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PRINCIPLES OF TOXICOLOGY

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342 PROPERTIES AND EFFECTS <strong>OF</strong> METALS<br />

alkyl mercury compounds, or ingestion of the treated grain, may also result in toxic endpoints. The<br />

most sensitive endpoint for oral exposure to alkyl mercury compounds is the developing nervous<br />

system. In addition, mercury may adversely affect a wide range of other organ systems after exposure<br />

to high levels. Affected systems include the immune, respiratory, cardiovascular, gastrointestinal,<br />

hematologic, and reproductive systems.<br />

The inhalation reference concentration (RfC) for elemental mercury is 3 × 10 –4 mg/m 3 . An oral<br />

RfD of 3 × 10 –4 mg/kg daily for inorganic mercury and 1 × 10 –4 mg/kg per day for organic mercury<br />

has also been established. These values are under review by USEPA at present. Mercury is not classified<br />

as a carcinogen by any route of exposure.<br />

Nickel<br />

Nickel is a hard, silver-white, malleable, ductile metallic element used extensively in alloys and for<br />

plating because of its oxidation resistance. Nickel, combined with other elements, occurs naturally in<br />

the earth’s crust. Nickel released to the atmosphere typically exists in particulate form or adsorbed to<br />

particulate matter. Primary removal mechanisms of atmospheric nickel include gravitational settling<br />

and precipitation. Nickel released to soil may be adsorbed to soil surfaces depending on the soil<br />

conditions. Nickel released to aquatic systems generally exists in particulate forms that settle out in<br />

areas of active sedimentation. However, nickel also may exist in soluble form under appropriate<br />

conditions.<br />

Nickel salts exhibit significant solubility in water. Nickel occurs naturally in drinking water at an<br />

average concentration of about 2 µg/L. Adult daily intake of nickel from water is about 2 µg/day. About<br />

170 µg of nickel is consumed in food per day. Available information indicates that nickel does not pose<br />

a toxicity problem following ingestion because the absorption from food or water is low.<br />

The most prevalent effect of nickel exposure is nickel dermatitis in nickel-sensitive individuals.<br />

Nickel dermatitis typically exhibits two components: (1) a simple dermatitis localized in the contact<br />

area and (2) chronic eczema or neurodermatitis without apparent connection to such contact. Nickel<br />

sensitivity, once acquired, may be persistent. Toxicological information of concern to industrially<br />

exposed humans is primarily confined to two potential categories of effects: (1) dermatoses, contact<br />

and atopic dermatitis, and allergic sensitization; and (2) cancers of the lung and nasal sinuses. Cancers<br />

of the lung and nasal sinuses in nickel workers have been described for more than 50 years in association<br />

with nickel refining processes (calcination, smelting, roasting, and electrolysis) and from nickel plating<br />

and polishing operations (e.g., electrolysis and grinding). Noncarcinogenic respiratory effects, such<br />

as bronchitis and emphysema, have also been seen in occupational exposures. These effects occurred<br />

at concentrations much higher than those found in the environment.<br />

The current daily oral RfD for nickel is 2 × 10 –4 mg/kg. An inhalation RfD has not been established<br />

and is currently under review. USEPA has classified nickel refinery dust and nickel subsulfide as class<br />

A carcinogens by the inhalation route. Nickel is not presently considered to be a carcinogen by the<br />

oral route.<br />

Zinc<br />

Zinc is found in natural form in the air, in soil and water, and occurs in the environment primarily in<br />

the +2 oxidation state. It is a bluish-white metal that can combine with a number of other elements.<br />

Most zinc ore is zinc sulfide. Zinc is an essential trace element in the diet. In water, zinc partitions to<br />

sediments or suspended solids through sorption. Zinc is likely to sorb strongly onto soil, and the<br />

mobility of zinc in soil depends on the solubility of the speciated forms of the compound and on soil<br />

properties such as pH, redox potential, and cation exchange potential. In air, zinc is present primarily<br />

as small dust particles.<br />

Humans are exposed to small amounts of zinc in food and drinking water each day. Levels in air<br />

are generally low and fairly constant. Occupational exposure to zinc occurs in a number of mining and<br />

industrial activities, such as the manufacture of zinc-containing alloys, paints, and pesticides.

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