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There is some evidence of genotoxicity of Hg based upon an epidemiological
study (ATSDR 1989) in which there was a statistical relationship between
chromosome breaks and concentrations of methyl mercury in the blood of
Swedish subjects on fish diets.
Toxicokinetics
The pharmacokinetics of Hg depend largely on its chemical form. At low
doses, most of the elemental Hg is oxidized to the divalent cation which does not
cross the blood-brain barrier. Oral absorption of elemental Hg has been
estimated to be between 0.01 and 0.1 percent (ATSDR 1989). Dermal absorption
of metallic Hg is estimated to be approximately 2 percent, while the absorption
efficiency via inhalation is probably closer to 80 percent. Oral absorption
efficiency of inorganic Hg is estimated to be approximately 7.5 percent based
upon animal and human feeding studies. The oral absorption efficiency of
methylmercury is reported to be as high as 95 percent.
Ecological effects
Mercury is recognized as one of the most toxic of the heavy metals.
Numerous physical factors can affect the acute and chronic toxicities and
bioaccumulation of the various forms of Hg. Data are available on the acute
toxicity of Hg to at least 28 genera of freshwater animals. Acute values for
water-borne invertebrate species range from 2.1 ug/L for Daphnia to 2,000 ug/L
for three insects. Acute values for fishes range from 30 ug/L for the guppy to
1,000 ug/L for some tropical marine organisms. Few data are available for
various organomercury compounds, although they appear to be at least five times
more acutely toxic than metallic mercury. Available chronic data indicate that
methylmercury is the most chronically toxic of the mercury compounds. This is
in part because of the ability of methylmercury to bioconcentrate.
References
Agency for Toxic Substances and Disease Registry. (1989). "Toxicological
profile for mercury," U.S. Public Health Service, Washington, DC.
D49
Appendix D Toxicological Profiles
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