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Shark Depredation and Unwanted Bycatch in Pelagic Longline

Shark Depredation and Unwanted Bycatch in Pelagic Longline

Shark Depredation and Unwanted Bycatch in Pelagic Longline

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USA Atlantic, Gulf of Mexico <strong>and</strong> Caribbean <strong>Pelagic</strong> Longl<strong>in</strong>e Swordfish <strong>and</strong> Tuna Fisheries<br />

if encompass<strong>in</strong>g more areas, was derived for the aggregate of shark<br />

species captured <strong>in</strong> PLL operations from 1992-2000 (Beerkircher<br />

et al., 2002). As referenced, silky sharks are second only to blue<br />

sharks <strong>in</strong> the total number of catches <strong>in</strong> this fishery. However, <strong>in</strong><br />

assessments of the SAB <strong>and</strong> FEC exclusively, silky sharks were the<br />

predom<strong>in</strong>ant species taken (Beerkircher et al., 2002). Dusky <strong>and</strong><br />

night sharks also exceeded blue sharks for CPUE <strong>and</strong> overall catch<br />

numbers. Quarterly deviations <strong>in</strong> CPUE also exist for several species<br />

with silky shark catch rates the highest <strong>in</strong> the 1st <strong>and</strong> 4th quarters of<br />

the year (Table A9.5). Comparable to the aforementioned decl<strong>in</strong>es<br />

<strong>in</strong> blue shark <strong>and</strong> alternate species CPUE <strong>in</strong> recent years, these<br />

authors also report a 1992-2000 decl<strong>in</strong>e when weighed aga<strong>in</strong>st 1981<br />

to 1983 estimates taken from Berkeley <strong>and</strong> Campos (1988) (Table<br />

A9.6). These downward trends may reflect shifts <strong>in</strong> abundance but<br />

could also be <strong>in</strong>dicative of spatial <strong>and</strong> gear factors that have served to<br />

reduce catchability (Beerkircher et al., 2002).<br />

Based on the catch disposition figures derived by Hoey <strong>and</strong> Moore<br />

(1999), rank<strong>in</strong>gs of the highest weight of shark species caught by area<br />

have been tabulated (Table A9.7). Greater resolution of these rank<strong>in</strong>gs<br />

reveals that apart from the MAB, NEC <strong>and</strong> NED, a shark species or<br />

group never exceeded 100,000 pounds <strong>in</strong> a given area dur<strong>in</strong>g the<br />

collective years covered <strong>in</strong> the report (1990-1997). In over half of the<br />

areas, the most captured shark by weight didn’t exceed ~ 20,000 lbs.<br />

Because <strong>in</strong> rare <strong>in</strong>stances, disproportionately high numbers of sharks<br />

were caught when fishermen shifted to directed shark fish<strong>in</strong>g (Hoey <strong>and</strong><br />

Moore, 1999), the degree of shark bycatch (exclud<strong>in</strong>g shortf<strong>in</strong> makos)<br />

was likely even lower than the figures allude. However, the magnitude<br />

of overall catch weight, data only representative of when observers<br />

were present, is secondary. What is most germane is that fish<strong>in</strong>g <strong>in</strong><br />

certa<strong>in</strong> regions will lead to <strong>in</strong>creased shark encounters. Moreover,<br />

despite constitut<strong>in</strong>g the primary aggregate of bycatch species <strong>in</strong> the<br />

PLL fishery (e.g. Beerkircher et al., 2002), shark catches aside from<br />

those of blue sharks, do not appear exorbitantly high <strong>in</strong> U.S. domestic<br />

operations; at least when compared to the catches by foreign fleets.<br />

A9.2.3. <strong>Shark</strong> depredation<br />

In addition to be<strong>in</strong>g captured as bycatch, sharks are also responsible<br />

for remov<strong>in</strong>g baits <strong>and</strong> gear (bite-offs) <strong>and</strong> <strong>in</strong>flict<strong>in</strong>g damage upon<br />

other catch already hooked <strong>and</strong> thus less able to avoid predation.<br />

<strong>Depredation</strong> thus represents a major nuisance to fishermen. To the<br />

detriment of <strong>in</strong>dustry, POP data <strong>in</strong>dicates that of all damage between<br />

1990 <strong>and</strong> 1997 (4% of total observed catch), 68% occurred on catches<br />

of swordfish, yellowf<strong>in</strong> <strong>and</strong> bigeye tuna collectively (Hoey <strong>and</strong> Moore,<br />

1999). Although damaged catch has been reported <strong>in</strong> assessments<br />

of catch disposition by several authors (e.g. Hoey <strong>and</strong> Moore, 1999;<br />

Beerkircher et al., 2004; Diaz, 2006; Kerstetter <strong>and</strong> Graves, 2006B), the<br />

available data are not usually resolvable to a level where possible to<br />

def<strong>in</strong>itively identify the depredat<strong>in</strong>g species (Lawrence Beerkircher,<br />

personal communication). The po<strong>in</strong>t of <strong>in</strong>teraction is rarely observed<br />

to enable positive identification. In addition to sharks, cetaceans<br />

(Hoey <strong>and</strong> Moore, 1999) are also responsible for damag<strong>in</strong>g catch <strong>and</strong><br />

pilfer<strong>in</strong>g baits <strong>and</strong> gear. In fact, depredation by mar<strong>in</strong>e mammals<br />

could equal or even exceed that done by sharks <strong>in</strong> certa<strong>in</strong> areas such<br />

as the MAB (Lawrence Beerkircher, personal communication). To<br />

facilitate the ability to dist<strong>in</strong>guish between the depredat<strong>in</strong>g species,<br />

NMFS is implement<strong>in</strong>g a new data collection protocol requir<strong>in</strong>g more<br />

comprehensive report<strong>in</strong>g details <strong>in</strong> early 2007 (Lawrence Beerkircher,<br />

personal communication). However, even if able to dist<strong>in</strong>guish<br />

between damage done by sharks <strong>and</strong> other animals, <strong>in</strong>terspecific<br />

identification of the depredat<strong>in</strong>g animal will likely rema<strong>in</strong> impossible.<br />

If such data are deemed as important, account<strong>in</strong>g for auxiliary<br />

factors such as the CPUE, abundance, distribution, <strong>and</strong> behavioral<br />

tendencies of potentially depredat<strong>in</strong>g species may strengthen the<br />

ability to identify the source species.<br />

Importantly, depredations on target or alternative catch may not<br />

always be accounted for. In cases where soak times are protracted,<br />

animals that die or are weakened from stressors experienced<br />

while hooked are much easier targets for scaveng<strong>in</strong>g species such<br />

as blue sharks (Ward et al., 2004). Thus, reduc<strong>in</strong>g soak-times is a<br />

straightforward method that could possibly mitigate both shark<br />

catch rates <strong>and</strong> depredation.<br />

A9.3. Potential Strategies to Reduce <strong>Shark</strong><br />

Interactions <strong>and</strong> Mortality<br />

A9.3.1. That related to other taxa or fisheries<br />

A comprehensive Atlantic PLL Take Reduction Plan (APLTRP)<br />

was recently submitted to NOAA (2006). Although not directly<br />

addressed, it is conceivable that some of the measures <strong>in</strong>tended by<br />

the Take Reduction Team (TRT) to reduce the number of serious<br />

<strong>in</strong>jury <strong>in</strong>teractions with pilot whales <strong>and</strong> Risso’s dolph<strong>in</strong>s could also<br />

be successfully applied to sharks. The applicable proposals described<br />

<strong>in</strong> the APLTRP <strong>in</strong>clude proper h<strong>and</strong>l<strong>in</strong>g protocols; m<strong>and</strong>atory<br />

ma<strong>in</strong>l<strong>in</strong>e, gear <strong>and</strong> bait requirements to be discussed <strong>in</strong> greater detail<br />

shortly; <strong>and</strong> additional time-area closures.<br />

There are also exist<strong>in</strong>g regulations apply<strong>in</strong>g to the Atlantic <strong>and</strong> GOM<br />

bottom longl<strong>in</strong>e fishery that may be effective tools <strong>in</strong> <strong>in</strong>creas<strong>in</strong>g<br />

post-release survival for sharks taken by PLL (APLTRT, 2006). These<br />

<strong>in</strong>clude the rapid release of non-reta<strong>in</strong>ed species with an immediate<br />

retrieval of gear rema<strong>in</strong><strong>in</strong>g deployed; the use of l<strong>in</strong>e-cutters <strong>and</strong><br />

dip-nets for release purposes; <strong>and</strong> the ma<strong>in</strong>tenance of seawater flow<br />

across the gills (as must be ma<strong>in</strong>ta<strong>in</strong>ed <strong>in</strong> sawfish caught by bottom<br />

longl<strong>in</strong>e). However, these should be viewed as techniques that could<br />

potentially reduce the detrimental effects from, rather then the rates<br />

of, <strong>in</strong>teractions.<br />

A9.3.2. That related to pelagic operations<br />

POP data, as previously reported upon by Hoey <strong>and</strong> Moore (1999),<br />

have revealed sets yield<strong>in</strong>g disproportionately high shark catches.<br />

In some <strong>in</strong>stances, PLL fishermen have reportedly altered operative<br />

strategies <strong>in</strong> order to l<strong>and</strong> <strong>in</strong>creased numbers of sharks. Alternatively,<br />

a particular set of conditions may translate <strong>in</strong>to higher catch rates.<br />

Independent of whether or not <strong>in</strong>tended however, these particular<br />

sets can be analyzed for environmental <strong>and</strong> operative factors that<br />

may have contributed to the higher catch rates. Account<strong>in</strong>g for such<br />

variables could prove beneficial to <strong>in</strong>dustry if deriv<strong>in</strong>g measures to<br />

help circumvent high numbers of shark <strong>in</strong>teractions, or to enhance<br />

survivorship of discards.<br />

143

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