Using advanced dispersion models and mobile monitoring to characterize spatial patterns of ultrafine particles in an urban area

Abstract In urban settings with elevated bridges, buildings, and other complex terrain, the relationship between traffic and air pollution can be highly variable and difficult to accurately characterize. Atmospheric dispersion models are often used in this context, but incorporating background concentrations and characterizing emissions at high spatiotemporal resolution is challenging, especially for ultrafine particles (UFPs). Ambient pollutant monitoring can characterize this relationship, especially when using continuous real-time monitoring. However, it is challenging to quantify local source contributions over background or to characterize spatial patterns across a neighborhood. The goal of this study is to evaluate contributions of traffic to neighborhood-scale air pollution using a combination of regression models derived from mobile UFP monitoring observations collected in Brooklyn, NY and outputs from the Quick Urban & Industrial Complex (QUIC) model. QUIC is a dispersion model that can explicitly take into account the three-dimensional shapes of buildings. The monitoring-based regression model characterized concentration gradients from a major elevated roadway, controlling for real-time traffic volume, meteorological variables, and other local sources. QUIC was applied to simulate dispersion from this same major roadway. The relative concentration decreases with distance from the roadway estimated by the monitoring-based regression model after removal of background and by QUIC were similar. Horizontal contour plots with both models demonstrated non-uniform patterns related to building configuration and source heights. We used the best-fit relationship between the monitoring-based regression model after removal of background and the QUIC outputs ( R 2  = 0.80) to estimate a UFP emissions factor of 5.7 × 10 14 particles/vehicle-km, which was relatively consistent across key model assumptions. Our joint applications of novel techniques for analyzing mobile monitoring data and the advanced dispersion model QUIC provide insight about source contributions above background levels and spatiotemporal air pollution patterns in urban areas.

[1]  J. Kaufman,et al.  Modeling traffic air pollution in street canyons in New York City for intra-urban exposure assessment in the US Multi-Ethnic Study of atherosclerosis and air pollution , 2009 .

[2]  Mark J. Nieuwenhuijsen,et al.  Fine particulate matter and carbon monoxide exposure concentrations in urban street transport microenvironments , 2007 .

[3]  D. Westerdahl,et al.  Characterization of on-road vehicle emission factors and microenvironmental air quality in Beijing, China , 2009 .

[4]  S. Wood Generalized Additive Models: An Introduction with R , 2006 .

[5]  T. Tuch,et al.  Dispersion of traffic-related exhaust particles near the Berlin urban motorway - Estimation of fleet emission factors , 2008 .

[6]  L Morawska,et al.  A model for determination of motor vehicle emission factors from on-road measurements with a focus on submicrometer particles. , 2001, The Science of the total environment.

[7]  P. Elliott,et al.  A regression-based method for mapping traffic-related air pollution: application and testing in four contrasting urban environments. , 2000, The Science of the total environment.

[8]  Geoffrey C. Bowker,et al.  Impacts of noise barriers on near-road air quality , 2008 .

[9]  Balwinder Singh,et al.  Evaluation of the QUIC-URB fast response urban wind model for a cubical building array and wide building street canyon , 2008 .

[10]  H. Tong,et al.  Comparative Toxicity of Size-Fractionated Airborne Particulate Matter Collected at Different Distances from an Urban Highway , 2009, Environmental health perspectives.

[11]  Matthias Ketzel,et al.  Particle number, particle mass and NO x emission factors at a highway and an urban street in Copenhagen , 2009 .

[12]  A. Faustini,et al.  Impact of Fine and Ultrafine Particles on Emergency Hospital Admissions for Cardiac and Respiratory Diseases , 2010, Epidemiology.

[13]  R. Gehrig,et al.  Real-world emission factors of fine and ultrafine aerosol particles for different traffic situations in Switzerland. , 2005, Environmental science & technology.

[14]  Christer Johansson,et al.  Urban scale modeling of particle number concentration in Stockholm , 2005 .

[15]  Vlad Isakov,et al.  The effects of roadside structures on the transport and dispersion of ultrafine particles from highways , 2007 .

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

[17]  Zoran Ristovski,et al.  Determination of average emission factors for vehicles on a busy road , 2003 .

[18]  Matthew A. Nelson,et al.  A non-CFD modeling system for computing 3D wind and concentration fields in urban environments , 2010 .

[19]  Bert Brunekreef,et al.  Land use regression model for ultrafine particles in Amsterdam. , 2011, Environmental science & technology.

[20]  Jonathan I Levy,et al.  The influence of traffic on air quality in an urban neighborhood: a community-university partnership. , 2009, American journal of public health.

[21]  Brent C. Hedquist,et al.  Flow, turbulence, and pollutant dispersion in urban atmospheresa) , 2010 .

[22]  Rex Britter,et al.  A baseline urban dispersion model evaluated with Salt Lake City and Los Angeles tracer data , 2003 .

[23]  R. Britter,et al.  FLOW AND DISPERSION IN URBAN AREAS , 2003 .

[24]  John D. Spengler,et al.  Modeling Spatial Patterns of Traffic-Related Air Pollutants in Complex Urban Terrain , 2011, Environmental health perspectives.