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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 />

abundant pelagic shark <strong>in</strong> the Northwest Atlantic (Simpfendorfer<br />

et al., 2002). The species reportedly comprises 50% of the universal<br />

Northwest Atlantic PLL bycatch, a group of species not comprised<br />

exclusively of sharks (Crowder <strong>and</strong> Myers, 2001). A virtually<br />

unwanted species <strong>in</strong> tuna <strong>and</strong> swordfish operations, blue shark<br />

discards peaked at an estimated 29,000 <strong>in</strong>dividuals <strong>in</strong> 1993 (NMFS,<br />

2006). As of 2000, predicted annual discards for the species were set<br />

at 1,575 metric tons (mt) based on POP data (Harr<strong>in</strong>gton et al., 2005).<br />

In comparison, silky shark discards (mt) were predicted to be (163);<br />

dusky (113); s<strong>and</strong>bar (40); bigeye thresher shark (39); <strong>and</strong> Sphyrna<br />

lew<strong>in</strong>i (scalloped hammerhead) (32) (Harr<strong>in</strong>gton et al., 2005). In an<br />

analysis by Hoey <strong>and</strong> Moore (1999) of the POP data spann<strong>in</strong>g 1990-<br />

1997, the follow<strong>in</strong>g positively identified shark species were captured<br />

<strong>in</strong> descend<strong>in</strong>g order by number while exclud<strong>in</strong>g all other factors:<br />

blue (19,264); silky (1,905); mako (1,726); dusky (1,122); hammerhead<br />

(multiple sp., 725); tiger (351); common thresher (348); s<strong>and</strong>bar<br />

(333); oceanic whitetip (262); Carcharh<strong>in</strong>us limbatus (blacktip) (92);<br />

<strong>and</strong> porbeagle (45). When tak<strong>in</strong>g <strong>in</strong>to account the relative scarcity<br />

of blue sharks <strong>in</strong> more Southern tropical fish<strong>in</strong>g zones (e.g. GOM),<br />

the magnitude of these disparities highlights both the comparative<br />

dom<strong>in</strong>ance of blue versus other shark species as bycatch <strong>in</strong> this<br />

fishery, <strong>and</strong> the disproportionate numbers of blue sharks taken <strong>in</strong><br />

their prevalent take zones.<br />

It has been reported that Canadian observers may only be<br />

document<strong>in</strong>g blue shark catches brought on deck, a predicament<br />

not account<strong>in</strong>g for the leader bite-offs prior to board<strong>in</strong>g (DFO, 2002;<br />

Campana et al., 2005). Thus, blue shark catches may also be grossly<br />

underreported <strong>in</strong> that fishery, an outcome not implausible for the<br />

U.S domestic fishery as well. However, this species appears quite<br />

resilient to the rigors of longl<strong>in</strong>e capture. Low board<strong>in</strong>g (at-vessel)<br />

blue shark mortality has been observed, where dependent upon the<br />

study, 7-19% of the all blue shark discards were deemed alive at the<br />

time of release (e.g. Cramer 1997C; Campana et al., 2005). Logbook<br />

data have reported an oscillat<strong>in</strong>g but nevertheless decl<strong>in</strong><strong>in</strong>g trend <strong>in</strong><br />

blue shark catch numbers dur<strong>in</strong>g recent years (Crowder <strong>and</strong> Myers,<br />

2001; NMFS, 2006). Thus, <strong>in</strong> studies equat<strong>in</strong>g catchability (CPUE)<br />

with <strong>in</strong>dices of abundance, Atlantic blue sharks are among those<br />

species reported to have undergone considerable population decl<strong>in</strong>es<br />

(Baum et al., 2003). In accordance with previous arguments aga<strong>in</strong>st<br />

treat<strong>in</strong>g CPUE as an <strong>in</strong>dex of abundance (Cooke <strong>and</strong> Bedd<strong>in</strong>gton,<br />

1984), the extent of the reported blue shark decl<strong>in</strong>e (~60% s<strong>in</strong>ce<br />

1986) postulated by Baum et al. (2003) has been questioned by<br />

several authors (e.g. Campana et al., 2005) on the basis that potential<br />

reasons for drops <strong>in</strong> CPUE aside from abundance decl<strong>in</strong>es were<br />

not accounted for. It is acknowledged, however, that the species has<br />

likely endured some level of decl<strong>in</strong>e <strong>in</strong> recent years (Brooks et al.,<br />

2005; Campana et al., 2006). Consider<strong>in</strong>g its comparatively high<br />

fecundity <strong>in</strong> relation to most other sharks, even a m<strong>in</strong>imal decl<strong>in</strong>e<br />

would suggest that blue sharks, even if released alive, may be dy<strong>in</strong>g<br />

at a higher rate follow<strong>in</strong>g PLL capture <strong>and</strong> discard than presumed.<br />

If the supposition is true that virtually all blue sharks are discarded<br />

alive with a high ultimate rate of survivability, the decl<strong>in</strong>es <strong>in</strong><br />

abundance surmised by certa<strong>in</strong> authors would only be conceivable<br />

due to a climb <strong>in</strong> natural mortality or an <strong>in</strong>crease <strong>in</strong> l<strong>and</strong><strong>in</strong>gs of the<br />

species by non-U.S fleets <strong>in</strong> N. Atlantic high seas fisheries. This area<br />

warrants further <strong>in</strong>vestigation.<br />

Table A9.3. <strong>Shark</strong> species compris<strong>in</strong>g U.S. Atlantic (domestic) management<br />

units (Bonfil, 1994).<br />

Large Coastal <strong>Shark</strong>s<br />

Small Coastal <strong>Shark</strong>s<br />

FAO Common<br />

Name<br />

S<strong>and</strong>bar<br />

Blacktip<br />

Dusky<br />

Sp<strong>in</strong>ner<br />

Silky<br />

Bull<br />

Bignose<br />

Copper<br />

Galapagos<br />

Night<br />

Caribbean reef<br />

Tiger<br />

Lemon<br />

S<strong>and</strong>tiger<br />

Bigeye s<strong>and</strong> tiger<br />

Nurse<br />

Scalloped<br />

hammerhead<br />

Great hammerhead<br />

Smooth hammerhead<br />

Whale<br />

Bask<strong>in</strong>g<br />

Great White<br />

Atlantic sharpnose<br />

Carribbean sharpnose<br />

F<strong>in</strong>etooth<br />

Blacknose<br />

Smalltail<br />

Bonnethead<br />

S<strong>and</strong> devil<br />

Scientific Name<br />

Carcharh<strong>in</strong>us<br />

plumbeus<br />

Carcharh<strong>in</strong>us limbatus<br />

Carcharh<strong>in</strong>us obscurus<br />

Carcharh<strong>in</strong>us<br />

brevip<strong>in</strong>na<br />

Carcharh<strong>in</strong>us<br />

falciformis<br />

Carcharh<strong>in</strong>us leucas<br />

Carcharh<strong>in</strong>us altimus<br />

Carcharh<strong>in</strong>us<br />

brachyurus<br />

Carcharh<strong>in</strong>us<br />

galapagensis<br />

Carcharh<strong>in</strong>us signatus<br />

Carcharh<strong>in</strong>us perezi<br />

Galeocerdo cuvier<br />

Negaprion brevirostris<br />

Carcharias taurus<br />

Odontaspis noronhai<br />

G<strong>in</strong>glymostoma<br />

cirratum<br />

Sphyrna lew<strong>in</strong>i<br />

Sphyrna mokarran<br />

Sphyrna zygaena<br />

Rh<strong>in</strong>codon typus<br />

Cetorh<strong>in</strong>us maximus<br />

Carcharodon<br />

carcharias<br />

Rhizoprionodon<br />

terraenovae<br />

Rhizoprionodon<br />

porosus<br />

Carcharh<strong>in</strong>us isodon<br />

Carcharh<strong>in</strong>us<br />

acronotus<br />

Carcharh<strong>in</strong>us porosus<br />

Sphyrna tiburo<br />

Squat<strong>in</strong>a dumeril<br />

<strong>Pelagic</strong> <strong>Shark</strong>s Shortf<strong>in</strong> mako Isurus oxyr<strong>in</strong>chus<br />

Longf<strong>in</strong> mako<br />

Porbeagle<br />

Thresher<br />

Bigeye thresher<br />

Blue<br />

Oceanic whitetip<br />

Sharpnose sevengill<br />

Bluntnose sixgill<br />

Bigeye sixgill<br />

Isurus paucus<br />

Lamna nasus<br />

Alopias vulp<strong>in</strong>us<br />

Alopias superciliosus<br />

Prionace glauca<br />

Carcharh<strong>in</strong>us<br />

longimanus<br />

Heptranchias perlo<br />

Hexanchus griseus<br />

Hexanchus vitulus<br />

137

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