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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 />

were provided on the life status of sharks caught subsequent to the<br />

1991 requirement that for f<strong>in</strong>n<strong>in</strong>g to be practiced, the whole carcass<br />

had to be reta<strong>in</strong>ed. If, as is reported, the 1991 requirement ‘effectively<br />

prevented them (the vessels) from reta<strong>in</strong><strong>in</strong>g shark f<strong>in</strong>s whilst <strong>in</strong><br />

Australian waters’, then the high survival prospects (Moyes et al<br />

2006) of post release sharks would obviously have contributed to<br />

there hav<strong>in</strong>g been no apparent trend <strong>in</strong> abundance as a consequence<br />

of fishery impact (based on observed catch rate data <strong>in</strong> the five<br />

years subsequent to 1991). And <strong>in</strong> New Zeal<strong>and</strong> where similar<br />

amounts of the same species were be<strong>in</strong>g caught <strong>and</strong> actually<br />

processed for their f<strong>in</strong>s throughout the 10-year period, impact<br />

of this is thought to not have had a serious effect on shark stocks<br />

(Francis et al 2001). Over a period of approximately 10 years (1990s)<br />

Australia’s domestic longl<strong>in</strong>e fishery had the unrestricted option<br />

of utiliz<strong>in</strong>g all sharks, even just for their f<strong>in</strong>s. Whether this has<br />

had any bear<strong>in</strong>g upon present day shark catch rates is not known.<br />

Five species, great white, grey nurse, megamouth, green sawfish <strong>and</strong><br />

Herbert’s nurse shark are prohibited take <strong>and</strong> of these there have<br />

been 5 grey nurse <strong>and</strong> one great white <strong>in</strong>teraction recorded <strong>in</strong> pelagic<br />

longl<strong>in</strong>e fisheries <strong>in</strong> Australia.<br />

A1.6. Influence of International Initiatives<br />

on Domestic <strong>Shark</strong> Management<br />

Various <strong>in</strong>ternational fisheries management <strong>in</strong>itiatives have been<br />

<strong>in</strong>fluential or <strong>in</strong>strumental <strong>in</strong> subsequent national <strong>in</strong>itiatives<br />

<strong>in</strong> Australia for improved fisheries management, <strong>in</strong>clud<strong>in</strong>g the<br />

management of shark bycatch. For example, the United Nations Food<br />

<strong>and</strong> Agriculture Organization produced the ‘Code of Conduct for<br />

Responsible Fish<strong>in</strong>g’. In 1999, Australia ratified the United Nations<br />

Agreement for the Conservation <strong>and</strong> Management of Straddl<strong>in</strong>g<br />

Fish Stocks <strong>and</strong> Highly Migratory Fish Stocks, <strong>and</strong> became a party to<br />

the United Nations Convention on the Law of the Sea. Australia is<br />

a signatory to the Convention on International Trade <strong>in</strong> Endangered<br />

Species (CITES), which can mean an obligation <strong>in</strong> relation to particular<br />

shark species. Australia has produced a <strong>Shark</strong> Assessment Report<br />

(SAR), a requirement of member nations <strong>in</strong> response to the Food <strong>and</strong><br />

Agriculture Organization of the United Nation’s International Plan of<br />

Action on sharks. The SAR identifies conservation <strong>and</strong> management<br />

issues associated with shark catch, the most significant of which<br />

are those <strong>in</strong>clud<strong>in</strong>g target, by product <strong>and</strong> bycatch. There were 24<br />

priority requirements identified. They <strong>in</strong>cluded better record<strong>in</strong>g<br />

of all shark catches, protection of species with poor conservation<br />

status, cross jurisdictional management of stocks, national controls<br />

on shark f<strong>in</strong>n<strong>in</strong>g, the need to develop shark bycatch reduction<br />

methods, h<strong>and</strong>l<strong>in</strong>g practices of returned catch, ecosystem effects of<br />

shark management practices (specifically trophic cascade), impact of<br />

<strong>in</strong>creased shark populations, impact of prey removal <strong>and</strong> the impact<br />

of market dem<strong>and</strong> on shark populations. Australia’s management of<br />

the practice of shark f<strong>in</strong>n<strong>in</strong>g is also consistent with its obligation to the<br />

United Nations Food <strong>and</strong> Agriculture Organizations Code of Conduct<br />

for Responsible Fisheries to fully utilize bycatch <strong>and</strong> by product species.<br />

This practice is reiterated to signatory nations to the FAO IPOA<br />

sharks, <strong>in</strong> that <strong>in</strong>cidental shark capture should not result <strong>in</strong> waste, <strong>and</strong><br />

capture of non-utilized species should be m<strong>in</strong>imized. Australia is also<br />

a member of Regional Fisheries Management Organizations such as<br />

the Indian Ocean Tuna Commission (IOTC) <strong>and</strong> the Commission for<br />

the Conservation of Southern Bluef<strong>in</strong> Tuna (CCSBT) under which<br />

shark bycatch management specifically can be further addressed. For<br />

<strong>in</strong>stance, with<strong>in</strong> such processes, Australia entered <strong>in</strong>to a Bilateral <strong>Shark</strong><br />

<strong>Bycatch</strong> Code of Practice agreement with Japan, the objective be<strong>in</strong>g to<br />

ensure all sharks taken are either: released alive <strong>and</strong> undamaged (i.e.<br />

not mutilated or cut prior to release), or reta<strong>in</strong>ed whole, not just f<strong>in</strong>s<br />

<strong>and</strong> killed first before be<strong>in</strong>g processed.<br />

A1.7. National Management Processes<br />

for <strong>Shark</strong>s <strong>in</strong> Australia<br />

Commonwealth fisheries bycatch is managed by several procedures<br />

such as by a direction <strong>and</strong>/or a specific <strong>in</strong>clusion with<strong>in</strong> a statutory<br />

Management Plan, as a condition or a bycatch regulation prescription<br />

of a fish<strong>in</strong>g permit, through an urgent temporary order or as a<br />

prohibition aga<strong>in</strong>st the take of a particular species <strong>in</strong> the Fisheries Act.<br />

Increas<strong>in</strong>g catches of sharks <strong>and</strong> the <strong>in</strong>herently low productivity<br />

of sharks are the reasons for concern, not just <strong>in</strong> Australia but also<br />

worldwide for populations of some shark species. But, the relatively<br />

low market value of sharks is considered to have been the reason<br />

why few countries have managed shark catch <strong>in</strong> the past (SAG <strong>and</strong><br />

Lack, 2004). Without appropriate management <strong>in</strong> place to prevent<br />

or at least conta<strong>in</strong> <strong>in</strong>creased exploitation potential, today’s bycatch<br />

(discarded sharks) can become a by-product tomorrow as determ<strong>in</strong>ed<br />

by a chang<strong>in</strong>g market dem<strong>and</strong>. From a scientific perspective,<br />

management of pelagic sharks is complicated by the unknown<br />

effects on the oceanic ecosystems of remov<strong>in</strong>g large number of these<br />

top predators. Also, because sharks have historically been of low<br />

economic value <strong>in</strong> most countries, data quality has been poor.<br />

The above situation precipitated development of the International<br />

Plan of Action for the Conservation <strong>and</strong> Management of <strong>Shark</strong>s (FAO<br />

1999), to which Australia responded by establish<strong>in</strong>g a <strong>Shark</strong> Advisory<br />

Group <strong>in</strong> 2000 for the purpose of develop<strong>in</strong>g a shark assessment<br />

report which was released <strong>in</strong> 2001 (Rose <strong>and</strong> SAG 2001). This<br />

report highlighted the necessity for development of an Australian<br />

<strong>Shark</strong>-plan (SAG <strong>and</strong> Lack 2004) ‘to ensure the conservation <strong>and</strong><br />

management of shark resources <strong>and</strong> their ecologically susta<strong>in</strong>able<br />

use’. Specifically related to fisheries impacts, the ma<strong>in</strong> objectives<br />

of the plan were to ensure susta<strong>in</strong>ability of target <strong>and</strong> non-target<br />

catches, to m<strong>in</strong>imize <strong>in</strong>cidental catches of sharks that are not be<strong>in</strong>g<br />

utilized <strong>and</strong> for those that are utilized, m<strong>in</strong>imize waste such as when<br />

f<strong>in</strong>s only from the shark are reta<strong>in</strong>ed, <strong>in</strong> accordance with article 7.2.2<br />

of the Code of Conduct for Responsible Fish<strong>in</strong>g (FAO 1995). The<br />

NPOA–sharks provides a guide to <strong>in</strong>corporat<strong>in</strong>g shark conservation<br />

<strong>and</strong> management issues <strong>in</strong>to the various fisheries management plans.<br />

It recommends exam<strong>in</strong><strong>in</strong>g the methods used to manage <strong>and</strong> reduce<br />

shark by-catch.<br />

The pelagic longl<strong>in</strong>e fishery was identified as a potential source of<br />

significant shark catches <strong>and</strong> attempts have been made to evaluate<br />

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