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

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160<br />

AIR QUALITY GUIDELINES<br />

Extrapolation of CR functions beyond the observed air quality concentrations<br />

The accuracy of the underlying CR function may be altered by extrapolating the<br />

existing function to concentrations either below or above the range of the original<br />

study. The current evidence has failed to detect the existence of a threshold at the<br />

population level, so calculating effects down to a background concentration is a<br />

scientifically supportable assumption. However, some analysts use a conservative<br />

approach to extrapolation and only apply the study to a range equal to that of the<br />

original study. Others extrapolate the CR functions down to zero, while some<br />

have assumed the existence of threshold concentrations below which health effects<br />

are unlikely. Regarding the upper range of concentrations, some analysts<br />

have extrapolated the CR functions up to the highest observed concentrations in<br />

the area under study. The accuracy of these extrapolations depends on the shape<br />

of the underlying CR function and is often not observable. Thus an appropriate<br />

strategy is to explore the sensitivity of these assumptions on the ultimate result.<br />

One issue that is of particular concern is the extrapolation of a linear function to<br />

the highest observed concentrations in highly polluted cities or regions. At very<br />

high concentrations, it is likely that the CR function will begin to flatten; therefore<br />

a linear extrapolation well beyond the range of the underlying data should be<br />

carefully evaluated. The global burden of disease project specifically addressed<br />

this issue by considering non-linear functional forms and assuming a maximum<br />

for the relative risk estimates (2).<br />

Choice of health outcomes<br />

Often, the analyst must choose to focus on a subset of several health end-points<br />

that have been studied. The choice of which end-points to include in the quantitative<br />

assessment may be determined by the strength of available evidence from<br />

the epidemiological as well as other scientific literature, the accuracy of the definition<br />

of the end-point under consideration, the availability of information on<br />

baseline rates, and the importance of the impact from both the health and, perhaps,<br />

the economic viewpoint. It is much easier to choose a given end-point to<br />

include if many studies of this health effect exist, particularly if the studies involve<br />

a wide range of cities, seasonal patterns, meteorology, co-pollutants and<br />

background health status. The daily time series studies of mortality and PM provide<br />

a good example of this, in that they have been conducted in five continents<br />

and show reasonably consistent results. In addition, all-cause mortality has a<br />

clear and consistent definition (as opposed to, for example, asthma or mortality<br />

from cardiovascular disease) regardless of location. Finally, most of the analyses<br />

to date indicate that effects on mortality, particularly those relating to long-term<br />

exposure to air pollution, tend to dominate the economic effects, often accounting<br />

for 80% or more of the total.<br />

The consistency of the daily time series studies among so many locations<br />

suggests it is reasonable to extrapolate the findings of the effects of long-term

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