Evaluation and improvement of ammonia emissions inventories

Abstract Two case studies are performed to improve ammonia emissions inputs used to model fine particulate matter (PM2.5 is the portion of particulate matter smaller than 2.5 μm aerodynamic diameter) formation of ammonium sulfate and ammonium nitrate. Ammonia emissions are analyzed in detail for North Carolina and the San Joaquin Valley (SJV) of California, with a focus on the Charlotte, NC, and Fresno, California metropolitan areas. A new gridded ammonia emissions inventories suitable for atmospheric modeling for the two case study cities was also developed. Agricultural sources accounted for the bulk of ammonia emissions in both case studies. Livestock waste contributed about 80% in North Carolina and 64% in the SJV, while fertilizer application contributed about 6–7% in both domains. Forests and non-agricultural vegetation contributed 5% in North Carolina and 12% in the SJV. Motor vehicles accounted for about 6% of ammonia emissions in North Carolina and 14% in the SJV. In the Charlotte and Fresno urban areas, the distribution of emissions is less heavily weighted toward agricultural sources and more heavily weighted toward highway vehicles (highway vehicles account for an estimated 64% of emissions in Charlotte and 51% of emissions in Fresno). The emissions estimates for agricultural sources (livestock and fertilizer application) decline to approximately 14% in the winter for both the Charlotte and Fresno urban areas. Emissions estimates for soils and vegetation also decline to approximately 0 during the winter for both the Fresno and Charlotte area. As a result, motor vehicles account for a larger fraction (approximately 73% and 70% for Charlotte and Fresno, respectively) of winter ammonia emissions, particularly in the Charlotte urban area.

[1]  Matthew P. Fraser,et al.  Detection of Excess Ammonia Emissions from In-Use Vehicles and the Implications for Fine Particle Control , 1998 .

[2]  Viney P. Aneja,et al.  Characterization of atmospheric ammonia emissions from swine waste storage and treatment lagoons , 2000 .

[3]  William H. Schlesinger,et al.  A global budget for atmospheric NH3 , 1992 .

[4]  D Ledbury,et al.  1997 census of agriculture. , 1999 .

[5]  Viney P. Aneja,et al.  Agricultural ammonia emissions and ammonium concentrations associated with aerosols and precipitation in the southeast United States , 2003 .

[6]  David Fowler,et al.  Atmospheric nitrogen compounds II: emissions, transport, transformation, deposition and assessment , 2001 .

[7]  A. Bouwman,et al.  A global high‐resolution emission inventory for ammonia , 1997 .

[8]  Ellen Kinnee,et al.  UNITED STATES LAND USE INVENTORY FOR ESTIMATING BIOGENIC OZONE PRECURSOR EMISSIONS , 1997 .

[9]  Andrew J. Kean,et al.  On-Road Measurement of Ammonia and Other Motor Vehicle Exhaust Emissions , 2000 .

[10]  K. W. Van der Hoek Estimating ammonia emission factors in Europe: Summary of the work of the UNECE ammonia expert panel , 1998 .

[11]  Commercial fertilizers 1992 , 1992 .

[12]  Gode Gravenhorst,et al.  Evaluation of ammonia fluxes into the free atmosphere over Western Germany , 1980 .

[13]  V. Aneja,et al.  Analysis of ammonia, ammonium aerosols and acid gases in the atmosphere at a commercial hog farm in eastern North Carolina, USA , 1998 .

[14]  Theo Demmers,et al.  Ammonia emission factors for UK agriculture. , 2000 .

[15]  D. Fowler,et al.  Ammonia emissions from non-agricultural sources in the UK , 2000 .

[16]  Spyros N. Pandis,et al.  Response of Inorganic PM to Precursor Concentrations , 1998 .

[17]  P. Warneck Chemistry of the natural atmosphere , 1999 .

[18]  P. Riggan,et al.  Emissions of some trace gases from biomass fires , 1990 .

[19]  J. Duyzer,et al.  The dry deposition of ammonia onto a Douglas fir forest in the Netherlands , 1994 .

[20]  Jan Willem Erisman,et al.  Ammonia exchange over coniferous forest , 1998 .

[21]  Brussels eng Ammonia emissions to air in Western Europe , 1994 .