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Vol. 53 - Alaska Resources Library and Information Services

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spills need consideration.<br />

The effects of oil spills in the nearshore zone are well documented<br />

(see Clark, 1982). Incorporation of oil into the subtidal sediment <strong>and</strong><br />

its subsequent loss are functions of the circumstances of the particular<br />

spill <strong>and</strong> the energy of the nearshore zone. Because of its high energy<br />

the nearshore zone of the North Aleutian Shelf appears likely to have oil<br />

incorporated into <strong>and</strong> readily lost from subtidal s<strong>and</strong> following a spill.<br />

Whereas prediction of the probable occurrence, magnitude <strong>and</strong> extent of an<br />

oil spill reaching the nearshore subtidal habitats of the smallest<br />

juvenile king crab is beyond the scope of this study, there is little<br />

doubt that should a significant spill reach the nearshore zone there could<br />

be substantial acute, lethal <strong>and</strong> sublethal effects. Substantial immediate<br />

effects including the oiling <strong>and</strong> mortality of intertidal crabs occurred<br />

during the AMOCO CADIZ spill (See review by Conan et al, 1981).<br />

Substantial mortality of juvenile king crab would require water column<br />

concentrations of 4.2 ppm total hydrocarbons by IR, the 96-h LC 50 for<br />

moribundity found by Brodersen et al (1977) for juvenile king crab exposed<br />

to WSF of Cook Inlet crude oil. The concentrations of oil in the<br />

sediment that would produce mortality in the juvenile king crab are not<br />

known. If a spill should produce acute mortality in the smallest juvenile<br />

king crab, any substantial loss of yearling crab could be felt as decrease<br />

in year class strength in the commercial fisheries 8 years later when the<br />

crabs would have reached harvestable size.<br />

Chronic indirect effects persisting beyond a spill could derive from<br />

loss or reduction in the macro or meiofaunal food of the smallest<br />

juveniles. Meiofaunal groups vary considerably in their resistance to oil<br />

contamination <strong>and</strong> can recover quickly (Giere, 1979). In studying a<br />

refinery effluent Dicks <strong>and</strong> Hartley (1982) report that oligochaetes had<br />

decreased density at stations near the refinery <strong>and</strong> showed a gradient in<br />

density paralleling that of sediment concentrations of aliphatic<br />

hydrocarbon. The immunoassay identified oligochaetes as a dietary item<br />

for the smallest juvenile crab. In subtidal recruitment studies<br />

V<strong>and</strong>erhorst (Unpublished data; see V<strong>and</strong>erhorst, 1984) found significant<br />

reductions in the numbers of species of polychaetes, mollusks <strong>and</strong><br />

crustaceans recruiting into s<strong>and</strong> contaminated with crude oil at total oil<br />

levels initially at 2000 ppm <strong>and</strong> falling to below 1000 ppm in 3 months.<br />

Densities of a crustacean <strong>and</strong> a polychaete selected a priori for detailed<br />

analysis were reduced to 1/4 <strong>and</strong> 1/3, respectively, of the densities in<br />

control s<strong>and</strong>. From intertidal recruitment studies V<strong>and</strong>erhorst et al.<br />

(1981) predicted full recovery of the infauna to take 31 months following<br />

an initial contamination of the s<strong>and</strong> at 1800 ppm. An oil spill in the<br />

shallow nearshore zone can reasonably be expected to reduce the density of<br />

food important to juvenile crabs, but prediction of the extent of such<br />

restriction in the crab's food supply requires prediction of the salient<br />

features of such a spill.<br />

252

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