Environmental Health Criteria 214
Environmental Health Criteria 214
Environmental Health Criteria 214
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HUMAN EXPOSURE ASSESSMENT<br />
internal exposure sources (e.g., pesticides in adipose tissue).<br />
Furthermore, their use may result in improved monitoring of total<br />
population exposure, characterization of individual and population<br />
exposures and evaluation of internal sources of exposure. These<br />
markers are also useful surveillance tools for monitoring chemical<br />
exposure in both individuals and populations over time.<br />
Use of biological markers of exposure can improve the risk<br />
assessment process by providing a critical link between chemical<br />
exposure, internal dose and health impairment (IPCS, 1993). Biological<br />
markers of exposure can improve clinical diagnoses where there is a<br />
well-established relationship between biological marker and outcome.<br />
10.2 General characteristics<br />
Biological markers represent events or changes in human<br />
biological systems as a result of exposure or disease (US NRC, 1991b).<br />
They are classified as markers of exposure, effect, and susceptibility<br />
and are considered to represent events along a theoretical continuum<br />
from causal exposure to resulting health outcome (US NRC, 1987;<br />
Schulte, 1989). A biological marker of exposure is defined as a<br />
xenobiotic substance or its metabolite(s) or the product of an<br />
interaction between a xenobiotic agent and some target molecule(s) or<br />
cell(s) that is measured within a compartment of an organism (US NRC,<br />
1989; IPCS, 1993). Biological markers of effect are measurable<br />
biochemical, physiological, behavioural or other alterations within an<br />
organism that, depending upon the magnitude, can be recognized as<br />
associated with an established or possible health impairment or<br />
disease (IPCS, 1993). Biological markers of susceptibility are<br />
indicators of inherent or acquired abilities of an organism to respond<br />
to the challenge of exposure to a specific xenobiotic substance (IPCS,<br />
1993). Although the distinction between some biological markers of<br />
exposure and effect may be overlapping, this chapter will focus on<br />
those biological markers which can be applied to environmental<br />
exposure assessment.<br />
10.3 Considerations for use in environmental exposure assessment<br />
The use of biological markers for exposure assessment represents<br />
a different perspective for evaluation of human exposure to a<br />
contaminant than traditional exposure assessment. Biological markers<br />
of exposure are considered measures of internal dose, whereas exposure<br />
is frequently defined as the concentration of an agent at the boundary<br />
between an individual and the environment multiplied by time (US NRC,<br />
1991b; IPCS, 1993). Owing to long-term storage of specific<br />
contaminants in biological tissues (e.g., bone and fat), some<br />
biological markers are markers of both cumulative dose and future<br />
internal exposure.<br />
Biological markers of exposure have been used most frequently in<br />
industrial hygiene and occupational medicine (Elkins, 1954, 1967;<br />
Lauwerys, 1983; Schulte, 1991). Before widespread application of<br />
biological markers for exposure assessment of the general population<br />
can occur, it is important to consider the situations which are best<br />
suited for biological monitoring. Ideally, a biological marker of<br />
exposure should be chemical-specific, detectable in trace quantities,<br />
available by non-invasive techniques and inexpensive to assay. Also,<br />
it must relate consistently and quantitatively to the extent of<br />
exposure and ideally also integrate the exposure over time (Bond et<br />
al., 1992). Currently there are very few biological markers that<br />
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