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effects of additional heavy oiling. This may be a result of an adaptation<br />

of microorganisms to the presence of oil, or to a selection of oil<br />

resistant populations.<br />

It is not surprising that hydrocarbons did not directly inhibit<br />

sulfate reduction since this process appears to be active in oil formation<br />

waters (Bailey, et al., 1973; ZoBell, 1958). However, it was surprising<br />

that <strong>com</strong>pounds which inhibited acetate oxidation did not directly<br />

inhibit sulfate reduction, as other investigations have pointed<br />

to the importance of acetate as a substrate for sulfate reduction (Winfrey<br />

and Ward, submitted; Srensen et al, 1981; Banat and Nedwell, personal<br />

<strong>com</strong>munication).<br />

The chemistry of hydrocarbons present in the various sediments one<br />

year after the spill indicated the presence of oil highly altered by<br />

evaporation and biodegradation. The levels observed in the environment<br />

were also lower (0.1-1 mg/g) than the levels added in our experiments<br />

to simulate heavy oiling (50-250 mg/g). It is possible that a temporary<br />

inhibition of acetate oxidation could have resulted from very heavy<br />

oiling of relatively fresh oil. Such conditions could have existed at<br />

all polluted sites immediately following the AMOCO CADIZ spill, although<br />

rapid loss of volatile <strong>com</strong>pounds probably occurred between<br />

spillage and beaching of oil (Dowty, et al, 1981; Ward, et al, 1980).<br />

Any inhibitory effect would then have been reduced as cleanup or transport<br />

of hydrocarbons out of the sediments decreased hydrocarbon amount,<br />

and as evaporation, dissolution and biodegradation altered the remaining<br />

sediment hydrocarbons. By the time site <strong>com</strong>parison experiments<br />

could be performed, recovery from any negative effects which might have<br />

occurred had apparently taken place. The inhibitory effects on acetate<br />

oxidation we observed may be significant in extremely cold regions<br />

where slow rates of evaporation would occur.<br />

ACKNOWLEDGEMENTS<br />

We are indebted to the Centre Oceanologique de Bretagne at Brest<br />

and the Station Biologique at Roscoff for providing laboratory space<br />

and assistance. We also thank Bob Clark of the NOAA National Analytical<br />

Facility for supplying AMOCO CADIZ mousse, George Ward of Exxon<br />

Corp. for supplying the light Arabian crude oil, and Dale Meland and<br />

Melinda Tussler for technical assistance.<br />

This study was part of a joint effort undertaken by the Centre National<br />

pour 1' Exploitation des Oceans (CNEXO) of the French Ministry of<br />

Industry and the NOAA of the U.S. Department of Commerce to study the<br />

ecological consequences of the AMOCO CADIZ oil spill. It was financed<br />

by funds given to NOAA (contract NA 79RAC00013) by the Amoco Transport<br />

Company and by the NOAA Outer Continental Shelf Environmental Assessment<br />

Program, through an interagency agreement with the Bureau of Land<br />

Management.<br />

186

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