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Aquatic Environment and Biodiversity Annual Review 2012

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

Figure 6.7: <strong>Annual</strong> estimates of fish bycatch in the target hoki, hake <strong>and</strong> ling trawl fishery, calculated for<br />

commercial species, non-commercial species, <strong>and</strong> overall for 2000–01 to 2006–07 (black). Also shown (in<br />

light grey) are the equivalent bycatch estimates calculated for 1990–91 to 1998–99 by Anderson et al.<br />

(2001), <strong>and</strong> for the years 1990–91, 1994–95, 1998–99 <strong>and</strong> 1999–2000 to 2002–03 by Anderson <strong>and</strong> Smith<br />

(2004), (in dark grey). Error bars show the 95% confidence intervals.<br />

Total annual discard estimates for 2000–01 to 2006–07 ranged from about 5500 to 29 000 t per year<br />

with the main species being discarded including spiny dogfish, rattails, javelinfish, hoki, <strong>and</strong><br />

shovelnose dogfish. Total annual discards for 1990–91 to 1998–99 were between 6600 t <strong>and</strong> 17 900 t,<br />

<strong>and</strong> overall there has been no obvious trend in total discards (Figure 6.8). The target species (hoki,<br />

hake, <strong>and</strong> ling) made up 9.7% of total observed discards. Discard rates were strongly influenced by<br />

the use of meal plants on fishing vessels; discards of non-commercial species on factory vessels<br />

without meal plants was up to twice the level of discards for vessels with meal plants. The use of meal<br />

plants, especially for species such as javelinfish <strong>and</strong> other rattails, has become more prevalent in<br />

recent years.<br />

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