An Assessment of PCBs and OC Pesticides in Eggs of

Authors: Megan L Harris Laurie K Wilson John E Elliott

Publish Date: 2005/06/28

Volume: 14, Issue: 6, Pages: 607-625

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Abstract

Eggs of doublecrested and pelagic cormorants were collected between 1970 and 2002 from colonies in the Strait of Georgia BC Canada and assayed for concentrations of organochlorine OC pesticides and polychlorinated biphenyls PCBs Doublecrested cormorant eggs from the early 1970’s contained up to 41 mg kg−1 pp′DDE and 125 mg kg−1 ∑PCBs Corresponding values for pelagic cormorant eggs were 15 mg kg−1 pp′DDE and 39 mg kg−1 ∑PCBs Egg tissue concentrations of the dominant OC pesticides and ∑PCBs dropped mainly during the 1970’s with minor declines thereafter The data suggest that contaminant levels in cormorants have now stabilized at low levels throughout the resident population Small but significant latitudinal gradients in several OC pesticides and PCBs indicated that areas of the southern strait were more contaminated than areas of the less populated northern strait Interspecific differences in contamination may indicate that pelagic cormorants have a reduced capacity to metabolize chlordanes DDT and PCBs compared to doublecrested cormorants Alternatively the two species may have more divergent prey bases than previously thought During the 1980’s TCDD toxic equivalents largely contributed by polychlorinated dibenzopdioxins PCDDs and dibenzofurans PCDFs were correlated with physiological and biochemical alterations Also from 1989 to 1990 four deformed cormorant chicks two of each species were found during nest visits none were found between 1991 and 1995 The relative rates of deformed chicks were 6 per 10000 for doublecrested and 16 per 10000 for pelagic cormorants The findings of deformed chicks were coincident with the period of highest PCDD and PCDF contamination however the sample sizes were too low to derive a substantive connection Colonywide productivity of doublecrested cormorants was poorer in the southern colonies where PCBs in particular were elevated While of concern these lines of evidence are insufficient to conclude that chlorinated hydrocarbon contamination was a dominant contributor to population declines It seems more probable that ecological variables particularly changing prey and predator dynamics drove the reductions in population size

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