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Vol. 53 - Alaska Resources Library and Information Services

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oil residues in the gut <strong>and</strong> muscle tissue are different. The more water-soluble aromatics<br />

(naphthalene, alkylated benzenes) are transported to the muscle tissues (including gills)<br />

more rapidly, with the phenanthrenes <strong>and</strong> dibenzothiophenes preferentially located in the<br />

gut. During the first two weeks after the spill, however, it is these higher molecular<br />

weight aromatics which persist, the water-soluble aromatics being depurated more<br />

readily.<br />

Initial levels of oil in filter-feeders from Bay 7 are equal or greater than those<br />

from Bays 9 <strong>and</strong> 10, where water column levels of oil were 20 to 200 times as great.<br />

Sediments are ruled out as an oil-biotal intermediary due to the near absence of oil in<br />

Bay 7 sediments. Thus one must postulate that while Mya <strong>and</strong> Serripes from Bays 9 <strong>and</strong> 10<br />

either cease pumping due to water column levels or die after initial accumulation of oil,<br />

animals in low-to-moderately contaminated waters continue to pump <strong>and</strong> acquire oil as<br />

long as it is present in the water. At water column concentrations of 50 µg/l (50 ppb), a<br />

clam (1 g dry weight) pumping at a rate of 1 liter per hour would pass 1.2 mg of oil<br />

through its body in 24 hours, more than enough to acquire a 100-500 ppm concentration.<br />

As levels of oil in Bays 9 <strong>and</strong> 10 were much higher, 1-50 ppm initially <strong>and</strong> 100-200 ppb for<br />

at least a day to a day <strong>and</strong> a half after cessation of the oil spillage, opportunities for<br />

greater bioaccumulation in Bays 9 <strong>and</strong> 10 were available but were probably not achieved<br />

due to either saturation in the gut, inability to transport oil across the membranes fast<br />

enough to acquire more oil, or a wholesale cessation of pumping. The latter explanation is<br />

the most likely.<br />

Mya truncata <strong>and</strong> Serripes groenl<strong>and</strong>icus are filter-feeders <strong>and</strong> accumulate oil<br />

primarily from the water column. They depurate 60-75 percent of the accumulated oil<br />

within two weeks, even though the sediments in which they reside remain contaminated<br />

with oil. On the other h<strong>and</strong>, Macoma calcarea <strong>and</strong> Nuculana minuta are deposit-feeders,<br />

<strong>and</strong> accumulate petroleum hydrocarbons primarily from the sediments. In controlled<br />

laboratory experiments, Roesijadi et al. (1978) showed that the deposit-feeder, Macoma<br />

inquinata, accumulated higher concentrations of aromatic hydrocarbons from Prudhoe Bay<br />

crude oil-contaminated sediments than did the filter-feeder, Protothaca staminea. In the<br />

BIOS study, the deposit-feeders continued to accumulate hydrocarbons during the two<br />

weeks after the spill (Bays 9 <strong>and</strong> 11) or became heavily contaminated immediately after<br />

the spill <strong>and</strong> retained the hydrocarbons for at least two weeks (Bay 7 <strong>and</strong> 10). The GC 2<br />

61

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