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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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<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 />

when wire is not used. Higher risk of los<strong>in</strong>g target species can be<br />

an important consequence if wire use is not permitted because of<br />

deficiencies <strong>in</strong> ma<strong>in</strong>tenance of damaged monofilament l<strong>in</strong>e between<br />

sets. Prior to the ban, <strong>in</strong>stead of monofilament l<strong>in</strong>e, a short (< 1 m)<br />

length of usually multi-str<strong>and</strong> sta<strong>in</strong>less steel wire was <strong>in</strong>corporated<br />

between the hook <strong>and</strong> a swivel, beyond which the rema<strong>in</strong>der of the<br />

branchl<strong>in</strong>e extended to the ma<strong>in</strong>l<strong>in</strong>e clip.<br />

Use of wire was recently prohibited <strong>in</strong> Australia, the <strong>in</strong>tention<br />

be<strong>in</strong>g that a greater proportion of sharks caught would now escape<br />

the mono (relative to wire) which would be more likely severed.<br />

This, to a certa<strong>in</strong> extent removed the option that fishers otherwise<br />

could exercise of kill<strong>in</strong>g all sharks to reta<strong>in</strong> or to recover hooks. It<br />

is true that for a fisher who only wants to discard all sharks <strong>and</strong> is<br />

unconcerned about the extent of hook loss, mono, not wire to the<br />

hook does provide easier discard<strong>in</strong>g opportunity. But, the likelihood<br />

that many of such discards are left with long sections of mono trail<strong>in</strong>g<br />

(as well as the hook) is high. The long-term health implications<br />

of this are not fully understood although the anecdotal evidence<br />

(see survey results) is that, to a shark, such potential impediment is of<br />

little or not consequence.<br />

The majority of fishers surveyed did not consider hook recovery from<br />

sharks warranted <strong>and</strong>, if given the option they would not elect to<br />

<strong>in</strong>corporate wire. But op<strong>in</strong>ion varied with wire be<strong>in</strong>g considered<br />

an essential tool to make fish<strong>in</strong>g viable where bycatch species that<br />

are particularly destructive to fish<strong>in</strong>g gear (sharks, snake mackerel,<br />

wahoo lancet fish) are prevalent. Without wire, fishers commented<br />

that it was easier to discard sharks that are caught efficiently by cutt<strong>in</strong>g<br />

the mono near the hook, despite loss of all hooks by do<strong>in</strong>g so. This<br />

contrasts to the practice <strong>in</strong> those fisheries where despite similar shark<br />

retention <strong>and</strong> f<strong>in</strong>n<strong>in</strong>g restrictions, wire usage is still permitted. Here<br />

a common practice with wire is to use it to advantage <strong>and</strong> recover all<br />

fish<strong>in</strong>g gear, <strong>in</strong>clud<strong>in</strong>g hooks. This is made possible because, under<br />

tension (a fish on the hook) wire, unlike mono has no elasticity. A<br />

shark can therefore be more easily controlled with safety <strong>and</strong> <strong>in</strong><br />

do<strong>in</strong>g so all fish<strong>in</strong>g gear, <strong>in</strong>clud<strong>in</strong>g the hook is <strong>in</strong>variably recovered,<br />

with frequent, time-consum<strong>in</strong>g costly shark damage repairs greatly<br />

m<strong>in</strong>imized. (A high, elevated work deck on a vessel does limit this<br />

capacity, however).<br />

There is potential therefore <strong>in</strong> fisheries where the use of wire is<br />

permitted, for improvement <strong>in</strong> shark conservation although this can<br />

be reliant to a large extent on:<br />

• The existence of other measures to constra<strong>in</strong> the extent to<br />

which sharks that are caught can be reta<strong>in</strong>ed; <strong>and</strong><br />

• The attitude of <strong>in</strong>dividual fishers to sharks <strong>and</strong> the measures<br />

they choose to take to discard them when caught.<br />

An important component of this can be, as it is <strong>in</strong> Australia,<br />

the choice or not to use firearms as a rout<strong>in</strong>e method to<br />

dispatch fish prior to them be<strong>in</strong>g l<strong>and</strong>ed<br />

(see follow<strong>in</strong>g section).<br />

Additional advantages of wire are that a lead centre swivel is generally<br />

used where mono attaches to wire. As this tends to be with<strong>in</strong><br />

1 metre of the hook, l<strong>in</strong>e s<strong>in</strong>k rate to avoid seabird <strong>in</strong>teractions is<br />

optimized. Hook storage b<strong>in</strong> tangles that reduce fish<strong>in</strong>g efficiency<br />

<strong>and</strong> exacerbate bird <strong>in</strong>teraction rates are also much reduced with<br />

branch-l<strong>in</strong>e configuration of the above design.<br />

In a fishery where gear damage by fish (not only sharks) is high,<br />

average trip length <strong>and</strong> fish<strong>in</strong>g effort can also be an important<br />

<strong>in</strong>fluence on the desirability of wire use. In Australia, where average<br />

trip length is only about 4 days <strong>and</strong> daily effort around 950 hooks set<br />

(Table A1.1), the capacity to withst<strong>and</strong> substantial gear damage is<br />

much more feasible than <strong>in</strong> fisheries with considerably longer trips<br />

sett<strong>in</strong>g many more hooks. Daily gear damage can be so great, on<br />

voyages of extended duration that if fish<strong>in</strong>g effort capacity is to be<br />

ma<strong>in</strong>ta<strong>in</strong>ed throughout the trip it is more feasible to conta<strong>in</strong> damage<br />

by us<strong>in</strong>g wire rather than have enough replacement gear. Regulations<br />

that restrict the number of clips that can be carried aboard vessels<br />

<strong>in</strong> Australia also limit this as an option. (There is <strong>in</strong>sufficient time<br />

for crew to actually repair all damaged gear except on much larger<br />

vessels where sufficient crew keep pace with repair needs).<br />

A1.9. Fish<strong>in</strong>g Practices that Affect <strong>Shark</strong> Catches<br />

A1.9.1. Fish<strong>in</strong>g location<br />

It would seem that shark catch rates <strong>in</strong> the AFZ particularly of<br />

blue sharks, <strong>in</strong>crease <strong>in</strong> more southern waters. However, now it is a<br />

requirement that vessels fish<strong>in</strong>g <strong>in</strong> this region must possess a m<strong>in</strong>imum<br />

quota of Southern bluef<strong>in</strong> tuna before a longl<strong>in</strong>e is set <strong>in</strong> a specified<br />

period of the year. Few longl<strong>in</strong>e permit holders possess quota for this<br />

species. Availability <strong>and</strong> cost of quota is now prohibitive for economic<br />

longl<strong>in</strong>e efficiency, with the majority of quota now consumed on<br />

aquaculture of this species. This scenario is likely to have greatly<br />

reduced overall shark catch potential as it also has for seabird<br />

mortalities. Survival rates of more southerly, cold-water caught<br />

sharks may however be better due to reduced metabolic rate <strong>and</strong><br />

lower oxygen dem<strong>and</strong>s (Francis et al, 2001).<br />

Questionnaire respondents considered that l<strong>in</strong>e sett<strong>in</strong>g <strong>in</strong>shore (often<br />

by un<strong>in</strong>tentional l<strong>in</strong>e drift) of the cont<strong>in</strong>ental shelf break greatly<br />

<strong>in</strong>creases shark catch rates <strong>and</strong> where this is a known consequence,<br />

this region is generally avoided. As noted previously, consideration<br />

is currently be<strong>in</strong>g given to apply<strong>in</strong>g longl<strong>in</strong>e fish<strong>in</strong>g restrictions <strong>in</strong><br />

relation to waters adjacent to or over the shelf break. But, this is not<br />

be<strong>in</strong>g driven by any perceived need <strong>in</strong> relation to shark management.<br />

<strong>Shark</strong> catch rate <strong>and</strong> species composition of the catch will change<br />

because of this. Evaluat<strong>in</strong>g the extent of fish<strong>in</strong>g effort <strong>in</strong> relation to<br />

this area factor for shark <strong>in</strong>teractions, based on exist<strong>in</strong>g logbook <strong>and</strong><br />

observer fish<strong>in</strong>g position records would be of value.<br />

A1.9.2. L<strong>in</strong>e set, soak <strong>and</strong> haul duration, depth <strong>and</strong> tim<strong>in</strong>g<br />

The average number of hooks on a longl<strong>in</strong>e usually has a direct<br />

relationship to duration of l<strong>in</strong>e sett<strong>in</strong>g <strong>and</strong> haul<strong>in</strong>g. The <strong>in</strong>terval<br />

between sett<strong>in</strong>g end <strong>and</strong> haul<strong>in</strong>g, referred to as ‘the soak’, has no real<br />

relatship to fish<strong>in</strong>g effort (hooks set) <strong>in</strong> this particular fishery. But the<br />

comb<strong>in</strong>ed duration of these events can, not only alter catch rate but<br />

survival prospects for species that are discarded. Francis et al (2001)<br />

44

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