Inuit exposure to organochlorines through the aquatic food chain in arctic québec.

Inuit people (Eskimos) are likely exposed to persistent organochlorine compounds because their traditional diet includes fatty tissues of the arctic marine biota. Here we present the results of organochlorine compound analysis in milk fat samples from arctic Québec Inuit women and in fat tissues from various animal species inhabiting that region. The total concentration of polychlorinated biphenyl congeners in Inuit milk fat was similar to that of the beluga, while the profile of the 10 congeners resembled that of the polar bear. Mean concentrations of various organochlorines in milk-fat samples from Inuit women were between 2 and 10 times greater than those found in samples previously collected from southern Québec women. The Inuit mothers exhibit the greatest body burden known to occur from exposure to organochlorine residues present in the environment by virtue of their location at the highest trophic level of the arctic food web. Imagesp618-a

[1]  R Wagemann,et al.  Arctic marine ecosystem contamination. , 1992, The Science of the total environment.

[2]  D. Thomas,et al.  Arctic terrestrial ecosystem contamination. , 1992, The Science of the total environment.

[3]  R Wagemann,et al.  Presence and implications of chemical contaminants in the freshwaters of the Canadian Arctic. , 1992, The Science of the total environment.

[4]  François G. Meyer,et al.  High levels of PCBs in breast milk of inuit women from arctic quebec , 1989, Bulletin of environmental contamination and toxicology.

[5]  D. Muir,et al.  Organochlorine contaminants in arctic marine food chains: identification, geographical distribution and temporal trends in polar bears. , 1988, Environmental science & technology.

[6]  D. Muir,et al.  Organochlorine contaminants in arctic marine food chains: accumulation of specific polychlorinated biphenyls and chlordane-related compounds. , 1988, Environmental science & technology.

[7]  L. Birnbaum The role of structure in the disposition of halogenated aromatic xenobiotics. , 1985, Environmental health perspectives.

[8]  S. Tanabe,et al.  Absorption Efficiency and Biological Half-Life of Individual Chlorobiphenyls in Rats Treated with Kanechlor Products , 1981 .

[9]  A. A. Jensen,et al.  Levels and trends of environmental chemicals in human milk. , 1991 .

[10]  S. Gingras,et al.  PCDDs, PCDFs and PCBs in human milk of women exposed to a PCB fire and of women from the general population of the province of Québec - Canada , 1991 .

[11]  S. Safe,et al.  Polychlorinated biphenyls (PCBs), dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and related compounds: environmental and mechanistic considerations which support the development of toxic equivalency factors (TEFs). , 1990, Critical reviews in toxicology.

[12]  J. Jacobson,et al.  Effects of in utero exposure to polychlorinated biphenyls and related contaminants on cognitive functioning in young children. , 1990, The Journal of pediatrics.

[13]  R. O. Gilbert Statistical Methods for Environmental Pollution Monitoring , 1987 .

[14]  M. Crago,et al.  Chronic otitis media and hearing deficit among native children of Kuujjuaraapik (Northern Quebec): a pilot project. , 1987, Canadian journal of public health = Revue canadienne de sante publique.

[15]  C. K. Wong,et al.  Comparative rates of elimination of some individual polychlorinated biphenyls from the blood of PCB-poisoned patients in Taiwan. , 1982, Food and chemical toxicology : an international journal published for the British Industrial Biological Research Association.