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MERCURY 454<br />

5. POTENTIAL FOR HUMAN EXPOSURE<br />

science technicians, registered nurses, <strong>and</strong> machine operators. These estimates were derived from<br />

observations of the actual use of mercury (97% of total estimate) <strong>and</strong> the use of trade-name products known<br />

to contain mercury (3%). It is unknown how many of the potentially exposed workers were actually<br />

exposed. Data from the NOES conducted by NIOSH from 1983 to 1986 was broken out by exposure to a<br />

variety of mercury compounds (RTECS 1998). Estimates of the total numbers of all workers <strong>and</strong> women<br />

workers potentially exposed are presented in Table 5-20. A total of 151,947 workers were potentially<br />

exposed to mercury or various mercury compounds; 33% (50,468) of these workers were women.<br />

Table 5-21 summarizes the calculated mercury absorption from air at various occupational exposure<br />

guideline concentrations.<br />

5.6 EXPOSURES OF CHILDREN<br />

This section focuses on exposures from conception to maturity at 18 years in humans <strong>and</strong> briefly considers<br />

potential pre-conception exposure to germ cells. Differences from adults in susceptibility to hazardous<br />

substances are discussed in Section 2.6, Children’s Susceptibility.<br />

Children are not small adults. A child’s exposure may differ from an adult’s exposure in many ways.<br />

Children drink more fluids, eat more food, <strong>and</strong> breathe more air per kilogram of body weight, <strong>and</strong> have a<br />

larger skin surface in proportion to their body volume. A child’s diet often differs from that of adults. The<br />

developing human’s source of nutrition changes with age: from placental nourishment to breast milk or<br />

<strong>for</strong>mula to the diet of older children who eat more of certain types of foods than adults. A child’s behavior<br />

<strong>and</strong> lifestyle also influence exposure. Children crawl on the floor; they put things in their mouths; they may<br />

ingest inappropriate things such as dirt or paint chips; they spend more time outdoors. Children also are<br />

closer to the ground, <strong>and</strong> they do not have the judgement of adults in avoiding hazards (NRC 1993).<br />

Significant health risks, including numerous neuropathological <strong>and</strong> neurobehavioral effects, are associated<br />

with prenatal exposure to methylmercury (Zelikoff et al. 1995). Fetuses <strong>and</strong> breast-fed infants may be<br />

exposed to higher than background concentrations of mercury via maternal consumption of large amounts of<br />

fish or marine mammals contaminated with mercury, via maternal exposure to mercury through dental<br />

amalgams, via maternal use of consumer products containing mercury or various mercury compounds, <strong>and</strong><br />

via occupational exposure of the mother (Zelikoff et al. 1995). Fetuses can be exposed to mercury via<br />

exposures of their mothers either be<strong>for</strong>e or during pregnancy; nursing infants can be exposed via<br />

consumption of contaminated breast milk from mothers exposed via medical, domestic, or occupational

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