Ultrafine particles near a major roadway in Raleigh, North Carolina: Downwind attenuation and correlation with traffic-related pollutants

Ultrafine particles (UFPs, diameter < 100 nm) and co-emitted pollutants from traffic are a potential health threat to nearby populations. During summertime in Raleigh, North Carolina, UFPs were simultaneously measured upwind and downwind of a major roadway using a spatial matrix of five portable industrial hygiene samplers (measuring total counts of 20–1000 nm particles). While the upper sampling range of the portable samplers extends past the defined “ultrafine” upper limit (100 nm), the 20–1000 nm number counts had high correlation (Pearson R = 0.7–0.9) with UFPs (10–70 nm) measured by a co-located research-grade analyzer and thus appear to be driven by the ultrafine range. Highest UFP concentrations were observed during weekday morning work commutes, with levels at 20 m downwind from the road nearly fivefold higher than at an upwind station. A strong downwind spatial gradient was observed, linearly approximated over the first 100 m as an 8% drop in UFP counts per 10 m distance. This result agreed well with UFP spatial gradients estimated from past studies (ranging 5–12% drop per 10 m). Linear regression of other vehicle-related air pollutants measured in near real-time (10-min averages) against UFPs yielded moderate to high correlation with benzene (R2 = 0.76), toluene (R2 = 0.49), carbon monoxide (R2 = 0.74), nitric oxide (R2 = 0.80), and black carbon (R2 = 0.65). Overall, these results support the notion that near-road levels of UFPs are heavily influenced by traffic emissions and correlate with other vehicle-produced pollutants, including certain air toxics.

[1]  B. Gullett,et al.  Real-time, on-line characterization of diesel generator air toxic emissions by resonance-enhanced multiphoton ionization time-of-flight mass spectrometry. , 2004, Analytical chemistry.

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

[3]  Yifang Zhu,et al.  Study of ultrafine particles near a major highway with heavy-duty diesel traffic , 2002 .

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

[5]  Pamela Ohman-Strickland,et al.  Respiratory effects of exposure to diesel traffic in persons with asthma. , 2007, The New England journal of medicine.

[6]  W. Kreyling,et al.  Translocation of Inhaled Ultrafine Particles to the Brain , 2004, Inhalation toxicology.

[7]  Lidia Morawska,et al.  Concentrations of submicrometre particles from vehicle emissions near a major road , 2000 .

[8]  Michael J Kleeman,et al.  Size and Composition Distributions of Particulate Matter Emissions: Part 1—Light-Duty Gasoline Vehicles , 2007, Journal of the Air & Waste Management Association.

[9]  Yifang Zhu,et al.  Field Comparison of P-Trak and Condensation Particle Counters , 2006 .

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

[11]  G. Oberdörster,et al.  Translocation and effects of ultrafine particles outside of the lung. , 2006, Clinics in occupational and environmental medicine.

[12]  Dave K. Verma,et al.  Correlation of nitrogen dioxide with other traffic pollutants near a major expressway , 2008 .

[13]  Vlad Isakov,et al.  Traffic and Meteorological Impacts on Near-Road Air Quality: Summary of Methods and Trends from the Raleigh Near-Road Study , 2008, Journal of the Air & Waste Management Association.

[14]  Michael J Kleeman,et al.  Size and Composition Distributions of Particulate Matter Emissions: Part 2—Heavy-Duty Diesel Vehicles , 2007, Journal of the Air & Waste Management Association.

[15]  Sara Janhäll,et al.  Roadside measurements of fine and ultrafine particles at a major road north of Gothenburg , 2002 .

[16]  Matthias Ketzel,et al.  Evaluation and modelling of the size fractionated aerosol particle number concentration measurements nearby a major road in Helsinki – Part I: Modelling results within the LIPIKA project , 2007 .

[17]  David B. Kittelson,et al.  Nanoparticle emissions on Minnesota highways , 2004 .

[18]  A. Peters,et al.  Respiratory effects are associated with the number of ultrafine particles. , 1997, American journal of respiratory and critical care medicine.

[19]  Sara Janhäll,et al.  Size resolved traffic emission factors of submicrometer particles , 2004 .

[20]  Vlad Isakov,et al.  Characterization of Near-Road Pollutant Gradients Using Path-Integrated Optical Remote Sensing , 2008, Journal of the Air & Waste Management Association.

[21]  Brian J. Bennett,et al.  Ambient Particulate Pollutants in the Ultrafine Range Promote Early Atherosclerosis and Systemic Oxidative Stress , 2008, Circulation research.

[22]  J. Finkelstein,et al.  Translocation of Inhaled Ultrafine Manganese Oxide Particles to the Central Nervous System , 2006, Environmental health perspectives.

[23]  Michael J. Kleeman,et al.  SIZE AND COMPOSITION DISTRIBUTION OF FINE PARTICULATE MATTER EMITTED FROM MOTOR VEHICLES , 2000 .

[24]  J. Heyder,et al.  Pulmonary and systemic effects of short-term inhalation exposure to ultrafine carbon black particles. , 2004, Toxicology and applied pharmacology.