Prevalence of wide area impacts downwind of freeways under pre-sunrise stable atmospheric conditions

Abstract In urban areas, a large fraction of the population typically lives within 1.5–2 km of a freeway. In an earlier study, Hu et al. (2009) showed that in the pre-sunrise hours, with stable, nocturnal meteorological conditions, the vehicle-related pollution from a freeway in southern California extended more than 2 km downwind. This was in striking contrast to earlier studies in the U.S. and Australia showing that during the daytime pollutant concentrations extended no more than ∼300 m downwind of major roadways. The present study was designed to explore the variability of the large downwind pollutant impact zone observed by Hu et al. (2009) in the pre-sunrise hours on a wider geographic scale. An instrumented mobile platform was employed to measure vehicle-related pollutant concentrations on transects running upwind and downwind of four freeways in the coastal, central and eastern areas of the California South Coast Air Basin (SoCAB) during the pre-sunrise period (04:30–06:30). Extended freeway plumes were observed for ultrafine particles (UFP), nitric oxide and particle-bound polycyclic aromatic hydrocarbons (PAH) at all four sites during stable pre-sunrise periods. Plume lengths were measured to be ∼2 km or more with a dilution rate coefficient about a factor of ten lower than commonly observed for daytime. An average of 39 and 19% (±8–9%) of freeway plume peak concentrations of UFP remained 500 and 1500 m downwind, respectively, from the freeways for the four transects studied here. Because a large fraction of UFP and other vehicle related pollutants typically penetrate into indoor environments, and nocturnal surface inversions are widespread across the globe, our findings have significant implications for more extensive human exposures to vehicle-related pollutants than previously indicated based on daytime measurements of roadway plumes.

[1]  R. Burnett,et al.  Lung cancer, cardiopulmonary mortality, and long-term exposure to fine particulate air pollution. , 2002, JAMA.

[2]  Yifang Zhu,et al.  Penetration of freeway ultrafine particles into indoor environments , 2005 .

[3]  D. Brugge,et al.  Near-highway pollutants in motor vehicle exhaust: A review of epidemiologic evidence of cardiac and pulmonary health risks , 2007, Environmental health : a global access science source.

[4]  Steve L Mara,et al.  A Wide Area of Air Pollutant Impact Downwind of a Freeway during Pre-Sunrise Hours. , 2009, Atmospheric environment.

[5]  Ronald C. Cohen,et al.  Chemical evolution of the Sacramento urban plume: Transport and oxidation , 2002 .

[6]  Yifang Zhu,et al.  Concentration and Size Distribution of Ultrafine Particles Near a Major Highway , 2002, Journal of the Air & Waste Management Association.

[7]  P J Catalano,et al.  Using time- and size-resolved particulate data to quantify indoor penetration and deposition behavior. , 2001, Environmental science & technology.

[8]  J. Seinfeld,et al.  Evolution of nanoparticle size and mixing state near the point of emission , 2004 .

[9]  Yifang Zhu,et al.  Evolution of particle number distribution near roadways. Part II: the 'Road-to-Ambient' process , 2004 .

[10]  Scott Fruin,et al.  Mobile platform measurements of ultrafine particles and associated pollutant concentrations on freeways and residential streets in Los Angeles , 2005 .

[11]  Yifang Zhu,et al.  Comparison of daytime and nighttime concentration profiles and size distributions of ultrafine particles near a major highway. , 2006, Environmental science & technology.

[12]  S. Fruin,et al.  Near-road air pollution impacts of goods movement in communities adjacent to the Ports of Los Angeles and Long Beach , 2009 .

[13]  D. Niemeier,et al.  Near-roadway air quality: synthesizing the findings from real-world data. , 2010, Environmental science & technology.

[14]  Bert Brunekreef,et al.  Concentration response functions for ultrafine particles and all-cause mortality and hospital admissions: results of a European expert panel elicitation. , 2009, Environmental science & technology.

[15]  P. Tiittanen,et al.  Ultrafine particles in urban air and respiratory health among adult asthmatics. , 2001, The European respiratory journal.

[16]  Rex Britter,et al.  Dynamics and dispersion modelling of nanoparticles from road traffic in the urban atmospheric environment—A review , 2011 .