Hook Selectivity in Gulf of Mexico Gray Triggerfish when using circle or J Hooks

Similar documents
Beverly Sauls SEDAR31-DW11. 5 August 2012

Black Seabass Length Frequencies and Condition of Released Fish from At-Sea Headboat Observer Surveys, 2004 to 2010.

Discards of red grouper (Epinephelus morio) for the headboat fishery in the US Gulf of Mexico SEDAR 42- DW- 17

Overview of Florida s Cooperative East Coast Red Snapper Tagging Program, SEDAR41-DW10. Submitted: 1 August 2014

Standardized catch rates of U.S. blueline tilefish (Caulolatilus microps) from commercial logbook longline data

Nancy E. Kohler, Danielle Bailey, Patricia A. Turner, and Camilla McCandless SEDAR34-WP-25. Submitted: 10 June 2013

Specialized Survey Methods for Recreational Reef Fish Fisheries in Florida

Summary Report of the North Carolina Division of Marine Fisheries Cobia (Rachycentron canadum) Acoustic Tagging. Stephen J. Poland SEDAR58-SID-06

Estimates of Historic Recreational Landings of Vermilion Snapper in the South Atlantic Using the FHWAR Census Method. Ken Brennan SEDAR 55-WP04

Reef Fish Amendment 32 Gag and Red Grouper

Addendum to SEDAR16-DW-22

August 3, Prepared by Rob Cheshire 1 & Joe O Hop 2. Center for Coastal Fisheries and Habitat Research Beaufort, NC

Estimates of Historic Recreational Landings of Red Snapper in the South Atlantic Using the FHWAR Census Method SEDAR41-DW17 DRAFT

SEDAR 50 Discard Mortality Ad-Hoc Group Working Paper. Discard Mortality Ad-hoc Group SEDAR50-DW22. Submitted: 26 January 2017

Estimates of Historic Recreational Landings of Red Snapper in the South Atlantic Using the FHWAR Census Method SEDAR 41-DW17

SEDAR52-WP November 2017

Tab B, No /10/16. Red Snapper Management for Federally Permitted Charter Vessels. White Paper

SCDNR Charterboat Logbook Program Data, Mike Errigo, Eric Hiltz, and Amy Dukes SEDAR32-DW-08

Goliath grouper management stakeholder project. Kai Lorenzen, Jessica Sutt, Joy Hazell, Bryan Fluech, Martha Monroe University of Florida

Mike Murphy Fish and Wildlife Research Institute Florida Fish and Wildlife Conservation Commission St Petersburg, FL

Unless otherwise noted, images throughout the presentation are by FWC.

Status and Trends Report: 2012 Penaeid Shrimp Species Account FL FWCC FWRI SEDAR-PW6-RD July 2014

Atlantic States Marine Fisheries Commission DRAFT ADDENDUM I TO THE BLACK DRUM FISHERY MANAGEMENT PLAN FOR PUBLIC COMMENT

South Atlantic Council Issues

Atlantic States Marine Fisheries Commission

Update: This document has been updated to include biological information on red snapper and information from the recent Gulf of Mexico Fishery

Public Hearing Summary for Coastal Migratory Pelagics Framework Amendment 4

ASMFC Stock Assessment Overview: Red Drum

United States Commercial Vertical Line Vessel Standardized Catch Rates of Red Grouper in the US South Atlantic,

Coastal Migratory Pelagics Joint Amendment 28 (Separate management plans/ permits)

Days-at-Sea Pilot Program for Recreational Red Snapper

Modification to Gear Requirements for Yellowtail Snapper in the Gulf of Mexico

Fisheries of the Caribbean, Gulf of Mexico, and South Atlantic; Reef Fish Fishery of Puerto Rico and the U.S. Virgin Islands;

STANDARDIZED CATCH RATES OF BLUEFIN TUNA, THUNNUS THYNNUS, FROM THE ROD AND REEL/HANDLINE FISHERY OFF THE NORTHEAST UNITED STATES DURING

Minnesota Department of Natural Resources Fisheries Division, Lake Superior Area

Modifications to Gulf Reef Fish and South Atlantic Snapper Grouper Fishery Management Plans

Authors: Luiz Barbieri and Martha Bademan

Marine Recreational Information Program Transition to Improved Survey Designs

Cami T. McCandless and Joesph J. Mello SEDAR39- DW June 2014

John Carlson and Jason Osborne SEDAR34-WP-02. Submitted: 6 May 2013 Updated: 8 July 2013

Southeast Regional Office:

Georgia Red Snapper Catch & Effort Data Collection During Mini-Seasons, Kathy Knowlton SEDAR41-DW02

Craig A. Brown. NOAA Fisheries, Southeast Fisheries Center, Sustainable Fisheries Division 75 Virginia Beach Drive, Miami, FL, , USA

Angling in Manitoba (2000)

Unless otherwise noted, images throughout the presentation are by FWC.

Scoping Guide 10/15/15. Reef Fish Amendment 42 - Reef Fish Management for Federally Permitted Headboats

Georgia Bass Clubs. Tournament Creel Report

A non-equilibrium surplus production model of black grouper (Mycteroperca bonaci) in southeast United States waters

Columbia River Salmon Harvest Sport and Commercial Sharing Facts and Relationships

SCDNR Charterboat Logbook Program Data,

Preliminary catches of smoothhound sharks SEDAR39-DW-03

Modeling effects of fishing closures in the Western Florida Shelf

Update on recent modifications of fishing gear and fishing procedures to reduce bycatch of sea turtles in longline fishery

Preliminary Report. Note: calculations reported are preliminary and should not be cited without the author s permission. December 21, 2003.

Evaluating the Influence of R3 Treatments on Fishing License Sales in Pennsylvania

Gray Triggerfish Rebuilding Plan

The Economics of Atlantic Highly Migratory Species For-Hire Fishing Trips July - November 2013 Clifford Hutt and George Silva

Angling in Manitoba Survey of Recreational Angling

Sheepshead Fishery Overview South Atlantic State/Federal Management Board May 2014 Introduction Life History Landings

Black Sea Bass Encounter

Gulf States Seaward Boundary Changes Implications for Gulf Fisheries Management

Habitat Omnibus Amendment DEIS draft sections relative to recreational fishery DRAFT. Omnibus Essential Fish Habitat Amendment 2

Aerated Lakes Angler Survey: Swan and Spring Lakes, Alberta, 2015

DEPARTMENT OF FISH AND GAME

Red Snapper Allocation

ASMFC Stock Assessment Overview: Red Drum

A SURVEY OF 1997 COLORADO ANGLERS AND THEIR WILLINGNESS TO PAY INCREASED LICENSE FEES

Assessment Summary Report Gulf of Mexico Red Snapper SEDAR 7

Recreational Fishing License Sales in Florida:

Scholar Commons. University of South Florida. Beverly J. Sauls University of South Florida, January 2013

PUBLIC HEARING GUIDE 10/4/12

Establish interim harvest reductions that end overfishing and rebuild the spawning stock biomass by 2015.

Susquehanna River Walleye Fishery

Unless otherwise noted, images throughout the presentation are by FWC.

Draft. Hiroki Yokoi, Yasuko Semba, Keisuke Satoh, Tom Nishida

Alabama Management for Recreational Red Snapper

DOT HS September Crash Factors in Intersection-Related Crashes: An On-Scene Perspective

Mississippi Management for Recreational Red Snapper

Scoping Guide 10/15/15. Reef Fish Amendment 41 - Red Snapper Management for Federally Permitted Charter Vessels

2018 COM Doc. No. PA4_810 / 2018 November 7, 2018 (11:44 AM)

Florida s Artificial Reef Monitoring Efforts

Public Hearing Summary

INLAND LAKE MANAGEMENT REPORT FY Spring 2008

Tab B, No 4(a) 1/4/07

Department of Fish and Game

SEDAR 10 DW- 08. REVIEW OF TAGGING DATA FOR GAG GROUPER (Mycteroperca microlepis) FROM THE SOUTHEASTERN GULF OF MEXICO REGION

Mutton Snapper Public Workshops February Florida Fish and Wildlife Conservation Commission Division of Marine Fisheries Management

Rainy Lake Open-water Creel Survey:

Atlantic States Marine Fisheries Commission

Economic Contribution of the 2018 Recreational Red Snapper Season in the South Atlantic

Evaluation of effects of management options for the recreational cod fishery in the western Baltic Sea

Modify Federal Regulations for Swordfish Trip Limits the Deep-set Tuna Longline Fishery. Decision Support Document November 2010

White Paper on the Potential 2018 Experimental Wave 1 Recreational Black Sea Bass Fishery

CALIFORNIA DEPARTMENT OF FISH AND WILDLIFE RECOMMENDATIONS ON ADDITIONAL WINTER-RUN PROTECTIONS IN 2016 OCEAN FISHERIES

Florida Fish and Wildlife Conservation Commission (FWC)

N. Abid 2 and M. Idrissi 1 ABSTRACT

Minimum Stock Size Threshold (MSST) for reef fish stocks with low natural mortality

Executive Summary Lavoie Lake 2000

This is a review and discussion of actions and discussions from the South Atlantic Fishery Management Council s (Council) Sept. 30 through Oct.

Standardized catch rates of black grouper. Mycteroperca bonaci, and red grouper, Epinephelus morio, from Florida s commercial trip tickets,

Transcription:

Hook Selectivity in Gulf of Mexico Gray Triggerfish when using circle or J Hooks Alisha M. Gray and Beverly Sauls SEDAR43- WP- 09 25 March 2015 This information is distributed solely for the purpose of pre-dissemination peer review. It does not represent and should not be construed to represent any agency determination or policy.

Please cite this document as: Gray, A.M. and B. Sauls. 2015. Hook Selectivity in Gulf of Mexico Gray Triggerfish when using circle or J Hooks. SEDAR43-WP-09. SEDAR, North Charleston, SC. 6 pp.

Hook Selectivity in Gulf of Mexico Gray Triggerfish when using circle or J Hooks. Alisha M. Gray 1 and Beverly Sauls 1 1 Florida Fish and Wildlife Conservation Commission Fish and Wildlife Research Institute 100 8 th Ave SE, St Petersburg, FL 33701 March 2015 I. Introduction The US Gulf of Mexico supports a year-round recreational fishery that constitutes a large portion of total removals for many fish stocks. Harvest control measures for gray triggerfish include size limits, bag limits and in recent years, seasonal closures. Additional measures have been adopted, including regulating hook type and offset (GMFMC, 2007; Florida Administrative Code 68B- 14.005), to reduce hook related injuries to individuals that are released. Florida Administrative Code 68B-14.005 states that recreational anglers fishing in federal waters must use nonstainless steel circle hooks when catching reef fishes with natural bait. A circle hook is defined by this regulation as a fishing hook designed and manufactured to form a generally circular, or oval, shape. This analysis seeks to better understand how hook size and hook type might influence the size of fish caught. Data for this analysis were collected after the circle hook requirement was implemented; however, there were enough observations of gray triggerfish caught with J hooks to offer some insight into potential changes in selectivity since circle hooks were required. Size selectivity of hooks is considered separately for circle hooks and J hooks. II. Methods Data were collected as part of a cooperative research project with operators of for-hire fishing vessels that offer recreational fishing trips in the Gulf of Mexico. Biologists were assigned to randomly selected vessels to observe recreational anglers during hook and line fishing. Further details of the study are described in Sauls and Ayala (2012). Variables collected for individual gray triggerfish include region and depth of capture, fork length, hook size, hook type and anatomical location where the hook embedded. Hook size was determined in the field by laying them onto a standardized sizing chart (Figure 1). The smallest circle hook on the chart was size 5; therefore, smaller hooks that could not be assigned a size in the field were assigned to one overall small size category (size 3). Three regions were sampled on the Gulf coast of Florida, including the Northwest panhandle, the Big Bend, and greater Tampa Bay. Only greater Tampa bay (TB) and the northwest panhandle (NW) were used for this analysis, due to low sample sizes in the Big Bend.

We constructed a generalized linear model to test the significance of hook type and size on the fork length of gray triggerfish caught by recreational anglers. Covariates were also tested for inclusion to explain variability in the model. III. Results Of the total number of Gray Triggerfish observed, 3,680 fish, or nearly 90%, were caught with a circle hook, while 416, or roughly 10%, were caught with a J hook. Differences were seen in hook type use in the different regions (Table 1). The NW had a nearly 10:1 ratio of circle hook to J hook use, while TB had a 2:1 ratio. The NW also tended to use a smaller sized circle hook, with 71% of gray triggerfish observed from this region caught on small circle hooks (size 3), versus only 33% in greater TB. Additionally, almost all J hooks used in the NW were small, which was not the case in TB. Both regions, however, produced similarly sized fish (Figure 2), with the most common size being in the 30 cm length bin (between 25cm and 35cm). The average fork length of fish caught on circle hooks (regardless of hook size) was 6 mm larger than fish caught on J hooks (Table 2), which was statistically significant but does not represent a large effect. Factors tested for inclusion in the GLM model include hook size, hook type, depth of capture, and possible interaction terms. Region was not included in the model because it was potentially correlated with the selective use of circle hooks versus J hooks (Table 1). We first tested each variable in a single factor model, then used forward selection methods to enter additional factors. Factors were selected based on amount of influence on sums of squares. Hook size alone explained the highest percentage of variability among the single factor models, but the R square was very low (Table 3). As other factors were entered into the model, the R squared value was only slightly improved (Table 3). Results for the final model are shown in Table 4. Figures 3 and 4 illustrate how fork length varies with increased size of circle hooks and J hooks in each region. Small circle hooks capture a wide size range of fish; however, smaller fish disappear with increasing circle hook size (Figure 3). The NW has far fewer J hook observations (Figure 4), but of those that were observed, nearly all were small hook sizes. The only significant interaction was between hook size and depth. Gray triggerfish observations by hook size and depth are shown in Table 5, with depths binned into shallow (<30m), moderate (30m-35m) and deep (>35m) categories. Interaction terms for hook size * hook type and hook type * depth were not significant. Table 1. Gray triggerfish observations by hook type and region (NW=northwest, TB=greater Tampa Bay). Hook Type NW TB C 3356 92 J 324 54 Total 3680 146

Table 2. Least Squares Mean of fork length of fish caught using circle and J. Hook Type FL LS mean Pr > [t] C 348.99 0.0346 J 342.59 Table 3. GLM comparisons for the response variable, fork length. The final model selected is highlighted in gray. Sum of Squares R-square P-value Model 13499.06 0.0014 0.0208 Hook Type 131712.92 0.0137 <0.0001 Depth 698360.53 0.0723 <0.0001 Hook Size 698360.96 0.0723 <0.0001 Hook Size, Hook Type 802663.76 0.0832 <0.0001 Hook Size, Depth 923381.90 0.0957 <0.0001 Hook Size, Depth, Hook size * Depth 804665.00 0.0833 <0.0001 Hook Size, Depth, Hook Type 927656.43 0.0961 <0.0001 Hook Size, Depth, Hook Type, Hook size * Depth Table 4. Results for the final model. Source DF Type III SS Mean Square F Value Pr > F Hook Size 8 195500.5240 24437.5655 10.64 <.0001 Depth 1 2544.3935 2544.3935 1.11 0.2927 Depth*Hook Size 8 122991.4223 15373.9278 6.69 <.0001 Hook Type 1 4274.5229 4274.5229 1.86 0.1726 Table 5. Hook size use at each depth bin. Depth 1 includes all depths below 30m, depth 2 includes all depths between 30m and 35m, and depth 3 includes all depths above 35m. Depth 1 Frequency HookSize 3 5 6 7 8 9 10 11 12 Total 847 163 75 88 26 14 22 3 0 1238 Percent 22.14 4.26 1.96 2.30 0.68 0.37 0.58 0.08 0 32.36 Row Pct 68.42 13.17 6.06 7.11 2.10 1.13 1.78 0.24 0 2 Frequency 977 157 57 63 28 3 15 2 1 1303 Percent 25.54 4.10 1.49 1.65 0.73 0.08 0.39 0.05 0.03 34.06 Row Pct 74.98 12.05 4.37 4.83 2.15 0.23 1.15 0.15 0.08 3 Frequency 849 207 75 65 44 21 21 1 2 1285 Percent 22.19 5.41 1.96 1.70 1.15 0.55 0.55 0.03 0.05 33.59 Row Pct 66.07 16.11 5.84 5.06 3.42 1.63 1.63 0.08 0.16 Total Frequency 2673 527 207 216 98 38 58 6 3 3826 Percent 69.86 13.77 5.41 5.65 2.56 0.99 1.52 0.16 0.08 100

Figure 1. Hook sizing chart used in the field.

3000 2500 120 100 NW Frequency 2000 1500 1000 80 60 40 TB Frequency 500 20 0 0 10 20 30 40 50 60 Length bins (cm) 0 NW TB Figure 2. Size frequency of gray triggerfish in the Northwest Panhandle and in greater Tampa Bay. Fish are lumped into 10 cm fork length bins. Northwest panhandle (n=3680) is shown in blue and greater Tampa Bay (n=146) is shown in red. Figure 3. Fork length of gray triggerfish caught on circle hooks by hook size and region. All small hooks below size 5 were combined into the size 3 category.

Figure 4. Fork length of gray triggerfish caught on J hooks by hook size and region. All small hooks below size 5 were combined into the size 3 category. IV. Conclusion In fishery dependent observations, a high degree of variability is expected. Terminal tackle used on for-hire fishing vessels have a wide variety of configurations, vessel operators may choose from a variety of hook brands and fish with a variety of baits, and skill levels vary among anglers. However, observational studies that measure conditions within a fishery are important for understanding the true degree of impact, given all of the inherent variability. The lack of a significant interaction between hook size and hook type suggests that there are no significant differences in the sizes of fish caught with circle hooks compared to J hooks within the same hook size category. The overall conclusion from this analysis is that circle hooks do not select for substantially larger or older fish compared to J hooks, and the limited selectivity that was accounted for in the model was primarily attributed to hook size. Gray triggerfish size increased only slightly with increased hook size. Smaller size classes of fish disappear with increasing hook size; however, a wide size range of fish are observed across the range of hook sizes. References Sauls B, Ayala O. 2012. Circle hook requirements in the Gulf of Mexico: Application in recreational fisheries and effectiveness for conservation of reef fishes. B Mar Sci. 88(3):667-679.