Abstract

Abstract. Black carbon (BC) particles can have deleterious human health consequences and impact regional and global climate. Uncertainties remain in part due to incomplete knowledge on the evolution of physical properties and mixing state of black carbon from sources to the remote atmosphere. We aim to understand how “road-to-ambient” processing and longer timescale aging in an urban plume affect black carbon physical properties. Refractory black carbon (rBC) was measured during summer 2016 using a single-particle soot photometer (SP2) in two distinct environments: near a major freeway and downwind of downtown Los Angeles. The near-road measurements were made at distances ranging from 30 to 114 m downwind of Interstate 405 in Los Angeles. These results were compared with measurements performed 100 km east of Los Angeles in Redlands, California. Coatings on rBC particles were quantified using two methods. As distance from the highway increased at the near-road site, we observed decreases in rBC mass and number concentrations and increases in the number fraction of rBC particles with thick coatings (f). The latter likely occurred due to rapid processing of the highway plume and entrainment of urban background particles. Most rBC-containing particles measured near the highway were either uncoated or thinly coated. In Redlands, we found that rBC mass concentrations on weekdays were similar to those observed at the furthest measured distance from the highway (114 m). However, rBC number concentrations for the smallest measured sizes were an order of magnitude lower in Redlands than all measured distances from the highway. Observations of f indicate that values in Redlands during periods when estimated photochemical age (PCA) was highest (6–8 h) were similar to corresponding values at the furthest measured distance from the highway. This suggests that the residence time of air in the Los Angeles Basin under typical summertime conditions measured during this campaign may not be sufficient for rBC to acquire thick coatings. However, under certain meteorological conditions, f was observed to be ∼0.20 in Redlands, with coating thickness histograms showing a larger contribution of rBC particles with coating thickness > 80 nm. This occurred during a weekend day when local emissions from diesel vehicles were lower (compared to weekdays) and winds brought air from the desert regions to Redlands, both of which would increase the relative contribution of remote sources of rBC. Afternoon values of f (and O3) were found to be systematically higher on weekends than weekdays, suggesting that the “weekend effect” can create more thickly coated rBC particles presumably due to enhanced secondary organic aerosol (SOA) and reduced available rBC as condensation sites.

Highlights

  • Black carbon (BC) is considered the second strongest climate-forcing agent following carbon dioxide (CO2) and causes a myriad of pernicious health effects including cancer (Hart et al, 2009; Lloyd and Cackette, 2011; WHO, 2012; Bond et al, 2013)

  • The first is analogous to the driver of Refractory black carbon (rBC) mass and number concentration decreases; as distance from the highway increases, the plume dilutes and entrains background air that would likely include a greater fraction of thickly coated aged particles

  • Improving understanding in spatiotemporal distributions of refractory black carbon, as well as evolution of rBC physical properties and mixing state at both (a) rapid timescales near sources and (b) longer timescales as pollutants are transported on urban, continental, and global scales is critical for reducing uncertainty on the impacts of aerosols on human health and regional and global climate

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Summary

Introduction

Black carbon (BC) is considered the second strongest climate-forcing agent following carbon dioxide (CO2) and causes a myriad of pernicious health effects including cancer (Hart et al, 2009; Lloyd and Cackette, 2011; WHO, 2012; Bond et al, 2013). Krasowsky et al.: Physical properties and mixing state of black carbon particles heating with consequences on atmospheric thermodynamics (Cooke and Wilson, 1996; Hansen et al, 1997, 2005; BanWeiss et al, 2012). Estimates of emissions and climate consequences of BC remain uncertain compared to other climateforcing agents (Bond et al, 2013). Improving understanding of spatiotemporal variation (from pollutant source to the remote atmosphere) in BC concentrations and physical properties is critical for reducing uncertainties in quantifying its climate and health impacts

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