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

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NITROGEN DIOXIDE<br />

particles. In some studies, however, the strongest effect was found for nitrogen<br />

dioxide itself, while PM had a weaker or no effect. In particular, stronger indications<br />

of an independent effect of nitrogen dioxide come from studies on hospital<br />

admissions or emergency department visits for respiratory and cardiovascular<br />

diseases, studies on asthma aggravation, and from evaluating indoor effects, especially<br />

among asthmatics and infants at risk of asthma.<br />

Nitrogen dioxide concentrations closely follow vehicle emissions in many situations,<br />

so nitrogen dioxide levels are generally a reasonable marker of exposure<br />

to traffic-related emissions. <strong>Health</strong> risks from nitrogen oxides may potentially result<br />

from nitrogen dioxide itself, correlated exhaust components such as ultrafine<br />

particles and hydrocarbons, or nitrogen dioxide chemistry products, including<br />

ozone and secondary particles. The issue is complicated by the fact that PM10 or<br />

PM2.5 might be indicators for regionally transported, rather homogeneously distributed<br />

particles as well as locally produced, rather non-homogeneously distributed<br />

combustion particles. Nitrogen dioxide is often recognized as an indicator<br />

of locally produced particles, mainly from mobile sources. This also seems to be<br />

the case in the Southern California Children’s <strong>Air</strong> Pollution Study, which on the<br />

one hand provides evidence for a strong nitrogen dioxide health effect, but on the<br />

other reports the impossibility of disentangling the effects of nitrogen dioxide<br />

from the effects of elemental carbon. The same issue applies to assessing the role<br />

of nitrogen dioxide in inducing respiratory disease in children.<br />

In conclusion, nitrogen dioxide concentrations are often used to establish<br />

spatial variability in air pollution concentrations from mobile sources and remain<br />

inseparable from the often unmeasured particle emissions from combustion<br />

sources, and in particular from mobile sources. Therefore, it is difficult to<br />

determine whether the effects observed for nitrogen dioxide and PM are the independent<br />

effects of the gaseous pollutant nitrogen dioxide and of PM, or are<br />

independent effects of locally produced fine and ultrafine carbonaceous particles<br />

and of regionally transported accumulation-mode particles.<br />

<strong>Guidelines</strong><br />

Evidence from animal toxicological studies indicates that long-term exposure<br />

to nitrogen dioxide at concentrations above current ambient concentrations has<br />

adverse effects. In population studies, nitrogen dioxide has been associated with<br />

adverse health effects even when the annual average nitrogen dioxide concentration<br />

complied with the WHO annual guideline value of 40 μg/m 3 (121). Also,<br />

some indoor studies suggest effects on respiratory symptoms among infants at<br />

concentrations below 40 μg/m 3 . Together, these results support a lowering of the<br />

annual nitrogen dioxide guideline value. However, since nitrogen dioxide is an<br />

important constituent of combustion-generated air pollution and is highly correlated<br />

with other primary and secondary combustion products, it is unclear to<br />

what extent the health effects observed in epidemiological studies are attributable<br />

375

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