Characterizing the range of children's air pollutant exposure during school bus commutes

Real-time and integrated measurements of gaseous and particulate pollutants were conducted inside five conventional diesel school buses, a diesel bus with a particulate trap, and a bus powered by compressed natural gas (CNG) to determine the range of children's exposures during school bus commutes and conditions leading to high exposures. Measurements were made during 24 morning and afternoon commutes on two Los Angeles Unified School District bus routes from South to West Los Angeles, with seven additional runs on a rural/suburban route, and three runs to test the effect of window position. For these commutes, the mean concentrations of diesel vehicle-related pollutants ranged from 0.9 to 19 μg/m3 for black carbon, 23 to 400 ng/m3 for particle-bound polycyclic aromatic hydrocarbon (PB-PAH), and 64 to 220 μg/m3 for NO2. Concentrations of benzene and formaldehyde ranged from 0.1 to 11 μg/m3 and 0.3 to 5 μg/m3, respectively. The highest real-time concentrations of black carbon, PB-PAH and NO2 inside the buses were 52 μg/m3, 2000 ng/m3, and 370 μg/m3, respectively. These pollutants were significantly higher inside conventional diesel buses compared to the CNG bus, although formaldehyde concentrations were higher inside the CNG bus. Mean black carbon, PB-PAH, benzene and formaldehyde concentrations were higher when the windows were closed, compared with partially open, in part, due to intrusion of the bus's own exhaust into the bus cabin, as demonstrated through the use of a tracer gas added to each bus's exhaust. These same pollutants tended to be higher on urban routes compared to the rural/suburban route, and substantially higher inside the bus cabins compared to ambient measurements. Mean concentrations of pollutants with substantial secondary formation, such as PM2.5, showed smaller differences between open and closed window conditions and between bus routes. Type of bus, traffic congestion levels, and encounters with other diesel vehicles contributed to high exposure variability between runs.

[1]  Mark J. Nieuwenhuijsen,et al.  Fine particle (PM2.5) personal exposure levels in transport microenvironments, London, UK. , 2001, The Science of the total environment.

[2]  J. Seiber Toxic air contaminants in urban atmospheres: Experience in California☆ , 1996 .

[3]  D. R. Lawson,et al.  Formaldehyde Measurement Methods Evaluation and Ambient Concentrations During the Carbonaceous Species Methods Comparison Study , 1990 .

[4]  J. Olsen,et al.  Cancer incidence in urban bus drivers and tramway employees: a retrospective cohort study. , 1998, Occupational and environmental medicine.

[5]  M. Kleeman,et al.  Comparison of Real-Time Instruments Used To Monitor Airborne Particulate Matter , 2001, Journal of the Air & Waste Management Association.

[6]  A W Gertler,et al.  On-road emissions of carbonyls from light-duty and heavy-duty vehicles. , 2001, Environmental science & technology.

[7]  J F Collins,et al.  Time resolved characterization of diesel particulate emissions. 1. Instruments for particle mass measurements. , 2001, Environmental science & technology.

[8]  J. Yanosky,et al.  A Comparison of Four Gravimetric Fine Particle Sampling Methods , 2001, Journal of the Air & Waste Management Association.

[9]  R. L. Dod,et al.  Tunnel measurements of the PAH, carbon thermogram and elemental source signature for vehicular exhaust , 1984 .

[10]  A. Carl Nelson,et al.  Validation of air monitoring data , 1980 .

[11]  Kun-Ho Park,et al.  Commuter exposure to volatile organic compounds under different driving conditions , 1999 .

[12]  F. Lurmann,et al.  Reductions in human benzene exposure in the California South Coast Air Basin , 2001 .

[13]  Bert Brunekreef,et al.  Assessment of exposure to traffic related air pollution of children attending schools near motorways , 2001 .

[14]  R. Colvile,et al.  Fine particle (PM2.5) personal exposure levels in transport microenvironments, London, UK. , 2001, The Science of the total environment.

[15]  T. Johnson Diesel Emission Control: 2001 in Review , 2002 .

[16]  T. Bush,et al.  Five years of nitrogen dioxide measurement with diffusion tube samplers at over 1000 sites in the UK , 2001 .

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

[18]  W A Turner,et al.  Calibration of Sharp Cut Impactors for Indoor and Outdoor Particle Sampling , 2000, Journal of the Air & Waste Management Association.

[19]  Thomas W. Kirchstetter,et al.  On-Road Emissions of Particulate Polycyclic Aromatic Hydrocarbons and Black Carbon from Gasoline and Diesel Vehicles , 1998 .

[20]  C. Pope,et al.  Respiratory disease associated with community air pollution and a steel mill, Utah Valley. , 1989, American journal of public health.

[21]  I. Mavroidis,et al.  Comparison of indoor and outdoor concentrations of CO at a public school. Evaluation of an indoor air quality model , 2002 .

[22]  G Ramachandran,et al.  Comparison of Short-Term Variations (15-Minute Averages) in Outdoor and Indoor PM2.5 Concentrations , 2000, Journal of the Air & Waste Management Association.

[23]  P J Lioy,et al.  Exposure to emissions from gasoline within automobile cabins. , 1992, Journal of exposure analysis and environmental epidemiology.

[24]  Peter F. Nelson,et al.  Exposure to emissions of 1,3-butadiene and benzene in the cabins of moving motor vehicles and buses in Sydney, Australia , 1997 .

[25]  P. S. Nielsen,et al.  Environmental air pollution and DNA adducts in Copenhagen bus drivers--effect of GSTM1 and NAT2 genotypes on adduct levels. , 1996, Carcinogenesis.

[26]  Lisa D. Sabin,et al.  Relative Importance of School Bus-Related Microenvironments to Children’s Pollutant Exposure , 2005, Journal of the Air & Waste Management Association.

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

[28]  B. Finlayson‐Pitts,et al.  Chemistry of the Upper and Lower Atmosphere , 2000 .

[29]  Thomas W Robert Harley Kirchstetter Impact of reformulated fuels on particle and gas-phase emissions from motor vehicles. , 1999 .

[30]  William T Winberry,et al.  Compendium of methods for the determination of toxic organic compounds in ambient air, June 1988 , 1988 .

[31]  James A. Wiley,et al.  Study of children's activity patterns , 1991 .

[32]  Petros Koutrakis,et al.  Method Comparisons for Particulate Nitrate, Elemental Carbon, and PM2.5 Mass in Seven U.S. Cities , 2000, Journal of the Air & Waste Management Association.

[33]  M R Ashmore,et al.  Exposure of commuters to carbon monoxide in Mexico City II. Comparison of in-vehicle and fixed-site concentrations. , 1995, Journal of exposure analysis and environmental epidemiology.

[34]  Application of an Ir tracer to determine soot exposure to students commuting to school on Baltimore public buses , 1998 .

[35]  J. Levy Impact of Residential Nitrogen Dioxide Exposure on Personal Exposure: An International Study. , 1998, Journal of the Air & Waste Management Association.

[36]  D. McDowall,et al.  Interrupted Time Series Analysis , 1980 .

[37]  Christian Monn,et al.  Exposure assessment of air pollutants: a review on spatial heterogeneity and indoor/outdoor/personal exposure to suspended particulate matter, nitrogen dioxide and ozone , 2001 .

[38]  R. Schierl,et al.  Airborne platinum concentrations in Munich city buses. , 1996, The Science of the total environment.

[39]  Stuart Batterman,et al.  Levels and composition of volatile organic compounds on commuting routes in Detroit, Michigan , 2002 .

[40]  K. Fung,et al.  Measurement of Formaldehyde and Acetaldehyde Using 2,4-Dinitrophenylhydrazine-impregnated Cartridges During the Carbonaceous Species Methods Comparison Study , 1990 .

[41]  Gina M. Solomon,et al.  No Breathing in the Aisles: Diesel Exhaust inside School Buses. , 2001 .

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

[43]  L. Knudsen,et al.  Increased urinary excretion of 8-oxo-2'-deoxyguanosine, a biomarker of oxidative DNA damage, in urban bus drivers. , 1999, Mutation research.

[44]  I L Gee,et al.  Commuter exposure to respirable particles inside buses and by bicycle. , 1999, The Science of the total environment.

[45]  S. Friedlander,et al.  Size distributions of polycyclic aromatic hydrocarbons and elemental carbon. 2. Ambient measurements and effects of atmospheric processes. , 1994, Environmental science & technology.

[46]  T. J. Ptak,et al.  PARTICULATE CONCENTRATION IN AUTOMOBILE PASSENGER COMPARTMENTS , 1994 .

[47]  S. Friedlander,et al.  Size distributions of polycyclic aromatic hydrocarbons and elemental carbon. 1. Sampling, measurement methods, and source characterization. , 1994, Environmental science & technology.

[48]  Yuji Horie On-road motor vehicle activity data , 1994 .

[49]  W. Carter,et al.  Computer modeling study of incremental hydrocarbon reactivity , 1989 .

[50]  Stephen A. Wise,et al.  Mobile sources of atmospheric polycyclic aromatic hydrocarbons: a roadway tunnel study , 1989 .

[51]  SARI ALM,et al.  Urban commuter exposure to particle matter and carbon monoxide inside an automobile , 1999, Journal of Exposure Analysis and Environmental Epidemiology.

[52]  Gwilym M. Jenkins,et al.  Time series analysis, forecasting and control , 1972 .

[53]  Charles Rodes,et al.  Measuring concentrations of selected air pollutants inside California vehicles : final report , 1998 .

[54]  W. B. Petersen,et al.  Carbon Monoxide Exposures to Los Angeles Area Commuters , 1982 .

[55]  George E. P. Box,et al.  Intervention Analysis with Applications to Economic and Environmental Problems , 1975 .

[56]  P. S. Nielsen,et al.  Biomarkers for exposure to ambient air pollution--comparison of carcinogen-DNA adduct levels with other exposure markers and markers for oxidative stress. , 1999, Environmental health perspectives.

[57]  D. Grosjean,et al.  Determination of nanogram amounts of carbonyls as 2,4-dinitrophenylhydrazones by high-performance liquid chromatography , 1981 .

[58]  Eduardo Behrentz,et al.  Measuring self-pollution in school buses using a tracer gas technique , 2004 .

[59]  Scott Fruin,et al.  Black carbon concentrations in California vehicles and estimation of in-vehicle diesel exhaust particulate matter exposures , 2004 .

[60]  Long-Path Open-Path Fourier Compendium of Methods for the Determination of Toxic Organic Compounds in Ambient Air , 1999 .

[61]  R. Harley,et al.  On-road measurement of carbonyls in California light-duty vehicle emissions. , 2001, Environmental science & technology.

[62]  L. Chan,et al.  A study of bus commuter and pedestrian exposure to traffic air pollution in Hong Kong , 1993 .

[63]  Phillip L. Williams,et al.  A comparison of two direct-reading aerosol monitors with the federal reference method for PM2.5 in indoor air , 2002 .

[64]  P J Lioy,et al.  Exposure to volatile organic compounds in the passenger compartment of automobiles during periods of normal and malfunctioning operation. , 1995, Journal of exposure analysis and environmental epidemiology.

[65]  P. S. Porter,et al.  Effects of changes in data reporting practices on trend assessments , 2000 .

[66]  Michael J. Kleeman,et al.  Evolution of atmospheric particles along trajectories crossing the Los Angeles basin , 2000 .

[67]  M. J. Norušis,et al.  SPSS 13.0 Guide to Data Analysis , 2000 .

[68]  E Z Conceição,et al.  Air quality inside the passenger compartment of a bus. , 1997, Journal of exposure analysis and environmental epidemiology.

[69]  H. Özkaynak,et al.  Commuter exposures to VOCs in Boston, Massachusetts. , 1991, Journal of the Air & Waste Management Association.