MRIP UPDATE: Improving Recreational Catch Estimation
New England Fishery Management Council Recreational Advisory Panel - November 1, 2011 Paul Perra NOAA Fisheries Service Gloucester, MA.
MRIP UPDATE: Improving Recreational Catch Estimation New England - - PowerPoint PPT Presentation
MRIP UPDATE: Improving Recreational Catch Estimation New England Fishery Management Council Recreational Advisory Panel - November 1, 2011 Paul Perra NOAA Fisheries Service Gloucester, MA. Marine Recreational Information Program (MRIP) 2
New England Fishery Management Council Recreational Advisory Panel - November 1, 2011 Paul Perra NOAA Fisheries Service Gloucester, MA.
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been a top MRIP priority.
estimates.
implementation
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NOAA Fisheries provides two estimates of recreational fishing activity:
particular reporting period.
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Collecting Data Assessing Fishery Health Setting Catch Targets Making Regulations Fishery management decisions are based on a continuous cycle. Our goal is to ensure fisheries remain productive – now and for generations to come. Quality Data is Critical
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The Marine Recreational Information Program - Moving Into a New Era of Data Collection
Created in 2007 to address:
National Research Council’s Review of Recreational Fisheries Survey Methods.
Magnuson-Stevens Act.
catch and effort estimates.
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angler intercepts at the expense of statistical rigor.
estimates and their precision.
NRC recommended we fix both the way we estimate catch and the way we gather data.
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potential for bias is the result of unaccounted for factors or untested assumptions
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Precise, but inaccurate Precise and accurate
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John Foster, NOAA Fisheries
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What We’ve Done in the Past What We’re Fixing Changes to New Catch Estimation Design Changes to New Shoreside Sampling Design We assumed our shoreside sampling was random and therefore representative of the whole population of anglers. Shoreside sampling design was not truly random, but rather a multi-stage cluster design. The new estimation method is appropriate for a multi-stage cluster sample. Our designs for sampling anglers and estimating catch are now matched. N/A. A multi-stage cluster sample design will still be used. We will emphasize getting complete counts of anglers and boats at sites sampled.
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What We’ve Done in the Past What We’re Fixing Changes to New Catch Estimation Design Changes to New Shoreside Sampling Design We assumed that catch sampled during peak times could accurately estimate catch across an entire 24-hour period. We’re testing the assumption that non- peak catch differs significantly from peak period catch. The new estimation method is weighted to account for catch during all periods of the day. We will sample sites during 4 specified six-hour blocks. Sampling during both peak and non-peak times will enable us to more accurately estimate catch across a whole day
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What We’ve Done in the Past What We’re Fixing Changes to New Catch Estimation Design Changes to New Shoreside Sampling Design
Samplers’ site assignments were selected based on the pressure rating by mode, day type and
samplers had discretion to sample alternate mode trips that they
the assigned site The selection probability
alternate modes sampled cannot be
it is not possible to weight the estimate to account for the true selection probability. Data collected for “alternate mode” trips sampled at primary assigned sites will not be used in new estimates. Samplers will only collect data for the mode for which the site was selected.
More Representative Sampling of Modes
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What We’ve Done in the Past What We’re Fixing Changes to New Catch Estimation Design Changes to New Shoreside Sampling Design
Site assignments were based on PPS sampling based on the pressure rating by mode, day type and month. However, samplers were allowed to move to an alternate site of their choice after 2 hours if there was little or no activity at the assigned site. The selection probabilities of the alternate sites were not
estimates were not weighted properly to account for the alternate site selection probabilities. Selection probabilities of the alternate sites have been estimated (model- based method), and the estimates have been re- weighted to account for them. Samplers will conduct interviews at a specific cluster of sites in a specific randomized order for the full time period, ensuring more structured sampling and less sampler discretion.
More Representative Sampling of Sites
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Removing potential bias affects both the point estimate and its associated measure of precision, expressed either as the Percent Standard Error (PSE) or graphically as the Confidence Interval.
Point Estimates
Precision
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Changes in catch estimates can affect:
under or over the catch limit?
Where there are significant changes in the estimates, revisions to fishing regulations may be necessary.
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2011 and release the updated estimates.
programming, legacy data.
methodology.
improved estimates.
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Intercept Survey (Angler Intercept Survey or APAIS).
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party/charter
workshops
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Intercept Survey design over the next 8 months
site pressure groupings;
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Tech call, Wave Meeting);
collection.
develop strategies to respond to challenges to states, including discussion of sample size issues;
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given time period.
telephone surveys conducted through random-digit dialing of coastal households.
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Accounting for possible under-estimates of effort by testing:
license directory)
National Saltwater Angler Registry
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MOAs in place with all Atlantic states. Each state has provided initial data. Next steps:
Mixed mode dual frame survey expanded pilot in South Atlantic beginning Wave 6 2011; then coastwide expansion in 2012, consistent with pilot results and peer review of methodology
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in-season management
expansions/improvements
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preliminary 2011 Waves in 2012
survey in South Atlantic region beginning Wave 6, 2011.
for Atlantic coast -TBA.
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numbers with a known level of precision.
increased sample sizes.
recreational fishing industry as we proceed with implementation
methodology is a fundamental improvement that allows for a range of future enhancements.
methodology and address effort issues.
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You will soon be able to query the new estimates using the comparison tool at www.CountMyFish.noaa.gov. NMFS contact for detailed MRIP questions is: gordon.colvin@noaa.gov or (301) 427-8118
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