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Air Quality Guidelines Global Update 2005 - World Health ...

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HEALTH EFFECTS OF AIR POLLUTION: AN OVERVIEW<br />

evaluation of epidemiological evidence (78). Such quantitative summary estimates<br />

have been generated for Asia, Europe and Latin America (38,39,73). Another<br />

such effort combined data from 109 studies conducted in different parts of<br />

the world (79).<br />

Quantitative summary estimates provide more robust information than data<br />

from individual studies, and therefore facilitate regional comparisons and the<br />

calculation of health impacts. One important problem in meta-analysis is the potential<br />

for publication bias, which refers to the tendency of editors (and authors)<br />

to publish articles containing positive findings rather than those that do not yield<br />

“significant” results (76). Statistical techniques are available to assess this bias and<br />

should be used when conducting meta-analysis (73,80).<br />

Quantitative summary estimates are often used for estimating the costs and<br />

benefits of air pollution (25). A limitation related to the usefulness of quantitative<br />

summary estimates for decision-making has to do with the heterogeneity of effect<br />

estimates from individual studies. Often in meta-analysis, effect estimates are<br />

pooled without consideration of the location of the individual studies. This may<br />

lead to the generation of quantitative summary estimates based on results that<br />

are not comparable. As observed with the development of exposure–response<br />

curves, more thought needs to go into how to address subgroup variations to enhance<br />

generalizability without losing power. Similarly, sources of heterogeneity<br />

include the air pollution mix, climate, and individual population sensitivities and<br />

demographics (31,81).<br />

Case-crossover analysis<br />

The case-crossover study design was proposed by Maclure (82) to study the effects<br />

of momentary and intermittent exposures on the risk of developing an acute<br />

and rare health event supposed to occur soon after the exposure. Since this design<br />

focuses on individual deaths rather than death counts, it is possible to control for<br />

factors that may modify or influence the effects of air pollution on mortality at<br />

the individual level. Therefore, this approach has been applied in studies of the<br />

effects of air pollution on health as an alternative to time series analysis, since it<br />

may improve causal inferences about air pollution effects (83).<br />

The design can be seen as a variation on the case-control study, in which each<br />

individual bearing the event of interest (the case) acts as his or her own control.<br />

For each case, the distribution of exposures in the period just before the event is<br />

compared with the distribution of exposures estimated from some separate referent<br />

time period. Thus, by making within-subject comparisons, time-independent<br />

confounders are controlled by design.<br />

When this design is applied to exposures that exhibit a time trend, however,<br />

there is great potential for confounding in the risk estimate owing to this trend in<br />

the exposure series (84). Therefore, an important methodological feature of this<br />

strategy is adequate selection of control or referent periods. Several simulation<br />

97

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