Emissions of toxic pollutants from compressed natural gas and low sulfur diesel-fueled heavy-duty transit buses tested over multiple driving cycles.

The number of heavy-duty vehicles using alternative fuels such as compressed natural gas (CNG) and new low-sulfur diesel fuel formulations and equipped with after-treatment devices are projected to increase. However, few peer-reviewed studies have characterized the emissions of particulate matter (PM) and other toxic compounds from these vehicles. In this study, chemical and biological analyses were used to characterize the identifiable toxic air pollutants emitted from both CNG and low-sulfur-diesel-fueled heavy-duty transit buses tested on a chassis dynamometer over three transient driving cycles and a steady-state cruise condition. The CNG bus had no after-treatment, and the diesel bus was tested first equipped with an oxidation catalyst (OC) and then with a catalyzed diesel particulate filter (DPF). Emissions were analyzed for PM, volatile organic compounds (VOCs; determined on-site), polycyclic aromatic hydrocarbons (PAHs), and mutagenic activity. The 2000 model year CNG-fueled vehicle had the highest emissions of 1,3-butadiene, benzene, and carbonyls (e.g., formaldehyde) of the three vehicle configurations tested in this study. The 1998 model year diesel bus equipped with an OC and fueled with low-sulfur diesel had the highest emission rates of PM and PAHs. The highest specific mutagenic activities (revertants/microg PM, or potency) and the highest mutagen emission rates (revertants/mi) were from the CNG bus in strain TA98 tested over the New York Bus (NYB) driving cycle. The 1998 model year diesel bus with DPF had the lowest VOCs, PAH, and mutagenic activity emission. In general, the NYB driving cycle had the highest emission rates (g/mi), and the Urban Dynamometer Driving Schedule (UDDS) had the lowest emission rates for all toxics tested over the three transient test cycles investigated. Also, transient emissions were, in general, higher than steady-state emissions. The emissions of toxic compounds from an in-use CNG transit bus (without an oxidation catalyst) and from a vehicle fueled with low-sulfur diesel fuel (equipped with DPF) were lower than from the low-sulfur diesel fueled vehicle equipped with OC. All vehicle configurations had generally lower emissions of toxics than an uncontrolled diesel engine. Tunnel backgrounds (measurements without the vehicle running) were measured throughout this study and were helpful in determining the incremental increase in pollutant emissions. Also, the on-site determination of VOCs, especially 1,3-butadiene, helped minimize measurement losses due to sample degradation after collection.

[1]  Eduardo Behrentz,et al.  Characterizing the range of children's air pollutant exposure during school bus commutes , 2005, Journal of Exposure Analysis and Environmental Epidemiology.

[2]  B. Holmén,et al.  Ultrafine PM emissions from natural gas, oxidation-catalyst diesel, and particle-trap diesel heavy-duty transit buses. , 2002, Environmental science & technology.

[3]  Nigel N. Clark,et al.  Speciation of Organic Compounds from the Exhaust of Trucks and Buses: Effect of Fuel and After-Treatment on Vehicle Emission Profiles , 2002 .

[4]  V. O. Wagner,et al.  Mutagenicity of emissions from a natural gas fueled truck. , 2002, Mutation research.

[5]  Alberto Ayala,et al.  Diesel and CNG Heavy-duty Transit Bus Emissions over Multiple Driving Schedules: Regulated Pollutants and Project Overview , 2002 .

[6]  N. Clark,et al.  Year-Long Evaluation of Trucks and Buses Equipped with Passive Diesel Particulate Filters , 2002 .

[7]  R Westerholm,et al.  Comparison of exhaust emissions from Swedish environmental classified diesel fuel (MK1) and European Program on Emissions, Fuels and Engine Technologies (EPEFE) reference fuel: a chemical and biological characterization, with viewpoints on cancer risk. , 2001, Environmental science & technology.

[8]  Dana Lowell,et al.  Performance and Durability Evaluation of Continuously Regenerating Particulate Filters on Diesel Powered Urban Buses at NY City Transit , 2001 .

[9]  R. Okamoto,et al.  AIRBORNE PARTICLE EMISSIONS FROM 2- AND 4-STROKE OUTBOARD MARINE ENGINES: POLYCYCLIC AROMATIC HYDROCARBON AND BIOASSAY ANALYSES , 2000 .

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

[11]  T. McKone,et al.  Simple and rapid extraction of polycyclic aromatic hydrocarbons collected on polyurethane foam adsorbent , 1998 .

[12]  J. M. Norbeck,et al.  Evaluation of factors that affect diesel exhaust toxicity. Final report , 1998 .

[13]  N. Kado,et al.  A simple modification of the Salmonella liquid-incubation assay. Increased sensitivity for detecting mutagens in human urine. , 1983, Mutation research.

[14]  B. Ames,et al.  Methods for detecting carcinogens and mutagens with the Salmonella/mammalian-microsome mutagenicity test. , 1975, Mutation research.

[15]  N. Kado,et al.  Mutagenicity of fine (< 2.5 μm) airborne particles: Diurnal variation in community air determined by a salmonella micro preincubation (microsuspension) procedure , 1986 .