Nonresident Angler Survey


Non-resident anglers are sampled from lists of individuals who are licensed to participate in saltwater fishing in each study state. The sample frame for each state consists of anglers who were licensed to fish in the state (license state) during the wave but reside in another state. Databases of licensed anglers are provided to NMFS by state natural resource agencies approximately one month prior to the beginning of data collection for each wave. Prior to sampling, addresses within the license databases are formatted to conform to USPS postal addressing standards, and duplicate angler records, as well as records for individuals less than18 years of age are identified and removed.


Each wave, a simple random sample of licensed anglers is selected from each state’s license frame. The survey instrument collects information about recent saltwater fishing activity for the sampled angler, as well as any other individuals who reside at the same address as the sampled angler; each sampled angler represents a cluster of anglers who reside at the same address. Table 3 provides the sample universe, sample size, expected response rates and estimated number of completed surveys for each state within a given reference wave, and Table 4 provides the annual sample size and expected number of completed interviews for each state.


Table 3. Estimated size of the sample universe, sample sizes, expected response rates and estimated number of completed interviews per wave for the Nonresident Angler Survey.


State

Estimated Number of Nonresident Anglers5

Sample Size

Expected Response Rate6

Estimated Completed Interviews

AL

341,049

244

61.4%

150

CT

67,024

241

62.2%

150

DE

150,946

279

53.7%

150

FL

2,654,378

244

61.4%

150

GA

72,437

212

70.8%

150

HI

223,717

234

64.1%

150

LA

164,403

244

61.4%

150

ME

126,542

241

62.2%

150

MD

258,122

279

53.7%

150

MA

308,116

241

62.2%

150

MS

91,219

244

61.4%

150

NH

53,958

241

62.2%

150

NJ

431,069

279

53.7%

150

NY

53,123

279

53.7%

150

NC

761,744

212

70.8%

150

PR

13,795

234

64.1%

150

RI

768,799

241

62.2%

150

SC

406,195

212

70.8%

150

VA

193,905

279

53.7%

150

Total

7,140,541

4,683

60.9%

2,850




Table 4. Annual sample sizes and estimated number of completed interviews for the Nonresident Angler Survey.


State

Sample Size

Expected Response Rate

Estimated Completed Interviews

AL

1,466

61.4%

900

CT

1,206

62.2%

750

DE

1,397

53.7%

750

FL

1,466

61.4%

900

GA

1,059

70.8%

750

HI

1,404

64.1%

900

LA

1,466

61.4%

900

ME

1,206

62.2%

750

MD

1,397

53.7%

750

MA

1,206

62.2%

750

MS

1,466

61.4%

900

NH

1,206

62.2%

750

NJ

1,397

53.7%

750

NY

1,397

53.7%

750

NC

1,271

70.8%

900

PR

1,404

64.1%

900

RI

1,206

62.2%

750

SC

1,059

70.8%

750

VA

1,397

53.7%

750

Total

25,073

61.0%

15,300


A resident of a study state who is also licensed to fish in one of the other study states could be sampled for both the RAS and the NAS. However, given the sampling rates, it is extremely unlikely (less than 1/10 of 1%) that the same individual would be sampled from both frames. Each wave, sample from each frame will be cross-checked against the other sample to identify any duplicates. If this situation were to occur, the NAS sample will be withheld and treated as a special case of nonresponse.


2. Describe the procedures for the collection, including: the statistical methodology for stratification and sample selection; the estimation procedure; the degree of accuracy needed for the purpose described in the justification; any unusual problems requiring specialized sampling procedures; and any use of periodic (less frequent than annual) data collection cycles to reduce burden.


2.1. Data Collection Procedures


The RAS and NAS are both single-phase, self-administered mail surveys, and data collection procedures for the two survey components are identical. These data collection procedures have been extensively tested through previous MRIP pilot studies (Andrews et al. 2010, Brick et al. 2012a). Each year, the surveys are administered for six, two-month reference waves. The data collection period for each wave begins one week prior to the end of the wave with an initial survey mailing. The timing of the initial mailing is such that materials are received prior to the end of the reference wave. The initial mailing is delivered by regular first class mail and includes a cover letter stating the purpose of the survey, a survey questionnaire, a post-paid return envelope and a prepaid cash incentive (as described in section A.9).


One week following the initial mailing, a follow-up thank you/reminder contact is initiated. For sample units with an attached landline telephone number (sample units for which a landline telephone number can be found through a lookup service), an automated voice message is delivered to remind sample units to complete and return the questionnaire. Previous studies have demonstrated that varying the delivery mechanism, for example, switching from regular first class mail to telephone or special mail, may improve response rates in mail surveys (Brick et al., 2012b). For sample with no associated landline telephone number, a thank you/reminder postcard is sent via regular fist class mail. We expect to identify landline telephone numbers for approximately 50% of sampled addresses.


Three weeks after the initial survey mailing, a follow-up mailing is delivered to all sample units that have not responded to the survey. The follow-up mailing is delivered via first class mail and includes a nonresponse conversion letter, a second questionnaire and a post-paid return envelope.


2.2. Estimation Procedures


Final sample weights for both the RAS and the NAS are calculated in stages. In the first stage, base sample weights within each stratum are calculated as the inverse of the selection probability ( , where πi is the probability of selecting unit i for the sample). In the RAS, base weights for addresses that cannot be matched to an angler license database (sample units in the unmatched strata), are adjusted to account for subsampling by multiplying the base weight by the inverse of the subsampling rate.


In the second stage, base weights (or adjusted base weights in unmatched RAS strata) are adjusted to account for nonresponse. Specifically, the weights of nonresponding units are increased by the inverse of the weighted response rate within nonresponse adjustment cells



where



and and are the sums of base weights in cell c for respondents and nonrespondents, respectively. Weights for all individuals who reside at a sampled address are equal to the final sample weight for the address.


In the RAS, nonresponse adjustment cells will be defined by state or residence, coastal/non-coastal county, matched/unmatched designation, and whether or not the address was successfully matched to a landline telephone number. In the NAS, adjustment cells will be at the stratum level (license state). Other potential criteria for defining nonresponse adjustment cells will be examined after each wave of data collection and may include demographic information and type of recreational fishing license.


Estimates of total fishing effort, as well as associated estimates of variance, are calculated in SAS Version 9.3 using the surveymeans procedure. For a given coastal state and wave, total effort is the sum of resident angler effort (from RAS) and nonresident angler effort (from NAS), both of which are calculated as weighted sums




where and are the final weight and reported number of recreational fishing trips, respectfully, for unit j at address i of stratum h.


Variance of the total effort estimate is estimated using the Taylor series method



where








For estimating total fishing effort, we expect stratification to be more effective than simple random sampling due to the higher rate of sampling in coastal strata and of licensed households. Results from the MFES for waves 5-6, 2012 resulted in an overall design effect of 0.72 for estimates of total fishing effort.



3. Describe the methods used to maximize response rates and to deal with nonresponse. The accuracy and reliability of the information collected must be shown to be adequate for the intended uses. For collections based on sampling, a special justification must be provided if they will not yield "reliable" data that can be generalized to the universe studied.


Through three waves of the MFES pilot study, response rates for the RAS and NAS are 41.8% and 60.9 %, respectively when a $2.00 cash incentive is included in the initial survey mailing. We expect similar response for the MFES when the survey is expanded to additional states.


The expected response rates will be achieved by using standard mail survey protocols (Dillman et al, 2008). An initial mailing will include an introductory letter stating the purpose of the survey, the survey questionnaire, a business reply envelope, and a prepaid, $2.00 cash incentive. During the initial waves of the MFES pilot study, a $2.00 incentive was found to be optimal in terms of maximizing response and minimizing data collection costs. Either a thank-you/reminder postcard or automated voice message will be administered to all sample units one week following the initial mailing. A final mailing, including a second questionnaire, a nonresponse conversion letter, and a business reply envelope will be sent to all nonrespondents three weeks after the initial mailing.


We will minimize nonresponse bias by using a questionnaire that maximizes responses by the entire sample population, including both anglers and non-anglers. The MFES pilot study tested two versions of the survey instrument. The MFES will utilize the “Weather and Outdoor Activity Survey” instrument, which provided the most representative sample of the general population in the MFES pilot study.


The MFES pilot study included a nonresponse follow-up study to assess nonresponse bias in the data collection design. Each wave, 400 nonrespondents were sampled for the follow-up study. Data collection for the nonresponse study was initiated six weeks after the final contact for the RAS and the NAS with the delivery of an advance letter via regular first-class mail. Five days later, a survey packet, including a cover letter, questionnaire (the same questionnaire used in the RAS and NAS), post-paid return envelope and a $5.00 cash incentive was delivered via FedEx (USPS Priority Mail was used where FedEXx is unavailable). A thank you/reminder postcard was delivered eight days after the FedEx.


To date, the nonresponse follow-up study has achieved a 40% response rate, and respondents to the nonresponse follow-up study are not significantly different from RAS and NAS respondents in terms of recreational fishing activity. These findings suggest that nonresponse bias in the RAS and NAS is minimal.


We will continue to assess nonresponse bias as the MFES is expanded to additional states. First, we will compare early and late responders with respect to reported fishing activity. This analysis will identify differences in respondents based upon the level of effort required to solicit a response. Previous studies (Brick et al., 2012, MFES pilot study) demonstrated that early and late responders are similar in terms of reported recreational fishing activity.


We will also utilize information from sample frames to define weighting classes for postsurveypost survey weighting adjustments. Weighting classes will be defined such that response rates and fishing activity are similar within classes. Nonresponse bias will be measured by comparing unadjusted estimates to estimates that have been adjusted to account for differential nonresponse among weighting classes. Previous studies identified differential nonresponse and reported fishing activity between households with and without licensed anglers and demonstrated that nonresponse weighting adjustment decreased estimates of fishing effort by 25% over unadjusted estimates (Andrews et al., 2010).


4. Describe any tests of procedures or methods to be undertaken. Tests are encouraged as effective means to refine collections, but if ten or more test respondents are involved OMB must give prior approval.


No additional testing is planned.


5. Provide the name and telephone number of individuals consulted on the statistical aspects of the design, and the name of the agency unit, contractor(s), grantee(s), or other person(s) who will actually collect and/or analyze the information for the agency.


Statistical support was provided by the following:

Dr. J. Michael Brick, Westat, 301- (301) 294-2004

Dr. Nancy A. Mathiowetz, University of Wisconsin-Milwaukee, 414-(414) 229-2216


Rob Andrews, Fisheries Biologist, NOAA Fisheries Service, Office of Science and Technology, 301-(301) 427-8105 is the point-of-contact for the Agency.




References


Andrews, W.R., J.M. Brick, N.M. Mathiowetz, and L. Stokes (2010). Pilot Test of a Dual Frame Two-Phase Mail Survey of Anglers in North Carolina. Retrieved from http://www.countmyfish.noaa.gov/projects/downloads/Final_Report%20NC%202009%20Dual%20Frame%20Two%20Phase%20Experiment.pdf.


Brick. J.M., W.R. Andrews, and N.M. Mathiowetz (2012a). A Comparison of Recreational Fishing Effort Survey Designs. Retrieved from https://www.st.nmfs.noaa.gov/mdms/doc/08A_Comparison_of_Fishing_Effort_Surveys_Report_FINAL.pdf.

Brick, J.M., W.R. Andrews, P.D. Brick, H. King, and N.M. Mathiowetz (2012b). Methods for Improving Response Rates in Two-Phase Mail Surveys. Survey Practice 5(4).

Dillman, D.A., J.D. Smyth, and L.M. Christian (2009). Internet, Mail, and Mixed-Mode Surveys: The Tailored Design Method. New York: Wiley and Sons.

Lohr, S. (2009). Multiple Frame Surveys. Chapter 4 in Pfeffermann, D. (Ed.) Handbook of Statistics: Sample Surveys Design, Methods and Applications (vol. 29A). Elsevier, Amsterdam.



1 Florida is not stratified due to the relatively high rate of fishing across the state, and Connecticut, Delaware, Hawaii, Puerto Rico and Rhode Island are not stratified due to the small geographic areas of the states.

2 Total fishing effort includes fishing by both resident (RAS) and nonresident anglers (NAS).

3 Target sample sizes reflect the number of addresses that will be mailed a survey questionnaire and are achieved by retaining all addresses from initial ABS samples that match to a state license database and 30% of addresses that do not match.

4 Estimated response rates and sampling requirements are based upon results from the MFES pilot study and are assumed to be uniform among states within a region (e.g. New England, Mid Atlantic, South Atlantic and Gulf).

5 Based upon participation estimates from the Marine Recreational Fisheries Statistics Survey

6 Estimated response rates are based upon results from the MFES pilot study and are assumed to be uniform among states within a region.

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