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MERCURY 379<br />

5.1 OVERVIEW<br />

5. POTENTIAL FOR HUMAN EXPOSURE<br />

Mercury occurs naturally as a mineral <strong>and</strong> is distributed throughout the environment by both natural <strong>and</strong><br />

anthropogenic processes. The natural global bio-geochemical cycling of mercury is characterized by<br />

degassing of the element from soils <strong>and</strong> surface waters, followed by atmospheric transport, deposition of<br />

mercury back to l<strong>and</strong> <strong>and</strong> surface water, <strong>and</strong> sorption of the compound to soil or sediment particulates.<br />

Mercury deposited on l<strong>and</strong> <strong>and</strong> open water is in part revolatilized back into the atmosphere. This<br />

emission, deposition, <strong>and</strong> revolatilization creates difficulties in tracing the movement of mercury to its<br />

sources. Major anthropogenic sources of mercury releases to the environment include mining <strong>and</strong><br />

smelting; industrial processes involving the use of mercury, including chlor-alkali production facilities;<br />

combustion of fossil fuels, primarily coal; production of cement; <strong>and</strong> medical <strong>and</strong> municipal waste<br />

incinerators <strong>and</strong> industrial/commercial boilers (EPA 1996b).<br />

The element has three valence states <strong>and</strong> is found in the environment in the metallic <strong>for</strong>m <strong>and</strong> in the <strong>for</strong>m<br />

of various inorganic <strong>and</strong> organic complexes. The major features of the bio-geochemical cycle of mercury<br />

include degassing of mineral mercury from the lithosphere <strong>and</strong> hydrosphere, long-range transport in the<br />

atmosphere, wet <strong>and</strong> dry deposition to l<strong>and</strong> <strong>and</strong> surface water, sorption to soil <strong>and</strong> sediment particulates,<br />

revolatilization from l<strong>and</strong> <strong>and</strong> surface water, <strong>and</strong> bioaccumulation in both terrestrial <strong>and</strong> aquatic food<br />

chains.<br />

Potential sources of general population exposure to mercury include inhalation of mercury vapors in<br />

ambient air, ingestion of drinking water <strong>and</strong> foodstuffs contaminated with mercury, <strong>and</strong> exposure to<br />

mercury through dental <strong>and</strong> medical treatments. Dietary intake is the most important source of<br />

nonoccupational exposure to mercury, with fish <strong>and</strong> other seafood products being the dominant source of<br />

mercury in the diet. Most of the mercury consumed in fish or other seafood is the highly absorbable<br />

methylmercury <strong>for</strong>m. Intake of elemental mercury from dental amalgams is another major contributing<br />

source to the total mercury body burden in humans in the general population (WHO 1990, 1991).<br />

Because the two major sources of mercury body burden include dietary intake <strong>and</strong> intake from dental<br />

amalgams, mercury is present at low concentrations in a variety of human tissues. Mercury has been<br />

detected in blood, urine, human milk, <strong>and</strong> hair in individuals in the general population. Inhalation of

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