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Environmental Health Criteria 214

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HUMAN EXPOSURE ASSESSMENT<br />

provide sufficient time resolution, free from interferences and<br />

cost-effective. Consideration should be given to the likelihood that<br />

the inconvenience of complying with personal monitoring protocols may<br />

alter the normal behaviour of the study participants. For example,<br />

participants tend to wear personal air monitors on days that they do<br />

not go to work. In duplicate portion studies, participants may not<br />

provide equal portions of expensive or well-liked foods, leading to<br />

underestimation of intake. Approaches to personal monitoring of<br />

inhalation, dietary and dermal exposures are discussed below.<br />

Table 6. Summary of personal monitoring approaches<br />

Exposure route Media <strong>Environmental</strong> sample Biological sample<br />

Inhalation air personal monitor breath<br />

urine<br />

Ingestion water tap water blood<br />

Ingestion food duplicate portion faeces<br />

breast milk<br />

Dermal soil/dust dermal patch others<br />

3.5.1.1 Personal monitoring of inhalation exposures<br />

Personal monitoring of human exposure to air pollutants requires<br />

that study participants transport their sample collection device with<br />

them at all times during the assessment period. Examples include a<br />

diffusion tube used for passive sampling of gases, such as VOCs, or a<br />

filter with a battery-operated pump for active sampling of aerosols<br />

and their components (ACGIH, 1995).<br />

Personal air monitors can be grouped into two general categories:<br />

integrated samplers that collect the pollutant over a specified time<br />

period and then are returned to the laboratory for analysis, and<br />

continuous samplers that use a self-contained analytical system to<br />

measure and record the pollutant concentration on the spot.<br />

Instruments in both categories can be either active or passive.<br />

Active monitors use a pump and a power source to move air past a<br />

collector or sensor. Passive monitors depend on diffusion to bring<br />

the pollutants into contact with the collector or sensor. Additional<br />

information may be found in Chapter 7 and ACGIH (1995).<br />

As Wallace & Ott (1982) pointed out, the direct measurement of<br />

exposures using personal monitors raises several methodological<br />

issues. Personal monitoring studies are complex, expensive, time<br />

consuming and labour intensive. Other challenges include selection and<br />

recruitment of representative subjects; distribution, maintenance and<br />

retrieval of many monitors; laboratory analysis of many air samples<br />

returned from monitors in the field or calibration and validation of<br />

many real-time monitors; and the transcription and statistical<br />

analysis of data on pollutant concentrations and time-activity<br />

patterns.<br />

3.5.1.2 Personal monitoring of dietary exposures<br />

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

Page 49 of 284<br />

6/1/2007

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