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

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HEALTH IMPACT ASSESSMENT<br />

Fig. 1. Schematic presentation of the main steps of health impact assessment<br />

<strong>Air</strong> pollution data<br />

Modelled levels a<br />

(or monitored)<br />

a If modelled data are used, the<br />

approach can be used to assess<br />

the impact of emission reduction<br />

strategies on different health<br />

outcomes.<br />

Exposure estimate<br />

Population risk<br />

Overall<br />

Susceptible groups<br />

Impact estimate<br />

Concentration–<br />

response function(s)<br />

Background data<br />

Mortality rates<br />

Morbidity rates<br />

the background or reference concentration to ultimately determine the change<br />

in air pollution being evaluated. The background level is the “natural” concentration<br />

of the pollutant that would exist even without any man-made pollution.<br />

The reference concentration can be an air pollution standard or goal developed<br />

by WHO, USEPA or other governmental institutions. As an alternative, some<br />

analysts have simply estimated the impact of some assumed percentage reduction,<br />

such as 10–20%, from current levels. Finally, some assessments have calculated<br />

the impacts of a specific control strategy, such as the USEPA analysis of<br />

motor vehicle standards (5), or are based on the modelled contribution of certain<br />

categories of pollution sources. For example, the CAFE analysis estimated the<br />

impact of PM from anthropogenic sources (24).<br />

Size and composition of population groups exposed to current levels<br />

of air pollution<br />

The relevant population exposed to the change in ambient concentrations is the<br />

second data requirement for the assessment. Ideally, these data can be obtained<br />

at the local level from census information or other available sources. In addition,<br />

since some of the CR functions are specific to certain subgroups (e.g. the elderly,<br />

asthmatics, infants and children), baseline demographic data on subgroups<br />

would be useful.<br />

Background incidence of mortality and morbidity<br />

Since the epidemiological studies typically estimate relative risk (i.e. the percentage<br />

change in health effects per unit of pollution), the third input into the analysis<br />

is the underlying incidence of the health effect being estimated (e.g. the underlying<br />

mortality rate in the population or deaths per thousand people). Ideally,<br />

157

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