Mike Murphy Fish and Wildlife Research Institute Florida Fish and Wildlife Conservation Commission St Petersburg, FL
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1 Development of historical annual recreational landings of red drum from 1950 through 1980 for the Atlantic coast states from Florida through New Jersey. Mike Murphy Fish and Wildlife Research Institute Florida Fish and Wildlife Conservation Commission St Petersburg, FL June 20, 2015 The last benchmark assessment used available data from 1989 through 2007 (SEDAR 18). The lack of age composition to characterize the catch prior to 1989 led to shortening of the original assessment period from to in the final reviewed assessment runs. The assessment model used for SEDAR 18 required external processing of the available data to develop a complete age composition of the catch for all fishing fleets used in the model (retained and released fisheries) and this required a large amount of data pooling and major assumptions about similar compositions over time. A disadvantage to the truncation of the data period is high uncertainty in the initial estimated state of the stock (level of depletion). There was also little contrast in exploitation rates through this period (especially in the south) by which to understand the stock response to removals. Given the move to use a new model platform (Stock Synthesis 3) that utilized the input data at a much less processed level, ideally retaining a truer level of uncertainty, the assessment time period was expanded to include exploitation back through Though the red drum commercial fishery was still fairly well developed by 1950 it was known that the additional years of data would add some contrast in the levels of exploitation. In order to implement this change, estimates of the recreational harvest and releases are needed through the complete time frame. The Marine Resources Information Program (and predecessor Marine Recreational Fisheries Statistics Survey) began providing estimates of recreational catch in The following follows the procedure used in estimating recreational harvest of black drum (ASMFC 2014). Previous estimates of historic recreational catch have been based on human population from the U.S. Census (e.g. Florida Spotted Seatrout, Murphy et al. 2011) or coastwide estimates of saltwater anglers and days spent saltwater fishing from the National Survey of Fishing, Hunting, and Wildlife-Associated Recreation (FHWAR) (South Atlantic Spanish mackerel, Brennan and Fitzpatrick 2012). The human population method assumes that the number of anglers is proportional to the total coastal population and does not account for periods when recreational fishing expanded faster (or slower) than human population. The FHWAR method applied to Spanish mackerel uses coastwide estimates of saltwater fishing effort and assumes that the rate of expansion in saltwater angling was the same across the entire region. Here, we combined information from the FHWAR survey with historical fishing license data to estimate historical recreational catch in each year and state from Historic fishing license data were available in the USFWS National Fishing License Reports ( from for each state. No data were available in 1960 and only Georgia was available in These reports provide values for the number of certified paid fishing license holders (participants) in each state, where
2 a license holder is one individual regardless of the number of licenses purchased. The reports do not differentiate between saltwater and freshwater anglers. The National Survey of Fishing, Hunting, and Wildlife-Associated Recreation (FHWAR) provides data about the state in which these activities occurred, the number of trips taken, days of participation, type of trip, and expenditures. The survey was conducted 1991, 1996, 2001, 2006, and 2011 by the Census Bureau for the U.S. Fish and Wildlife Service. An estimate of the percentage of anglers in each state that fish in saltwater is provided in these reports (%saltwater). This percentage was extrapolated linearly between years when the survey was not conducted. Prior to 1991, the %saltwater was only available nationally and only every five years from These national percentages were used to extrapolate back the statewide estimates. The total number of license holders from the USFWS Historic Fishing License data was then adjusted by the percent estimates from the FHWAR surveys to get the total number of saltwater participants by year and state (Table 1). Lastly, CPUE was calculated for each year and state from by dividing the MRFSS/MRIP harvest estimates by the total number of saltwater participants. The number of saltwater participants in each state each year from was then multiplied by the average CPUE (or available years in sparse-catch states like NJ, DE, MD) to estimate historical harvest since 1950 (Table 2). The same procedure was applied to live-release estimates (Table 3) Literature ASMFC Black drum stock assessment for peer review. Atlantic States Marine Fisheries Commission Stock Assessment Report No., Washington, D.C. Brennan, K., and K. Fitzpatrick Estimates of recreational landings of Spanish mackerel in the South Atlantic using the FHWAR census method. SEDAR 31-RD25. SEDAR, North Charleston, SC. Murphy, M. D., Chagaris, D., and D. Addis An assessment of the status of spotted seatrout in Florida waters through Florida Fish and Wildlife Conservation Commission. Fish and Wildlife Research Institute. IHR Available online at:
3 Table 1 Estimated number of saltwater angler participants each year based on National Survey of Fishing, Hunting, and Wildlife-Associated Recreation (FHWAR) data. Year DE FL GA MD NJ NC SC VA , ,900 58,689 45,387 80,422 95,637 44, , , ,187 60,518 46,801 82,928 98,618 46, , , ,475 62,347 48,216 85, ,598 47, , , ,762 64,176 49,630 87, ,579 48, , , ,049 66,006 51,045 90, ,560 50, , , ,337 67,835 52,459 92, ,541 51, , , ,624 69,664 53,874 95, ,521 53, , , ,911 71,493 55,289 97, ,502 54, , , ,199 73,322 56, , ,483 55, , , ,676 83,528 56, ,199 77,808 58, , , ,577 84,808 58, ,561 79,702 60, , , ,720 87,064 58, , ,602 64, , , ,199 89,882 73, , ,338 69, , , ,699 99,412 69, , ,518 77, , , , ,567 74, , ,586 79, , , , ,125 82, , ,987 86, , , , ,537 88, , ,296 79, , , , ,220 90, , , , , , , , , , , , , , , ,150 86, , , , , , , ,638 85, , ,272 88, , , , ,846 92, , ,823 94, , , , ,360 97, , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , ,075 97, , , , , , , , , , , , , , , ,013 96, , , , , , , , , , , , , , , ,388 99, , , , , , , ,225 87, , , , , , , ,649 88, , , , , , , ,869 88, , , , , , , ,965 92, , , , , , , , , , , , , , , , , , , , , , , , , , ,443 97, , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , , ,546 96, , , , , , , ,380 79, , , , , , , ,024 59, , , , , , , ,377 66, , , , , , , ,720 68, , , , , , , ,838 77, , , , , , , ,444 79, , , , , , , ,356 86, , , , , , ,579 1,008,471 92, , , , , , ,269 1,057,003 90, , , , , , ,856 1,085,113 93, , , , , , ,198 1,079,780 96, , , , , , ,484 1,059,224 95, , , , , , ,078 1,140,376 96, , , , , , ,736 1,066, , , , , , ,023
4 Table 2. Estimated historical recreational annual harvest of red drum (in numbers, equivalent to Type A+B1 catch from MRIP/MRFSS) during for Atlantic states from NJ through FL. Year NJ DE MD VA NC SC GA FL Total ,483 32,261 60,597 42, , , ,779 33,267 62,485 43, , , ,074 34,272 64,374 44, , , ,370 35,278 66,263 46, , , ,665 36,283 68,151 47, , , ,961 37,289 70,040 48, , , ,257 38,294 71,928 50, , , ,552 39,300 73,817 51, , , ,848 40,305 75,706 52, , , , ,954 26,247 79,641 59, , , , ,221 26,886 81,579 60, , , ,361 38,322 86,673 62, , , ,836 37,895 94,234 64, , , ,120 37, ,732 71, , , ,809 43, ,017 75, , , ,574 48, ,964 84, , , ,318 50, ,257 94, , , ,011 13,951 54, ,425 86, , , ,126 15,035 56, ,600 82, , , , ,823 59, ,761 81, , , , ,988 59, ,528 85, , , , ,038 17,035 59, ,584 91, , , , ,088 18,433 61, ,907 93, , , , ,136 19,898 67, ,732 96, , , , ,255 21,527 73, , , , , , ,166 18,149 74, , , , , , ,097 17,053 70, , , , , , ,268 17,709 64, ,452 96, , , ,084 16,487 61, ,118 91, , , , ,137 17,671 61, ,788 95, , , , ,114 18,073 59, ,089 92, , ,290
5 Table 3. Estimated historical recreational annual live-releases of red drum (in numbers, equivalent to Type B2 catch from MRIP/MRFSS) during for Atlantic states from NJ through FL. Year NJ DE MD VA NC SC GA FL Total ,343 3,289 1,457 13,643 22, ,416 3,391 1,503 14,068 22, ,489 3,494 1,548 14,493 23, ,562 3,596 1,593 14,918 24, ,635 3,699 1,639 15,344 24, ,708 3,801 1,684 15,769 25, ,781 3,904 1,730 16,194 26, ,854 4,006 1,775 16,619 26, ,927 4,109 1,821 17,044 27, ,906 4,322 2,074 18,762 28, ,953 4,427 2,106 19,219 29, ,783 4,704 2,162 21,278 32, , ,752 5,114 2,232 20,072 32, , ,757 5,684 2,468 20,508 33, , ,175 5,862 2,596 21,496 35, , ,527 6,348 2,908 22,699 37, , ,658 5,821 3,266 23,284 38, , ,932 7,621 2,985 25,321 42, , ,113 7,739 2,846 25,453 42, , ,299 8,725 2,834 26,746 45, , ,318 6,487 2,946 28,874 44, , ,332 6,924 3,150 36,202 53, , ,448 7,484 3,237 37,516 55, , ,886 7,909 3,348 39,654 58, , ,327 8,653 3,582 42,811 63, , ,395 9,039 3,701 44,672 65, , ,092 9,471 3,577 42,175 63, , ,657 8,925 3,324 37,939 57, , ,497 8,581 3,179 34,266 53, , ,494 8,563 3,287 36,750 55, , ,290 8,525 3,213 30,214 49,119
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