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Environmental Health Criteria 214

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HUMAN EXPOSURE ASSESSMENT<br />

In addition to time allocation measures and microenvironmental<br />

parameters, information on the intensity of contact is needed to<br />

assess exposure. Here the focus is on micro-level activities that<br />

affect the rate of contact with the contaminated media while the<br />

person is in a certain microenvironment (e.g., outdoors at home) and<br />

performing a specific activity (e.g., cleaning). The potential for<br />

dermal contact depends upon the surface area of exposed skin, thus<br />

clothing type and fabric consistency as well as the size of the<br />

person, whether the individual is sitting, crawling, kneeling or using<br />

their hands on the contaminated surface, or otherwise handling the<br />

contaminant. In addition, exposure for the given event depends upon<br />

the duration and frequency of each contact between the exposed skin<br />

and the contaminated media; e.g., 50 1-min contacts between the<br />

person's hand and the floor while cleaning. As described in Chapter 7,<br />

dietary factors, including the type of foods that are consumed and the<br />

amount consumed per time period of interest, are the most obvious.<br />

Concern also has been raised about the potential for contamination of<br />

foods from contact with surfaces during storage, preparation and<br />

consumption (Berry, 1992, Freeman et al., 1997). Hand-mouth and<br />

object-mouth contact, although difficult to measure, may be one of the<br />

most important routes of exposure to contaminants such as pesticides<br />

and lead that reside in house dust, especially in children (Charney et<br />

al., 1980; Rabinowitz & Bellinger, 1988; Davies et al., 1990). For<br />

pollutants for which inhalation is the primary route of exposure, the<br />

intensity of contact is influenced by one's level of exertion (often<br />

referred to as "activity level"). Breathing rate or heart rate is<br />

needed to predict dose (the amount of contaminant that enters the<br />

body), thereby producing a more accurate estimate of the resulting<br />

health effects.<br />

Finally, depending on the purpose of the exposure assessment, the<br />

required temporal resolution of the time-activity data may vary<br />

substantially. Whereas short-term time-activity patterns may be<br />

important for acute exposures, long-term average time-activity<br />

patterns may be more relevant in other circumstances. If long-term<br />

exposure is of major interest, e.g., over years or lifetime,<br />

residential history is an important information to assign respective<br />

ambient monitor data for the entire period of interest (Künzli et al.,<br />

1996).<br />

5.2.2 Surrogates of time-activity patterns<br />

For many exposures surrogates of time-activity patterns may be<br />

developed on the basis of generalizations about the activities of<br />

people at a particular time, who live in a specific geographic<br />

location or who share a specific set of living conditions. Usually the<br />

most important time-activity surrogate is age group. Some activities<br />

that are useful for predicting exposure to air pollutants, such as<br />

distance and timing of travel or duration of work and its locations,<br />

also show systematic differences in their frequency and duration by<br />

demographic characteristics. For instance, Schwab et al. (1990)<br />

documents how time in the kitchen, which influences exposure to<br />

combustion products, is greater among women in the USA than among men,<br />

even after adjusting for whether the woman works outside the home;<br />

likewise, men spend more time in transit, regardless of their age or<br />

employment status. It is likely that the frequency of contact with a<br />

wide variety of toxins differs across groups defined by gender and<br />

age, owing to traditional divisions of labour in many cultures.<br />

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

Page 84 of 284<br />

6/1/2007

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