DOI: 10.6084/m9.figshare.13020557
title: Contribution of tailpipe and non-tailpipe traffic sources to quasi-ultrafine, fine and coarse particulate matter in southern California

description: Exposure to traffic-related air pollution (TRAP) in the near-roadway environment is associated with multiple adverse health effects. To characterize the relative contribution of tailpipe and non-tailpipe TRAP sources to particulate matter (PM) in the quasi-ultrafine (PM<sub>0.2</sub>), fine (PM<sub>2.5</sub>) and coarse (PM<sub>2.5–10</sub>) size fractions and identify their spatial determinants in southern California (CA). Month-long integrated PM<sub>0.2</sub>, PM<sub>2.5</sub> and PM<sub>2.5–10</sub> samples (n = 461, 265 and 298, respectively) were collected across cool and warm seasons in 8 southern CA communities (2008–9). Concentrations of PM mass, elements, carbons and major ions were obtained. Enrichment ratios (ER) in PM<sub>0.2</sub> and PM<sub>10</sub> relative to PM<sub>2.5</sub> were calculated for each element. The Positive Matrix Factorization model was used to resolve and estimate the relative contribution of TRAP sources to PM in three size fractions. Generalized additive models (GAMs) with bivariate loess smooths were used to understand the geographic variation of TRAP sources and identify their spatial determinants. EC, OC, and B had the highest median ER in PM<sub>0.2</sub> relative to PM<sub>2.5</sub>. Six, seven and five sources (with characteristic species) were resolved in PM<sub>0.2</sub>, PM<sub>2.5</sub> and PM<sub>2.5–10</sub>, respectively. Combined tailpipe and non-tailpipe traffic sources contributed 66%, 32% and 18% of PM<sub>0.2</sub>, PM<sub>2.5</sub> and PM<sub>2.5–10</sub> mass, respectively. Tailpipe traffic emissions (EC, OC, B) were the largest contributor to PM<sub>0.2</sub> mass (58%). Distinct gasoline and diesel tailpipe traffic sources were resolved in PM<sub>2.5</sub>. Others included fuel oil, biomass burning, secondary inorganic aerosol, sea salt, and crustal/soil. CALINE4 dispersion model nitrogen oxides, trucks and intersections were most correlated with TRAP sources. The influence of smaller roadways and intersections became more apparent once Long Beach was excluded. Non-tailpipe emissions constituted ~8%, 11% and 18% of PM<sub>0.2</sub>, PM<sub>2.5</sub> and PM<sub>2.5–10</sub>, respectively, with important exposure and health implications. Future efforts should consider non-linear relationships amongst predictors when modeling exposures. <i>Implications</i>: Vehicle emissions result in a complex mix of air pollutants with both tailpipe and non-tailpipe components. As mobile source regulations lead to decreased tailpipe emissions, the relative contribution of non-tailpipe traffic emissions to near-roadway exposures is increasing. This study documents the presence of non-tailpipe abrasive vehicular emissions (AVE) from brake and tire wear, catalyst degradation and resuspended road dust in the quasi-ultrafine (PM<sub>0.2</sub>), fine and coarse particulate matter size fractions, with contributions reaching up to 30% in PM<sub>0.2</sub> in some southern California communities. These findings have important exposure and policy implications given the high metal content of AVE and the efficiency of PM<sub>0.2</sub> at reaching the alveolar region of the lungs and other organ systems once inhaled. This work also highlights important considerations for building models that can accurately predict tailpipe and non-tailpipe exposures for population health studies.