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Agricultural fires in the southeastern U.S. during SEAC 4 RS: Emissions of trace gases and particles and evolution of ozone, reactive nitrogen, and organic aerosol
Author(s) -
Liu Xiaoxi,
Zhang Y.,
Huey L. G.,
Yokelson R. J.,
Wang Y.,
Jimenez J. L.,
CampuzanoJost P.,
Beyersdorf A. J.,
Blake D. R.,
Choi Y.,
St. Clair J. M.,
Crounse J. D.,
Day D. A.,
Diskin G. S.,
Fried A.,
Hall S. R.,
Hanisco T. F.,
King L. E.,
Meinardi S.,
Mikoviny T.,
Palm B. B.,
Peischl J.,
Perring A. E.,
Pollack I. B.,
Ryerson T. B.,
Sachse G.,
Schwarz J. P.,
Simpson I. J.,
Tanner D. J.,
Thornhill K. L.,
Ullmann K.,
Weber R. J.,
Wennberg P. O.,
Wisthaler A.,
Wolfe G. M.,
Ziemba L. D.
Publication year - 2016
Publication title -
journal of geophysical research: atmospheres
Language(s) - English
Resource type - Journals
eISSN - 2169-8996
pISSN - 2169-897X
DOI - 10.1002/2016jd025040
Subject(s) - aerosol , trace gas , ozone , plume , atmospheric sciences , environmental chemistry , environmental science , air quality index , peroxyacetyl nitrate , nitrogen , reactive nitrogen , nitrate , nox , chemistry , meteorology , combustion , geography , geology , organic chemistry
Emissions from 15 agricultural fires in the southeastern U.S. were measured from the NASA DC‐8 research aircraft during the summer 2013 Studies of Emissions and Atmospheric Composition, Clouds and Climate Coupling by Regional Surveys (SEAC 4 RS) campaign. This study reports a detailed set of emission factors (EFs) for 25 trace gases and 6 fine particle species. The chemical evolution of the primary emissions in seven plumes was examined in detail for ~1.2 h. A Lagrangian plume cross‐section model was used to simulate the evolution of ozone (O 3 ), reactive nitrogen species, and organic aerosol (OA). Observed EFs are generally consistent with previous measurements of crop residue burning, but the fires studied here emitted high amounts of SO 2 and fine particles, especially primary OA and chloride. Filter‐based measurements of aerosol light absorption implied that brown carbon (BrC) was ubiquitous in the plumes. In aged plumes, rapid production of O 3 , peroxyacetyl nitrate (PAN), and nitrate was observed with ΔO 3 /ΔCO, ΔPAN/ΔNO y , and Δnitrate/ΔNO y reaching ~0.1, ~0.3, and ~0.3. For five selected cases, the model reasonably simulated O 3 formation but underestimated PAN formation. No significant evolution of OA mass or BrC absorption was observed. However, a consistent increase in oxygen‐to‐carbon (O/C) ratios of OA indicated that OA oxidation in the agricultural fire plumes was much faster than in urban and forest fire plumes. Finally, total annual SO 2 , NO x , and CO emissions from agricultural fires in Arkansas, Louisiana, Mississippi, and Missouri were estimated (within a factor of ~2) to be equivalent to ~2% SO 2 from coal combustion and ~1% NO x and ~9% CO from mobile sources.