Contrasts in Oxidative Potential and Other Particulate Matter Characteristics Collected Near Major Streets and Background Locations

Background: Measuring the oxidative potential of airborne particulate matter (PM) may provide a more health-based exposure measure by integrating various biologically relevant properties of PM into a single predictor of biological activity. Objectives: We aimed to assess the contrast in oxidative potential of PM collected at major urban streets and background locations, the associaton of oxidative potential with other PM characteristics, and the oxidative potential in different PM size fractions. Methods: Measurements of PM with aerodynamic diameter ≤ 10 μm (PM10), PM with aerodynamic diameter ≤ 2.5 μm (PM2.5), soot, elemental composition, and oxidative potential of PM were conducted simultaneously in samples from 8 major streets and 10 urban and suburban background locations in the Netherlands. Six 1-week measurements were performed at each location over a 6-month period in 2008. Oxidative potential was measured as the ability to generate hydroxyl radicals in the presence of hydrogen peroxide in all PM10 samples and a subset of PM2.5 samples. Results: The PM10 oxidative potential of samples from major streets was 3.6 times higher than at urban background locations, exceeding the contrast for PM mass, soot, and all measured chemical PM characteristics. The contrast between major streets and suburban background locations was even higher (factor of 6.5). Oxidative potential was highly correlated with soot, barium, chromium, copper, iron, and manganese. Oxidative potential of PM10 was 4.6 times higher than the oxidative potential of PM2.5 when expressed per volume unit and 3.1 times higher when expressed per mass unit. Conclusions: The oxidative potential of PM near major urban roads was highly elevated compared with urban and suburban background locations, and the contrast was greater than that for any other measured PM characteristic.

[1]  J. Schauer,et al.  Associations of Primary and Secondary Organic Aerosols With Airway and Systemic Inflammation in an Elderly Panel Cohort , 2010, Epidemiology.

[2]  Evon M. O. Abu-Taieh,et al.  Comparative Study , 2020, Definitions.

[3]  Zhi Ning,et al.  Redox activity of urban quasi-ultrafine particles from primary and secondary sources , 2009 .

[4]  B. 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 and Technology.

[5]  B. Forsberg,et al.  Oxidative properties of ambient PM2.5 and elemental composition : heterogeneous associations in 19 European cities , 2009 .

[6]  Flemming R Cassee,et al.  Oxidative potential of semi-volatile and non volatile particulate matter (PM) from heavy-duty vehicles retrofitted with emission control technologies. , 2009, Environmental science & technology.

[7]  A. Dillner,et al.  Generation of hydroxyl radicals from ambient fine particles in a surrogate lung fluid solution. , 2009, Environmental science & technology.

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

[9]  Roel P F Schins,et al.  Oxidant generation by particulate matter: from biologically effective dose to a promising, novel metric , 2006, Occupational and Environmental Medicine.

[10]  Hui Li,et al.  Hydroxyl-radical-dependent DNA damage by ambient particulate matter from contrasting sampling locations. , 2006, Environmental research.

[11]  Thomas Götschi,et al.  Comparison of Oxidative Properties, Light Absorbance, and Total and Elemental Mass Concentration of Ambient PM2.5 Collected at 20 European Sites , 2005, Environmental health perspectives.

[12]  W. MacNee,et al.  Combustion-derived nanoparticles: A review of their toxicology following inhalation exposure , 2005, Particle and Fibre Toxicology.

[13]  Constantinos Sioutas,et al.  Redox activity of airborne particulate matter at different sites in the Los Angeles Basin. , 2005, Environmental research.

[14]  B. Brunekreef,et al.  Epidemiological evidence of effects of coarse airborne particles on health , 2005, European Respiratory Journal.

[15]  André Nel,et al.  ATMOSPHERE: Enhanced: Air Pollution-Related Illness: Effects of Particles , 2005 .

[16]  Roy M. Harrison,et al.  Major component composition of PM10 and PM2.5 from roadside and urban background sites , 2004 .

[17]  Roel P F Schins,et al.  Inhaled particles and lung cancer. Part A: Mechanisms , 2004, International journal of cancer.

[18]  B. Legube,et al.  A comparative study of the effects of chloride, sulfate and nitrate ions on the rates of decomposition of H2O2 and organic compounds by Fe(II)/H2O2 and Fe(III)/H2O2. , 2004, Chemosphere.

[19]  Thomas Sandström,et al.  An in vitro and in vivo investigation of the effects of diesel exhaust on human airway lining fluid antioxidants. , 2004, Archives of biochemistry and biophysics.

[20]  Thomas Kuhlbusch,et al.  Hydroxyl radical generation by electron paramagnetic resonance as a new method to monitor ambient particulate matter composition. , 2003, Journal of environmental monitoring : JEM.

[21]  F. Kelly,et al.  Oxidative stress: its role in air pollution and adverse health effects , 2003, Occupational and environmental medicine.

[22]  P. Borm,et al.  Temporal variation of hydroxyl radical generation and 8-hydroxy-2′-deoxyguanosine formation by coarse and fine particulate matter , 2003, Occupational and environmental medicine.

[23]  A. Nel,et al.  Ultrafine particulate pollutants induce oxidative stress and mitochondrial damage. , 2002, Environmental health perspectives.

[24]  K. Donaldson,et al.  Interactions between ultrafine particles and transition metals in vivo and in vitro. , 2002, Toxicology and applied pharmacology.

[25]  Bert Brunekreef,et al.  Spatial variability of fine particle concentrations in three European areas , 2002 .

[26]  J Inmon,et al.  Ambient air particles: effects on cellular oxidant radical generation in relation to particulate elemental chemistry. , 1999, Toxicology and applied pharmacology.

[27]  Ernie Weijers,et al.  Contrast in air pollution components between major streets and background locations: Particulate matter mass, black carbon, elemental composition, nitrogen oxide and ultrafine particle number , 2011 .

[28]  R. Harrison,et al.  Evaluating the Toxicity of Airborne Particulate Matter and Nanoparticles by Measuring Oxidative Stress Potential — A Workshop Report and Consensus Statement , 2008 .

[29]  T. D. de Kok,et al.  Development and application of an electron spin resonance spectrometry method for the determination of oxygen free radical formation by particulate matter. , 2005, Environmental science & technology.

[30]  Simon Kingham,et al.  Traffic-related differences in outdoor and indoor concentrations of particles and volatile organic compounds in Amsterdam , 2000 .

[31]  K. Ikemura Development and application , 1971 .