Environmental Health Criteria 214
Environmental Health Criteria 214
Environmental Health Criteria 214
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HUMAN EXPOSURE ASSESSMENT<br />
the water contacts the skin. Dermal exposure in this situation is<br />
defined as the concentration of the contaminant in the water and the<br />
duration of contact.<br />
3.5.2 Indirect approaches to exposure assessment<br />
Indirect measures of exposure include estimates derived from<br />
environmental monitoring (i.e., measurements made in locations<br />
frequented by the study participants), models and questionnaires.<br />
3.5.2.1 <strong>Environmental</strong> monitoring<br />
Indirect estimates of exposure may be made by combining<br />
measurements of pollutant concentrations at fixed sites with<br />
information on rates of contact with these media recorded in data logs<br />
and diaries or time-activity surveys. Examples include air pollutant<br />
concentrations in specific areas combined with time budget records<br />
(see Chapter 5), food contaminant data combined with information on<br />
dietary patterns (see Chapter 7.4 for details), and pollutant<br />
concentrations on skin combined with data on frequency and duration of<br />
hand-to-mouth contact. Although collection of environmental,<br />
time-activity and questionnaire data needed for this exposure<br />
assessment approach is simpler than for personal monitoring, it is<br />
still invasive and laborious, and may lead to selection bias.<br />
Microenvironmental monitoring is a special case of environmental<br />
monitoring in which the location where measurements are made is<br />
considered to be homogeneous with respect to concentrations of the<br />
target pollutants over the averaging time of interest. The concept of<br />
a microenvironment has been widely applied in air pollution exposure<br />
assessments. Examples of potentially important micro-environments used<br />
for air pollution exposure assessment are listed in Table 7. The<br />
general form of the equation used to calculate time-weighted<br />
integrated exposure from micro environmental monitoring data is<br />
(3.1)<br />
where E is the time-weighted integrated exposure (e.g., mg/m 3 ),<br />
C is the concentration (e.g., mg/m 3 ), t is the unit time (e.g.,<br />
minute), T is the total elapsed time (e.g., minutes). The subscripts<br />
i, j and k denote the medium, the pathway and the microenvironment<br />
respectively (Duan, 1982). The most important assumptions inherent in<br />
this model are:<br />
* The concentration C j in microenvironment j is assumed to be<br />
constant during the time that person i is there.<br />
* The concentration C j within microenvironment j and the time<br />
that person i spends there are assumed to be independent events.<br />
* The number of microenvironments necessary to characterize personal<br />
exposure adequately is assumed to be small.<br />
The concept of a time-weighted integrated exposure is illustrated<br />
in Fig. 10. A unit width is indicated on the j axis for each of five<br />
microenvironments: indoors at home, indoors at work, indoors in other<br />
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