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------------------------------------ The Gulf and South Atlantic Fisheries Development Foundation, Inc. (Foundation) announces the availability of the following technical report:
Branstetter, S. 1997. Bycatch and it reduction in the Gulf of Mexico and South Atlantic shrimp fisheries.
The executive summary of this report is included below.
(((We have been contacted by the owner of a specific web site who is interested in making an electronic copy, including graphics, available on his site. We will make that information available if and when the process is completed.)))
Until then, this report (27 pages, 5 tables, 21 figures) is available for five dollars ($5.00 US) to cover the cost of processing requests and getting them mailed out. Payment must be in US funds; personal checks are fine, but credit card orders cannot be handled. The Foundation also recognizes that it may be difficult for international parties to obtain payment in U.S. funds; if so, please contact our office.
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----------------- Branstetter, S. 1997. Bycatch and it reduction in the Gulf of Mexico and South Atlantic shrimp fisheries. Gulf and South Atlantic Fisheries Development Foundation, Inc., Tampa, Florida.
EXECUTIVE SUMMARY
Concerns over the magnitude and species composition of bycatch, discards, and incidental finfish mortality associated with shrimp trawling prompted a 1990 amendment to the Magnuson Fishery Conservation and Management Act that mandated the development of a Bycatch Reduction Research Program. As part of a multi-organizational response to this mandate, the Gulf and South Atlantic Fisheries Development Foundation, Inc. (Foundation) coordinated the development of a strategic planning document - A Research Plan Addressing Finfish Bycatch in the Gulf of Mexico and South Atlantic Shrimp Fisheries. The long- term goal of this comprehensive four-year plan was to provide reliable information about bycatch in the southeast U.S. shrimp trawl fishery. Subsequently, the Foundation focused its programmatic contribution on four of the eight high-priority objectives outlined in that Plan:
update and expand bycatch estimates temporally and spatially ("catch characterization")
identify, develop, and evaluate gear options for reducing bycatch ("BRD evaluations"),
provide continued cooperative oversight of research plan implementation, and develop an information transfer and education program for commercial shrimp fishers and other parties affected by finfish bycatch ("information transfer"), and
develop and operate a standardized data management system for the cooperative research program
In 1993, the Foundation began placing observers aboard voluntarily participating commercial shrimp trawlers to collect fishery-dependent data concerning shrimp trawl bycatch. From 1993-1996, Foundation-contracted observers logged 2,320 days aboard trawlers, collecting information on 3,162 shrimp trawl tows. According to NMFS Galveston, the programmatic partners' pooled dataset consists of ~5700 tows, thus Foundation generated data comprises about 55% of the total. Characterization sampling by Foundation observers included 403 days in the Gulf of Mexico collecting data on 479 shrimp trawl tows, 34 days in the South Atlantic producing data for 34 tows, and an additional 14 days were logged monitoring the catch of 20 tows in the rock shrimp fishery operating off the Atlantic Florida coast. Greater effort was expended evaluating the exclusion efficiency of various bycatch reduction devices (BRDs) and turtle-excluder-devices (TEDs). Observers logged 1426 days in the Gulf of Mexico collecting data on 1696 tows examining BRDs, and 244 tows examining TEDs. In the South Atlantic, observers spent 443 days evaluating 689 BRD tows.
According to two separate NMFS analyses, over 450 and 150 taxa have been identified in trawls from the Gulf of Mexico and South Atlantic respectively; the average catch was 27 kg (~60 lb.) of biomass per hour of trawling. The bycatch to shrimp catch ratios generated by these data were in stark contrast to an often quoted ratio of 10:1. For the Gulf of Mexico, the bycatch to shrimp ratio was 5¼:1, and for the South Atlantic it was 4½:1. More importantly, the generalization of a 10:1 bycatch ratio has been often misquoted to represent the finfish to shrimp ratio when in fact, in the Gulf of Mexico the finfish to shrimp ratio was 4.2:1, and in the South Atlantic the ratio was 2.8:1.
General ecological concerns aside, bycatch reduction has a more pragmatic consequence for fishery management: alleviation of incidental mortality on heavily fished finfish stocks. For example, juveniles of a common Gulf of Mexico species (red snapper, Lutjanus campechanus) and a common South Atlantic species (weakfish, Cynoscion regalis) have been particularly identified as fishes impacted by shrimp trawling. Similar impacts are hypothesized for two other species (king mackerel, Scomboromorus cavalla, and Spanish mackerel, S. maculatus) which occur in both the Gulf of Mexico and the South Atlantic. This juvenile mortality is thought to effect recruitment to the fishable stocks, thus restricting allocations for directed recreational and commercial fishing efforts. The initial goal of the Bycatch Program was to reduce incidental mortality on these species, and others, by 50%.
To address this goal, the Foundation evaluated the exclusion efficiency of various bycatch reduction devices (BRDs) and turtle-excluder-devices (TEDs). Two general types of BRDs were tested: fisheyes (cone-shaped metal frames inserted into the codend webbing to provide an escape hole), and expanded mesh (large square- hung mesh located in the front of the codend usually encircling a funnel). Three different hard-grid TEDs were tested either against each other or against a "naked" net (net without a TED). Two soft TEDs were compared against naked nets and against each other, and one was compared against a hard TED.
Fish exclusion and shrimp retention were very dependent upon the placement and configuration of the BRD. A total of 12 different fisheye configurations were tested; some configurations were represented by minimal sample sizes and no analyses were conducted on the data. For the Gulf of Mexico, we found that only one configuration - a 5" X 12" placed 30 meshes back from the start of the codend - successfully met mortality reduction goals for red snapper by eliminating 38% of the individuals per net-hour; however there was a 6% shrimp loss associated with this gear. Other fisheye configurations reduced the number of red snapper by 20-25%, but none met the minimum 50% mortality reduction criterion. Four configurations of expanded mesh were extensively tested; three of these provided good fish exclusion, including red snapper (10-25%), without an associated shrimp loss, but only one configuration met the red snapper mortality reduction criterion. Other limited testing occurred for four other BRD concepts; none of these gears met the combined goals of shrimp retention and fish exclusion, but two of them warrant further evaluations. For the South Atlantic, none of the fisheye or expanded mesh configurations met the weakfish reduction goals during Foundation tests; however when combined with other researcher's data, the 5" X 12" fisheye at 30 meshes and the 3-bar expanded mesh BRD did exclude 40% or more of the weakfish taken per net-hour with less than a 5% difference in shrimp catch.
Most TED testing was against naked (no TED) nets in the offshore (> 15 fm) northwest Gulf of Mexico; other tests, comparing one TED to another, were conducted over a wider area. Results of these tests indicated hard-grid TEDs (Anthony Weedless, Georgia-grid, Super-Shooter, Seymore) did not contribute substantially to the reduction of finfish catch; this does not mean that they do not contribute to the mechanical exclusion of large fishes, but that they did not tend to reduce the catch of smaller fishes. Two soft TEDs (Morrison, Andrews 5") did have substantial (40-60%) total finfish exclusion capabilities; the Andrews TED excluded >70% of the red snapper, and the Morrison excluded ~25% of this species. TEDs have been mandated for several years now, and finfish mortality reductions attributable to soft TED use should be incorporated in the stock assessments for "key" species such as red snapper and weakfish, dependent upon the percent of the trawlers that have used soft TEDs over that time period.
Summary - The southeastern shrimp fishery may, in certain areas and at certain times, have an unwanted bycatch far exceeding the targeted shrimp catch. In recent years there has been a contribution to bycatch reduction by the industry through their use of TEDs, and bycatch can be further reduced through the use of BRDs. It is imperative, however, that this contribution does not also induce an economic hardship through a concurrent loss of shrimp from the catch. Otherwise, any benefits stemming from enhancement of finfish stocks would be negated by the additional burden on the shrimp industry. If this can be accomplished, in the long-run, reduction of finfish bycatch in the shrimp fishery is ecologically and economically beneficial to the southeast US fishing industry, and thus to the general public and the nation.
===================================== Steve Branstetter, Ph.D., Program Director Gulf & S. Atl. Fish. Develop. Fndn. Ste. 997, Lincoln Cntr., 5401 W. Kennedy Tampa, FL 33609 Phone 813-286-8390 FAX 813-286-8261 email: [log in to unmask]
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