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Aquatic Environment and Biodiversity Annual Review 2012

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AEBAR <strong>2012</strong>: Non-protected bycatch<br />

6.3.8. Scampi trawl fishery<br />

In the most recent study, covering the period 1990–91 to 2009–10, the ratio estimator used to<br />

calculate bycatch <strong>and</strong> discard rates in the scampi fishery was based on the number of trawls. Linear<br />

mixed-effect models (LMEs) identified fishery area as the key variable influencing bycatch rates <strong>and</strong><br />

discard rates.<br />

The key categories of catch/discards examined were; all QMS species combined, all non-QMS<br />

species combined, all invertebrate species combined, javelinfish, <strong>and</strong> all other rattail species<br />

combined.<br />

Observer coverage in the scampi fishery has been relatively low compared with most of the other<br />

fisheries assessed. The long-term level of observer coverage in the orange roughy, oreo, arrow squid,<br />

southern blue whiting, <strong>and</strong> ling longline fisheries is greater than 18% of the target fishery catch (<strong>and</strong><br />

over 40% for southern blue whiting) whereas in the scampi fishery (<strong>and</strong> also in the jack mackerel<br />

fishery) long-term coverage has only been about 11–12%. However, annual coverage in the scampi<br />

fishery was greater than 10% in most years <strong>and</strong> fell below 5% only once (in 2000–01).<br />

The annual number of observed trawls in the fishery ranged from 142 to 797, but has been over 300<br />

trawls in most years. The number of vessels observed in each year ranged from 3 to 8 (equivalent to<br />

33–66% of the fleet) <strong>and</strong> was very constant—5 or 6 vessels in most years. Analysis of the spread of<br />

observer effort compared with that of the scampi fishery as a whole, across a range of variables,<br />

indicated that this coverage was reasonably well spread. Although some less important regions of the<br />

fishery received little or no coverage (e.g. the central Chatham Rise, where commercial scampi<br />

fishing has only recently developed, <strong>and</strong> west coast South Isl<strong>and</strong>), the main scampi fisheries were<br />

consistently sampled throughout the period examined. Vessels were mostly of a similar size, <strong>and</strong> the<br />

small amount of effort by larger vessels was adequately covered, as was the full depth range of the<br />

fishery <strong>and</strong> (despite highly intermittent sampling in several years) all periods of the year.<br />

Over 450 bycatch species or species groups were observed in the scampi target fishery catch, most<br />

being non-commercial species, including invertebrate species, caught in low numbers. Scampi<br />

accounted for only about 17% of the total estimated catch from all observed trawls targeting scampi<br />

since 1 October 1990. The main bycatch species or species groups were javelinfish (16%), other<br />

(unidentified) rattails (13%), sea perch (Helicolenus spp., 8.4%), ling (7.5%), <strong>and</strong> hoki (6.1%). The<br />

first three of these bycatch groups were mostly discarded (Figure 6.17). Of the other invertebrate<br />

groups, unidentified crabs (1.1%) <strong>and</strong> unidentified starfish (0.8%) were caught in the greatest<br />

amounts. When combined into broader taxonomic groups, bony fish (excluding rattails) contributed<br />

the most to total bycatch (40%), followed by rattails (29%), rays <strong>and</strong> skates (3.5%), sharks <strong>and</strong><br />

dogfish (2.3%), crustaceans (2.2%), chimaeras (2.0%), echinoderms (1.6%), <strong>and</strong> cnidarians (0.6%). A<br />

large percentage of the bycatch in these groups was discarded, <strong>and</strong> was less than 85% only for bony<br />

fish (excluding rattails) (33%), rays <strong>and</strong> skates (67%), <strong>and</strong> chimaeras (28%).<br />

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