Environmental Health Criteria 214
Environmental Health Criteria 214
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 />
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