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Environmental Health Criteria 214

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HUMAN EXPOSURE ASSESSMENT<br />

By their very nature, bioaerosols have compositions and<br />

concentrations that are highly variable. The conditions favourable for<br />

growth, reproduction and dispersion vary within a wide range of<br />

temperature, moisture and nutrient conditions. These same factors<br />

influence by interactions with human and animal activities. Mechanical<br />

systems and machines can cause amplification and distribution of<br />

biological aerosols. As a result personal exposures are quite<br />

variable; this, in turn, has led many investigators to rely on area<br />

air sampling and/or bulk sampling of materials. For example, it is<br />

recommended that a surrogate measure of mite allergen exposure is<br />

derived from bedding and floor dust samples. Home samples, whether air<br />

or dust is sampled, are often the "exposure" value used in<br />

epidemiological investigations.<br />

Finally, the advancement of aerobiological exposure assessment to<br />

eventual use in quantitative risk assessment will require better<br />

understanding of relevant dose to cause sensitization and reactivity<br />

for many different organisms and/or agents.<br />

10. ASSESSING EXPOSURES WITH BIOLOGICAL MARKERS<br />

10.1 Introduction<br />

This chapter presents a summary of the major concepts,<br />

definitions, advantages, limitations, sampling, media and uses of<br />

biological markers as applied for exposure assessment to environmental<br />

contaminants. These exposures are frequently characterized by low<br />

contaminant concentrations, multiple sources and multiple types of<br />

chemicals. Use of biological markers has been extensively reviewed<br />

from both epidemiological and occupational monitoring perspectives as<br />

well as their use in risk assessment (Bernard & Lauwerys, 1986; Harris<br />

et al., 1987; US NRC, 1987; Hulka & Wilcosky, 1988; Cullen, 1989;<br />

Griffith et al., 1989; Henderson et al., 1989; Monster & Zielhuis,<br />

1991a,b; Schulte, 1991; Hulka & Margolin, 1992; IPCS, 1993; Aitio,<br />

1994; Grandjean et al., 1994; Silbergeld & Davis, 1994). The reader<br />

should refer to the research literature for a comprehensive and<br />

detailed understanding of the complex issues relevant to the<br />

development, validation, and application of biomarkers in studies of<br />

human exposure. The specific issue of using biological markers in<br />

occupational settings is beyond the scope of this chapter.<br />

It is important to indicate that, to date, very few biomarkers<br />

can be effectively used for quantitative estimation of prior<br />

environmental exposure to contaminants (e.g., carbon monoxide or<br />

lead). In most cases, there are qualitative or semi-quantitative<br />

indicators for monitoring such exposures. However, as the field<br />

evolves, and knowledge of the pharmacokinetics and pharmacodynamics of<br />

xenobiotics develops, the number of quantitatively validated<br />

biomarkers of exposure will also increase.<br />

Biological markers present unique advantages as tools for<br />

multimedia exposure assessment. They are highly sensitive indices of<br />

an individual's exposure to chemicals, since they provide a measure of<br />

the internal dose, account for all routes of exposure and integrate<br />

over a variety of sources of exposure (Friberg, 1985; Baselt, 1988;<br />

Sim & McNeil, 1992). Therefore, they can represent past exposure<br />

(e.g., the presence of lead in shed teeth), recent exposure to an<br />

external source (e.g., VOCs in exhaled breath) and even future<br />

http://www.inchem.org/documents/ehc/ehc/ehc<strong>214</strong>.htm<br />

Page 169 of 284<br />

6/1/2007

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