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  • https://doi.org/10.1097/01.ee9.0000605748.01146.6aCopy DOI Icon

Potential underestimation of ultrafine particle exposure when using proxy pollutants

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Abstract

OPS 49: Air pollution exposure methods, Room 412, Floor 4, August 27, 2019, 10:30 AM - 12:00 PM The health risks of ultrafine particle (UFP, Dp<100 nm) exposure are an important subject of current investigation in air pollution epidemiology. With routine monitoring of UFP still uncommon, studies often use other co-emitted pollutants as proxy for UFP, with NOx considered a good choice. We use long term fixed site measurements along with extensive mobile monitoring data to evaluate the spatiotemporal correlation of UFP and NOx. We incorporate 3–6 years of hourly particle number (PN) concentration data from multiple fixed sites across the San Francisco Bay Area that include near freeway, urban, suburban and rural sites. In addition, we incorporate observations from a 32-month mobile monitoring campaign comprising >3,000 h of coverage of a range of road types and land uses. Overall annual-average PN at the fixed sites span a range of 3 × 103 #/cm3 at rural site to 30 × 103 #/cm3 at near-freeway site. Across all sites, PN measurements on nearly all summer days show consistent, prominent mid-day peaks, lasting 5–7 h. This diurnal concentration pattern—characteristic of new particle formation (NPF)—is not observed for other co-emitted pollutants (NOx, BC, CO). While we found moderate correlation in diurnal patterns of NOx and UFP at sites with high traffic, the correlation dropped significantly for low traffic areas—especially during high insolation periods (e.g., summer daytime). Mobile monitoring data yielded similar results: NOx was observed to be a weaker proxy of UFP for non-freeway roads during high insolation periods. UFP in urban atmosphere is known to result primarily from vehicular traffic and photonucleation events, however, UFP exposure may be underestimated—especially in high insolation areas—if we use proxies for UFP that represent only emissions and not NPF. Our findings are especially important for ongoing and upcoming epidemiology studies that use other co-emitted pollutants as proxy of UFP.

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