25.10.2013 Views

Aquatic Environment and Biodiversity Annual Review 2012

Aquatic Environment and Biodiversity Annual Review 2012

Aquatic Environment and Biodiversity Annual Review 2012

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

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

Table 5.12: Potential <strong>and</strong> residual risk scores for each seabird taxon with a potential risk score of >=30 in<br />

Rowe (2010). Residual risk (“optimal risk” in Rowe 2010b, not tabulated therein for grey-faced petrel or<br />

light-mantled albatross) is estimated assuming mitigation is deployed <strong>and</strong> correctly used throughout all<br />

interacting fisheries.<br />

Taxon Potential score Residual score Percent reduction<br />

White-chinned petrel 159 123 23<br />

Sooty shearwater 126 108 14<br />

Black (Parkinson's) petrel 139 106 24<br />

Salvin's albatross 161 106 34<br />

White-capped albatross 141 94 33<br />

Flesh-footed shearwater 117 92 21<br />

Southern Buller's albatross 123 85 31<br />

Grey petrel 123 84 32<br />

Black-browed albatross 114 80 30<br />

Northern Buller's albatross 107 72 33<br />

Chatham albatross 114 71 38<br />

Campbell albatross 97 66 32<br />

Westl<strong>and</strong> petrel 89 59 34<br />

Antipodean albatross 89 55 38<br />

Gibson's albatross 89 55 38<br />

W<strong>and</strong>ering albatross 89 55 38<br />

Southern royal albatross 79 49 38<br />

King shag 48 48 0<br />

Pitt Isl<strong>and</strong> shag 46 46 0<br />

Chatham Isl<strong>and</strong> shag 45 45 0<br />

Hutton's shearwater 37 35 5<br />

Northern giant petrel 62 35 44<br />

Pied shag 35 35 0<br />

Indian yellow-nosed albatross 58 34 41<br />

Southern giant petrel 61 34 44<br />

Fluttering shearwater 34 32 6<br />

Spotted shag 31 31 0<br />

Stewart Isl<strong>and</strong> shag 31 31 0<br />

Yellow-eyed penguin 30 30 0<br />

Grey-faced petrel 31 – –<br />

Light-mantled albatross 30 – –<br />

Setnet <strong>and</strong> inshore trawl fisheries groups posed the greatest residual risk to seabirds (summed across<br />

all taxa); both had aggregate scores of over 200 <strong>and</strong> had no substantive mitigation. Surface <strong>and</strong><br />

bottom longline fisheries <strong>and</strong> middle-depth trawl fisheries for finfish <strong>and</strong> squid also had aggregate<br />

risk scores of 100 or more. These risk scores were substantially reduced if mitigation was assumed to<br />

be deployed throughout these fisheries (reductions of 24 to 56%), but all remained above 100.<br />

Trawling for southern blue whiting <strong>and</strong> deep-water species, inshore drift net, various seine methods,<br />

ring net, diving, dredging, <strong>and</strong> h<strong>and</strong> gathering all had aggregate risk scores of 40 or less if mitigation<br />

was assumed to be deployed throughout these fisheries. Diving, dredging, <strong>and</strong> h<strong>and</strong> gathering were all<br />

judged by the panel to pose essentially no risk to seabirds.<br />

94

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!