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Environmental Health Criteria 214

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HUMAN EXPOSURE ASSESSMENT<br />

Similarly, information about an individual's health condition may<br />

be important in characterizing their time-activity pattern. For<br />

instance, the limited data available on asthmatics suggests they may<br />

spend more time indoors than the general population (Goldstein et al.,<br />

1986, 1988; Lichtenstein et al., 1989; Schwab et al., 1991). As<br />

asthmatics are particularly sensitive to air pollutants, this activity<br />

information is important.<br />

Socioeconomic status may influence time-activity patterns related<br />

to, for instance, time spent travelling to work or outdoors.<br />

Currently, however, the gap existing in time-activity databases with<br />

respect to the activity patterns of sensitive (e.g., elderly) and<br />

potentially high-risk (e.g., low socioeconomic status) subgroups, is a<br />

limitation for extension of exposure models to these groups. Further<br />

study is needed to determine the extent to which income, education and<br />

occupation are reliable surrogates for exposure-related factors (e.g.,<br />

housing unit size and condition).<br />

5.2.3 Data collection methods<br />

Sociologists pioneered studies of activity patterns (Szalai,<br />

1972; Chapin, 1974; Robinson, 1977). These "time budget"<br />

investigations, which have been conducted in several nations,<br />

emphasize the purpose of activities (cooking, eating, TV watching).<br />

Ott (1989) summarizes such studies in relation to their usefulness to<br />

exposure assessment; a basic drawback for exposure assessment<br />

applications is the lack of information on location, particularly<br />

distinguishing whether the participant was indoors or outdoors. In the<br />

1960s and 1970s, a series of time-activity studies was conducted by<br />

geographers interested in the influence of the economic and physical<br />

structure of cities on travel patterns, e.g., journey to work (Hanson<br />

& Hanson, 1981), access to facilities (Fox, 1983) or shopping<br />

behaviour (Douglas, 1973). As such, the emphasis was on collecting<br />

information on the geographic location of trip origins and<br />

destinations as well as timing and mode use. Finally, the US<br />

Department of Transportation, in conjunction with the Census Bureau,<br />

has been collecting information on the travel activities (durations<br />

and mode use) of a representative national sample approximately every<br />

7 years since 1969 (US Federal Highway Administration, 1986, 1992).<br />

A variety of methods are available for collecting data about<br />

time-activity patterns, including interviewer-administered recall<br />

questionnaires, self-administered real-time diaries, direct<br />

observation and video recording. The diary techniques used in the<br />

social sciences for eliciting time-activity data have been applied to<br />

studies of total human exposure to air pollutants (see methodological<br />

reviews by Robinson (1988), Ott (1989), Quackenboss & Lebowitz<br />

(1989)). Specifically, participants are asked to complete a diary or<br />

questionnaire regarding their activities during the designated period<br />

(usually 12-48 h). The survey instruments used in these exposure<br />

studies, however, depart from any single type used previously. Rather<br />

than focusing on activity purposes or transportation exclusively, the<br />

instruments used in exposure studies probe for changes in location or<br />

activity that might lead to changes in the level of pollution to which<br />

the person came into contact.<br />

Time allocation measures for assessing exposure to air pollutants<br />

frequently have been collected using self-completed real-time diaries.<br />

Because this approach requests that participants record all activities<br />

over one or more 12-h or 24-h periods, it has the potential to provide<br />

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

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6/1/2007

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