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Aquatic Environment and Biodiversity Annual Review 2012

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

Figure 6.10: <strong>Annual</strong> estimates of fish discards in the target jack mackerel trawl fishery for the 2001-02 to<br />

2004–05 fishing years (in black), calculated for jack mackerel (JMA), commercial species (COM), noncommercial<br />

species (OTH), <strong>and</strong> overall (TOT). Also shown (in grey) are estimates of jack mackerel <strong>and</strong><br />

overall discards calculated for 1990–91 to 2000–01 by Anderson et al. (2000) <strong>and</strong> Anderson (2004a). Error<br />

bars show the 95% confidence intervals.<br />

6.3.5. Southern blue whiting trawl fishery<br />

In the most recent study, covering the period 2002–03 to 2006–07, the ratio estimator used to<br />

calculate bycatch <strong>and</strong> discard rates in this fishery was based on trawl duration. Linear mixed-effect<br />

models (LMEs) identified fishing depth as the key variable influencing bycatch rates <strong>and</strong> discard rates<br />

in this fishery, <strong>and</strong> regression tree methods were used to optimise the number of levels of this variable<br />

in order to stratify the calculation of annual bycatch <strong>and</strong> discard totals in each catch category.<br />

The key categories of catch/discards examined were; southern blue whiting, other QMS species<br />

combined, commercial species combined (as defined above for hoki/hake/ling), non-commercial<br />

species combined, <strong>and</strong> three commonly caught individual species, hake, hoki, <strong>and</strong> ling.<br />

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