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INTRODUCTION<br />

All fate and effects studies of oil spills in the marine environment<br />

depend on analytical chemical information concerning the distribution<br />

and <strong>com</strong>position of the spilled oil. This includes petroleum<br />

hydrocarbon concentrations and <strong>com</strong>positions in water, sediment, and<br />

tissue samples. In turn, this information can be used to deduce the<br />

nature of the weathering process (including evaporation, dissolution,<br />

and biodegradation) , biological assimilation and depuration, and the<br />

mass budget of the oil. Thus the analytical chemistry <strong>com</strong>ponent of the<br />

AMOCO CADIZ research program provides crucial information to many<br />

other <strong>com</strong>ponents of the program in the investigation of the timedependent<br />

fate and effects of this spill.<br />

During the six weeks following the grounding of the supertanker<br />

AMOCO CADIZ on March 16, 1978, oil came ashore along 320 kilometers of<br />

the Brittany coastline (Gundlach and Hayes, 1978). Various shoreline<br />

types were impacted (e.g., rocky shores, sand flats, coastal embayments,<br />

tidal mud flats and salt marshes). During the early stages of<br />

the spill, oil was transported offshore and deposited in the benthic<br />

environment. The fate of petroleum residues deposited in these impacted<br />

areas was and continues to be affected by coastal processes which<br />

dictate such factors as wave energy and sediment transport, and create<br />

environments of differing substrate character (e.g., grain size),<br />

chemical status (oxidizing versus reducing) , and biological activity<br />

. All of these factors and others<br />

(e.g., microbiological biomass)<br />

(e.g., light intensity) <strong>com</strong>bine to determine the weathering characteristics<br />

of the residual petroleum assemblage.<br />

Biological populations initially impacted by the spilled oil may<br />

be subject to chronic exposure to petroleum hydrocarbons associated<br />

with (and released from) the substrate to which they are closely<br />

linked, or they may undergo rapid or slow depuration of initial residues<br />

if no longer exposed to oil, via transplantation or due to flushing<br />

by "clean" seawater. Such differential exposure histories have<br />

been previously observed to profoundly affect the spilled oil residual<br />

body burdens in marine organisms (Boehm et al., 1982).<br />

Although oil spills have received increasing attention from the<br />

scientific <strong>com</strong>munity during the past decade, there have been few<br />

opportunities to examine the chemical <strong>com</strong>positional changes in beached<br />

or sedimented oil in a variety of coastal environments, over a significant<br />

period of time and to examine uptake (impact) and depuration<br />

(recovery) of petroleum by marine organisms. A detailed examination of<br />

the chemical changes in oiled substrate suggests both the anticipated<br />

residence time of deposited oil, and the potential for biological<br />

damage of the petroleum residues. Rashid (1974) examined <strong>com</strong>positional<br />

changes of Bunker C oil from the ARROW spill in Nova Scotia at different<br />

coastal locations. Other than this study only site-specific<br />

studies of the geochemistry of petroleum weathering (e.g., Mayo et al.,<br />

1978; Blumer et al., 1973; Teal et al . , 1978) have been undertaken.<br />

36

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