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Oil Spills and the Marine Environment







thereof, of the release of petroleum on fishery productivity as reflected in commercial catch statistics. Notable among these was a study undertaken along the coast of Louisiana, which supports very large and important commercial fisheries as well as a highly developed petroleum industry. Statistics show no decline in catches of shrimp, crabs, and fish concommitant with the development of the petroleum industry (). A decline in the oyster harvest coincident with the expansion of the petroleum industry in the 1940s has been attributed to an oyster disease and not oil. While it is tempting to seize upon this as evidence that oil is not detrimental to the productivity of a large coastal area, several shortcomings in fishery catch statistics need to be pointed out. They do not represent precise reporting, because they fail to take into account the changing effort and technological advances of fisheries and are generally not available for the localized areas in which pollution may be intense. On the other hand, field surveys in Texas indicate that the production of fish and shrimp is reduced in waters polluted by large oil-producing operations ().

It is certainly apparent that the long history of oil production on the Gulf Coast has not resulted in large scale devastation of fisheries, but data are inconclusive on the possibility of important local effects.

PLANKTON

Few observable effects of oil spills on the small, passively drifting plants and animals composing the plankton have been uncovered in post-spill investigations. Some kills were observed during the Torrey Canyon spill among phytoplankton (plant plankton), but none among the zooplankton (animal plankton) (). In any case, the heavy use of chemical dispersants complicates the issue. Studies following the Santa Barbara blowout could detect no harmful effects on phytoplanktonic productivity () or zooplankton populations (). However, because plankton is passively carried about by water currents, it would be very difficult to discern effects in the field, especially in open waters like the English or Santa Barbara Channels.

Laboratory experiments have generally produced more tangible results, although the degree to which these results may be extrapolated to natural conditions is open to question. As early as 1935, Galtsoff et al () found that growth in cultures of diatoms, which are important components of the phytoplankton, was inhibited by high concentrations of oil. Russian workers have also found that various diatom species are sensitive to kerosene and fuel oils (). Recently, researchers have found that water extracts of various crude and fuel oils and dispersants may inhibit growth of phytoplankters (), or affect the rate of photosynthesis (). However, it is difficult to relate the results of most of these studies to what might actually be experienced in the marine environment, because either the actual concentrations of hydrocarbons in the experimental water was unreported or the concentrations used in the