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MERCURY 462<br />

5. POTENTIAL FOR HUMAN EXPOSURE<br />

Children may be exposed to mercury during play at home or in school when using art supplies that contain<br />

colors from mercury compounds. Rastogi <strong>and</strong> Pritzi (1996) reported the migration of several toxic metals<br />

including mercury from crayons <strong>and</strong> artist watercolor paints (see Section 5.4). Migration of mercury from<br />

these art supply products occurred in 57% of the samples tested. The authors believe that children might be<br />

exposed not only to mercury, but to several other metals that can migrate from the paints. Grabo (1997) also<br />

reported that artists may be exposed to mercury because it is a main component in airbrush <strong>and</strong> brush<br />

painting pigments as well as a component of pastel chalks. Artist supplies that contain mercury should be<br />

stored out of children’s reach to avoid accidental poisoning.<br />

Infants <strong>and</strong> developing fetuses may be exposed to methylmercury if their mothers consume certain<br />

methylmercury-contaminated fish, shellfish, or wildlife species from contaminated waters prior to their<br />

pregnancy, during their pregnancy, or while nursing. Older children also may be exposed to methylmercury<br />

by eating contaminated fish <strong>and</strong> wildlife species. Certain states, Native American tribes, <strong>and</strong> U.S. Territories<br />

have issued fish <strong>and</strong> wildlife advisories <strong>for</strong> mercury in fresh water, estuarine, <strong>and</strong> saltwater fish <strong>and</strong> in<br />

freshwater turtles (see Section 5.7).<br />

In a study of lactating women, Oskarsson et al. (1996) assessed the total <strong>and</strong> inorganic mercury content in<br />

breast milk <strong>and</strong> blood in relation to fish consumption <strong>and</strong> amalgam fillings (see Section 5.5). In breast milk<br />

samples collected 6 weeks after delivery, about half of the total mercury was inorganic <strong>and</strong> half was<br />

methylmercury, whereas in blood samples only 26% was inorganic <strong>and</strong> 74% was methylmercury. Exposure<br />

of the infant to mercury from breast milk was calculated to range up to 0.3 µg/kg/day, of which<br />

approximately one-half was inorganic mercury. This exposure corresponds to approximately one-half the<br />

tolerable daily intake of total mercury <strong>for</strong> adults recommended by WHO. The authors concluded that ef<strong>for</strong>ts<br />

should be made to decrease total mercury burden in women of reproductive age (Oskarsson et al. 1996).<br />

Two-year-old children seem to be different in their weight-adjusted intake of methylmercury as shown by<br />

the results of the FDA Total Diet Study. Expressed on a per weight basis, methylmercury intake <strong>for</strong> all age<br />

groups except 2-year-old children was approximately 50 ng/kg/day (Clarkson 1990; Gunderson 1988). For<br />

2-year-old children, the intake was estimated to be approximately 100 ng/kg/day (assuming 50% of the fish<br />

intake was due to fish caught locally) or about twice as much methylmercury intake per body weight as <strong>for</strong><br />

other age groups. For additional details, see Section 5.5, General Population <strong>and</strong> Occupational Exposure.

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