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Environmental Health Criteria 214

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HUMAN EXPOSURE ASSESSMENT<br />

immediately following exposure (e.g., solvents in exhaled air, blood<br />

and urine), the half-life reflects elimination from the central<br />

compartment of blood and vessel-rich tissues. For samples taken days,<br />

weeks or even years after exposure, the half-life corresponds to the<br />

elimination from those compartments from which chemical clearance is<br />

much slower; for example, lead from bone or lipophilic organic<br />

chemicals from adipose tissue (Bernard, 1995).<br />

Toxicokinetic data from animals and humans can aid in the<br />

determination of the utility of biological markers in assessing<br />

individual or population exposures. Fig. 30 illustrates how<br />

toxicokinetic data could be utilized to select biological markers of<br />

exposure based on the timing and concentration of exposure (IPCS,<br />

1993). In order to interpret the extent of exposure, it is critical to<br />

collect the biological sample after the exposure has reached an<br />

equilibrium state. This can be especially important for chemicals with<br />

short half-lives, such as benzene in exhaled air with a half-life of<br />

22 h (Bernard, 1995). For example, in occupational settings,<br />

biological monitoring has no advantages over environmental monitoring<br />

for airborne chemicals with biological half-lives less than 10 h,<br />

since the integration time for the marker is too short to allow<br />

accurate representation of exposure (Droz, 1993).<br />

10.3.2 Biological variability<br />

The use of biological markers can also be affected by biological<br />

parameters. Variation can depict true differences in individual<br />

exposures, as represented for example by differing microenvironments<br />

or differing behaviour. It may also represent inherent<br />

inter-individual differences which affect the biological response to<br />

exposure (Droz, 1992). Sources of biological variability include<br />

demographic factors (e.g., age and sex), anthropometric<br />

characteristics (e.g., body size and fat distribution), behaviour<br />

(e.g., activity level or contaminant avoidance behaviours),<br />

biological/circadian rhythms and toxicokinetic differences due to<br />

genotype (Kompaore & Tsuruta, 1993), previous exposure, lifestyle<br />

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

Page 172 of 284<br />

6/1/2007

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