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Shark Depredation and Unwanted Bycatch in Pelagic Longline

Shark Depredation and Unwanted Bycatch in Pelagic Longline

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<strong>Shark</strong> <strong>Depredation</strong> <strong>and</strong> <strong>Unwanted</strong> <strong>Bycatch</strong> <strong>in</strong> <strong>Pelagic</strong> Longl<strong>in</strong>e Fisheries<br />

A7.5.2. Perception of <strong>in</strong>terviewees<br />

Skippers <strong>in</strong>terviewed were of the op<strong>in</strong>ion that they catch 10 to 20<br />

sharks or between 100 <strong>and</strong> 300 kg of sharks per set. Most felt the blue<br />

shark was the most commonly caught at a rate of up to 15 blue sharks<br />

(or 200 kg) per set. They usually reta<strong>in</strong> most blue sharks (with<strong>in</strong> the<br />

regulations). They report that blue sharks are usually hauled aboard<br />

alive, but die if they become badly entangled <strong>in</strong> their gear. Most felt<br />

that this capture had no effect on the species, however one skipper<br />

felt that the capture of blue sharks was dramatically threaten<strong>in</strong>g the<br />

species. The second most common species caught <strong>in</strong> their op<strong>in</strong>ion<br />

was the short-f<strong>in</strong> mako shark. Up to 10 makos are caught per set <strong>and</strong><br />

this comprises approximately 20 to 100 kg. They usually reta<strong>in</strong> all<br />

makos (aga<strong>in</strong> with<strong>in</strong> the regulations). The economic value of makos<br />

is higher than for blue sharks <strong>and</strong> thus reta<strong>in</strong>ed more frequently.<br />

Most makos are alive on capture, but a portion of them are dead.<br />

Most felt that this capture had no effect on the species, however the<br />

same skipper as above felt that the capture of makos was dramatically<br />

threaten<strong>in</strong>g the species. Two of the skippers <strong>in</strong>terviewed felt that<br />

shark bycatch was not caus<strong>in</strong>g any economic loss to the fishery. Three<br />

felt it was caus<strong>in</strong>g economic loss due to loss of bait <strong>and</strong> time. The<br />

rema<strong>in</strong><strong>in</strong>g did not know. Only half said that they submitted their<br />

shark catches <strong>in</strong> their logbook records.<br />

A7.6. Management Framework Relevant to <strong>Shark</strong><br />

Interactions<br />

At present there are no accepted mitigation measures for reduc<strong>in</strong>g<br />

shark bycatch <strong>and</strong> this requires <strong>in</strong>vestigation. South Africa has a<br />

draft NPOA-sharks, but this has not yet been adopted. However, <strong>in</strong><br />

order to address mount<strong>in</strong>g <strong>in</strong>ternational concern for high levels of<br />

shark bycatch, Mar<strong>in</strong>e <strong>and</strong> Coastal Management, Department of<br />

Environmental Affairs <strong>and</strong> Tourism, South African Government,<br />

have planned to close the pelagic sector of the shark-directed<br />

longl<strong>in</strong>e fishery <strong>and</strong> place a 10% shark bycatch limit on the tuna <strong>and</strong><br />

swordfish fishery. S<strong>in</strong>ce 2005 this fishery has been divided <strong>in</strong>to those<br />

target<strong>in</strong>g swordfish <strong>and</strong> those target<strong>in</strong>g tunas. Individuals with a<br />

swordfish permit may only l<strong>and</strong> sharks up to a maximum of 10%<br />

of their swordfish <strong>and</strong> tuna catch. Individuals with a tuna permit<br />

may only l<strong>and</strong> sharks up to a maximum of 10% of their tuna catch.<br />

Currently shark bycatch accounts for approximately 18% or 25% of<br />

the directed catch (Table A7.4). This is substantially larger than the<br />

suggested 10%, thus many of these shark species will be released or<br />

discarded. S<strong>in</strong>ce we have no estimate of post-release survival nor<br />

adequate <strong>in</strong>formation on the percentage of species hauled alive, this<br />

may not be sufficient to address mount<strong>in</strong>g concerns.<br />

<strong>Shark</strong> f<strong>in</strong>n<strong>in</strong>g regulations came <strong>in</strong>to effect <strong>in</strong> South Africa <strong>in</strong> 1998<br />

under the Mar<strong>in</strong>e Liv<strong>in</strong>g Resource Act of 1998 (MLRA, 1998).<br />

Regulations formed under this act banned f<strong>in</strong>n<strong>in</strong>g. The South<br />

African experimental pelagic longl<strong>in</strong>e fishery only commenced <strong>in</strong><br />

1997 <strong>and</strong> thus very little <strong>in</strong>formation exists on f<strong>in</strong>n<strong>in</strong>g practices <strong>in</strong><br />

this fishery. Under this regulation sharks were supposed to be l<strong>and</strong>ed<br />

whole, which would mean that no f<strong>in</strong>n<strong>in</strong>g was allowed. However,<br />

fishers compla<strong>in</strong>ed that it was impractical to l<strong>and</strong> sharks whole.<br />

Mar<strong>in</strong>e & Coastal Management gave concession for fishers to l<strong>and</strong><br />

the f<strong>in</strong>s with the correspond<strong>in</strong>g trunks, but this was not enforced<br />

as result sharks were def<strong>in</strong>itely f<strong>in</strong>ned dur<strong>in</strong>g this time. A 5% f<strong>in</strong> to<br />

carcass ratio was <strong>in</strong>troduced last year (2005) <strong>in</strong> an attempt to stop<br />

f<strong>in</strong>n<strong>in</strong>g Further regulations prohibit the use of a wire trace to limit<br />

the retention of shark catches <strong>in</strong> this fishery.<br />

A7.7. Economic, Social <strong>and</strong> Ecological Effects,<br />

Includ<strong>in</strong>g Effects on Fish<strong>in</strong>g Practices, from<br />

Regulations Govern<strong>in</strong>g <strong>Shark</strong> Interactions<br />

The total amount <strong>and</strong> condition of sharks l<strong>and</strong>ed is limited by the<br />

regulations discussed above. Most of the fishers that were <strong>in</strong>terviewed<br />

felt that the 10% regulation was hard to comply with because it doesn’t<br />

reflect the reality. In many cases they catch more than their 10% <strong>and</strong><br />

are thus forced to dump or discard dead sharks (Table 4). They felt it<br />

is also problematic because it results <strong>in</strong> the underreport<strong>in</strong>g of shark<br />

catches. Three <strong>in</strong>terviewees said that this regulation had m<strong>in</strong>imal<br />

economic impact on them, two said that it caused great economic<br />

loss, but was unable to quantify <strong>and</strong> the rema<strong>in</strong><strong>in</strong>g didn’t know.<br />

When revenue is acquired from f<strong>in</strong>n<strong>in</strong>g this typically goes to the<br />

crew <strong>and</strong>/or skipper. In some cases these vessels are owner-operator<br />

<strong>and</strong> thus revenue is accrued to the company. One skipper reported<br />

that they don’t f<strong>in</strong> at all on his vessel because he doesn’t approve of<br />

the practice. The crew occasionally will reta<strong>in</strong> the jaw of large makos.<br />

This will be dried <strong>and</strong> sold for their own revenue.<br />

Most felt that f<strong>in</strong>n<strong>in</strong>g regulations were effective. 60% felt that if<br />

there were no regulation regard<strong>in</strong>g f<strong>in</strong>n<strong>in</strong>g then the practise would<br />

threaten the status of shark populations. S<strong>in</strong>ce the 10% regulation<br />

has been adopted they now only reta<strong>in</strong> 10%, whereas before they<br />

would possibly have reta<strong>in</strong>ed more depend<strong>in</strong>g on space availability,<br />

current prices etc.<br />

They all said that they have altered their fish<strong>in</strong>g practices s<strong>in</strong>ce the<br />

regulations have been adopted. Before the adoption of the f<strong>in</strong>n<strong>in</strong>g<br />

regulations they would f<strong>in</strong> <strong>and</strong> dump most carcasses with the<br />

exception of makos which were reta<strong>in</strong>ed for their flesh.<br />

A7.8. Practices to Deal with Caught <strong>Shark</strong>s<br />

Most skippers <strong>in</strong>terviewed try to br<strong>in</strong>g the shark alongside the vessel,<br />

then cut the l<strong>in</strong>e as short as possible <strong>and</strong> release the shark with the<br />

hook <strong>in</strong> its mouth. Many however will go to great lengths to retrieve<br />

their hook often at the expense of the shark. If the shark is small<br />

enough then they will l<strong>and</strong> it, de-hook <strong>and</strong> release or discard. A dehooker<br />

is never used ma<strong>in</strong>ly because they don’t have one onboard<br />

<strong>and</strong> thus have never tried to use one. The decision as to whether they<br />

will reta<strong>in</strong> or discard is usually based on the follow<strong>in</strong>g: a) its size i.e. if<br />

it is too small they will usually discard, b) if their target catch is good<br />

they will discard (i.e. limited space availability) <strong>and</strong> c) regulations<br />

restrict<strong>in</strong>g them to 10% of their target catch. One <strong>in</strong>terviewee was<br />

concerned about the safety of his crew <strong>and</strong> thus did not l<strong>and</strong> large,<br />

live sharks. Product contam<strong>in</strong>ation was also a concern for half of the<br />

skippers <strong>in</strong>terviewed.<br />

118

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