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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 />

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

Page 51 of 284<br />

6/1/2007

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