Examining the temperature dependence of ethanol (E85) versus gasoline emissions on air pollution with a largely-explicit chemical mechanism

Abstract The increased use of ethanol in transportation fuels warrants an investigation of its consequences. An important component of such an investigation is the temperature dependence of ethanol and gasoline exhaust chemistry. We use the Master Chemical Mechanism (MCM, version 3.1, LEEDS University) with the SMVGEAR II chemical ordinary differential solver to provide the speed necessary to simulate complex chemistry to examine such effects. The MCM has over 13,500 organic reactions and 4600 species. SMVGEAR II is a sparse-matrix Gear solver that reduces the computation time significantly while maintaining any specified accuracy. Although we use a box model for this study, we determine and demonstrate in a separate study that the speed of the MCM with SMVGEAR II allows the MCM to be modeled in 3-dimensions. We also verified the accuracy of the model in comparison with smog chamber data. We then use the model with species-resolved tailpipe emissions data for E85 (15% gasoline, 85% ethanol fuel blend) and gasoline vehicles to compare the impact of each on nitrogen oxides, organic gases, and ozone as a function of ambient temperature and background concentrations, using Los Angeles in 2020 as a base case. We use two different emissions sets – one is a compilation of exhaust and evaporative data taken near 24 °C and the other from exhaust data taken at −7 °C – to determine how atmospheric chemistry and emissions are affected by temperature. We include diurnal effects by examining two day scenarios. We find that, accounting for chemistry and dilution alone, the average ozone concentrations through the range of temperatures tested are higher with E85 than with gasoline by ∼7 part per billion volume (ppbv) at higher temperatures (summer conditions) to ∼39 ppbv at low temperatures and low sunlight (winter conditions) for an area with a high nitrogen oxide (NOx) to non-methane organic gas (NMOG) ratio. The results suggest that E85's effect on health through ozone formation becomes increasingly more significant relative to gasoline at colder temperatures due to the change in exhaust emission composition at lower temperatures. Acetaldehyde and formaldehyde concentrations are also much higher with E85 at cold temperatures, which is a concern because both are considered to be carcinogens. These could have implications for wintertime use of E85. Peroxy acetyl nitrate (PAN), another air pollutant of concern, increases with E85 by 0.3–8 ppbv. The sensitivity of the results to box size, initial background concentrations, background emissions, and water vapor were also examined.

[1]  João V de Assunção,et al.  Dioxins and furans in the atmosphere of São Paulo City, Brazil. , 2005, Chemosphere.

[2]  J. Gaffney,et al.  The impacts of combustion emissions on air quality and climate - From coal to biofuels and beyond , 2009 .

[3]  M. Jacobson Improvement of SMVGEAR II on vector and scalar machines through absolute error tolerance control , 1998 .

[4]  J. Gaffney,et al.  The search for clean alternative fuels: There's no such thing as a free lunch! , 1990 .

[5]  Keith A. Smith,et al.  N 2 O release from agro-biofuel production negates global warming reduction by replacing fossil fuels , 2007 .

[6]  M. Jenkin,et al.  Evaluation of detailed aromatic mechanisms (MCMv3 and MCMv3.1) against environmental chamber data , 2004 .

[7]  M. Jacobson Effects of ethanol (E85) versus gasoline vehicles on cancer and mortality in the United States. , 2007, Environmental science & technology.

[8]  M. Jenkin,et al.  Modelling of the photooxidation of toluene: conceptual ideas for validating detailed mechanisms , 2002 .

[9]  M. Jacobson,et al.  Comparison of a 4000-reaction chemical mechanism with the carbon bond IV and an adjusted carbon bond IV-EX mechanism using SMVGEAR II , 2000 .

[10]  M. C. Dodge,et al.  A photochemical kinetics mechanism for urban and regional scale computer modeling , 1989 .

[11]  G. Streit,et al.  Atmospheric chemistry of aldehydes: enhanced peroxyacetyl nitrate formation from ethanol-fueled vehicular emissions. , 1988, Environmental science & technology.

[12]  L. Lave,et al.  Environmental Implications of Alternative-Fueled Automobiles: Air Quality and Greenhouse Gas Tradeoffs , 2000 .

[13]  Stephen Polasky,et al.  Climate change and health costs of air emissions from biofuels and gasoline , 2009, Proceedings of the National Academy of Sciences.

[14]  Lisa Graham,et al.  Emissions from light duty gasoline vehicles operating on low blend ethanol gasoline and E85 , 2008 .

[15]  Michael J. Pilling,et al.  Development of a detailed chemical mechanism (MCMv3.1) for the atmospheric oxidation of aromatic hydrocarbons , 2004 .

[16]  R. Turco,et al.  SMVGEAR: A sparse-matrix, vectorized gear code for atmospheric models , 1994 .

[17]  F Black,et al.  CHARACTERIZATION OF ALTERNATIVE FUEL VEHICLE EMISSIONS COMPOSITION AND OZONE POTENTIAL , 1996 .

[18]  Steven S. McConnell,et al.  A Comparison of Ethanol and Butanol as Oxygenates Using a Direct-Injection, Spark-Ignition Engine , 2009 .

[19]  Mark A. Delucchi,et al.  Lifecycle Analyses of Biofuels , 2006 .

[20]  Jacinto F. Fabiosa,et al.  Use of U.S. Croplands for Biofuels Increases Greenhouse Gases Through Emissions from Land-Use Change , 2008, Science.

[21]  M. Jacobson Computation of global photochemistry with SMVGEAR II , 1995 .

[22]  Mark Z. Jacobson,et al.  Fundamentals of Atmospheric Modeling: Preface , 2005 .

[23]  Andrew D. Jones,et al.  Supporting Online Material for: Ethanol Can Contribute To Energy and Environmental Goals , 2006 .

[24]  S. Polasky,et al.  Land Clearing and the Biofuel Carbon Debt , 2008, Science.

[25]  K. T. Knapp,et al.  The Effect of Ethanol Fuel on the Emissions of Vehicles over a Wide Range of Temperatures. , 1998, Journal of the Air & Waste Management Association.

[26]  G. Arbilla,et al.  Formaldehyde and acetaldehyde in a high traffic street of Rio de Janeiro, Brazil , 2003 .

[27]  M. Jacobson,et al.  Global‐through‐urban nested three‐dimensional simulation of air pollution with a 13,600‐reaction photochemical mechanism , 2010 .

[28]  Dennys E. Angove,et al.  Evaluation of two MCM v3.1 alkene mechanisms using indoor environmental chamber data , 2005 .

[29]  Larry G. Anderson,et al.  Ethanol fuel use in Brazil: air quality impacts , 2009 .

[30]  D. Tilman,et al.  Carbon-Negative Biofuels from Low-Input High-Diversity Grassland Biomass , 2006, Science.

[31]  M. Jenkin,et al.  The tropospheric degradation of volatile organic compounds: a protocol for mechanism development , 1997 .

[32]  Adalgiza Fornaro,et al.  Wet deposition and related atmospheric chemistry in the Sao Paulo metropolis, Brazil: Part 2 - contribution of formic and acetic acids , 2003 .

[33]  John M. E. Storey,et al.  Fuel Economy and Emissions of the Ethanol-Optimized Saab 9-5 Biopower , 2007 .

[34]  E. Grosjean,et al.  Ambient levels of gas phase pollutants in Porto Alegre, Brazil , 1998 .

[35]  Andrew D. Jones,et al.  Energy and Greenhouse Impacts of Biofuels , 2007 .

[36]  G. Whitten Comment on “Potential Air Quality Effects of Using Ethanol−Gasoline Fuel Blends: A Field Study in Albuquerque, New Mexico” , 1998 .

[37]  Eben I. Lichtman,et al.  Primary atmospheric oxidation mechanism for toluene. , 2009, The journal of physical chemistry. A.

[38]  Shijin Shuai,et al.  The effect of ethanol blended diesel fuels on emissions from a diesel engine , 2003 .

[39]  Randal S. Martin,et al.  Potential Air Quality Effects of Using Ethanol−Gasoline Fuel Blends: A Field Study in Albuquerque, New Mexico , 1997 .

[40]  D. L. Fox Air pollution. [Review] , 1985 .

[41]  G. Arbilla,et al.  Computer modeling study of ethanol and aldheyde reactivities in Rio de Janeiro urban air , 2003 .