Emission factors and evolution of SO2 measured from biomass burning in wildfires and agricultural fires

  • Pamela S. Rickly (Corresponding author)
  • , Hongyu Guo
  • , Pedro Campuzano-Jost
  • , Jose L. Jimenez
  • , Glenn M. Wolfe
  • , Ryan Bennett
  • , Ilann Bourgeois
  • , John D. Crounse
  • , Jack E. Dibb
  • , Joshua P. Digangi
  • , Glenn S. Diskin
  • , Maximilian Dollner
  • , Emily M. Gargulinski
  • , Samuel R. Hall
  • , Hannah S. Halliday
  • , Thomas F. Hanisco
  • , Reem A. Hannun
  • , Jin Liao
  • , Richard Moore
  • , Benjamin A. Nault
  • John B. Nowak, Jeff Peischl, Claire E. Robinson, Thomas Ryerson, Kevin J. Sanchez, Manuel Schöberl, Amber J. Soja, Jason M. St. Clair, Kenneth L. Thornhill, Kirk Ullmann, Paul O. Wennberg, Bernadett Weinzierl, Elizabeth B. Wiggins, Edward L. Winstead, Andrew W. Rollins (Corresponding author)

Publications: Contribution to journalArticlePeer Reviewed

Abstract

Fires emit sufficient sulfur to affect local and regional air quality and climate. This study analyzes SO2 emission factors and variability in smoke plumes from US wildfires and agricultural fires, as well as their relationship to sulfate and hydroxymethanesulfonate (HMS) formation. Observed SO2 emission factors for various fuel types show good agreement with the latest reviews of biomass burning emission factors, producing an emission factor range of 0.47-1.2gSO2kg-1C. These emission factors vary with geographic location in a way that suggests that deposition of coal burning emissions and application of sulfur-containing fertilizers likely play a role in the larger observed values, which are primarily associated with agricultural burning. A 0-D box model generally reproduces the observed trends of SO2 and total sulfate (inorganic + organic) in aging wildfire plumes. In many cases, modeled HMS is consistent with the observed organosulfur concentrations. However, a comparison of observed organosulfur and modeled HMS suggests that multiple organosulfur compounds are likely responsible for the observations but that the chemistry of these compounds yields similar production and loss rates as that of HMS, resulting in good agreement with the modeled results. We provide suggestions for constraining the organosulfur compounds observed during these flights, and we show that the chemistry of HMS can allow organosulfur to act as an S(IV) reservoir under conditions of pH>6 and liquid water content >10-7gsm-3. This can facilitate long-range transport of sulfur emissions, resulting in increased SO2 and eventually sulfate in transported smoke.
Original languageEnglish
Pages (from-to)15603-15620
Number of pages18
JournalAtmospheric Chemistry and Physics
Volume22
Issue number23
DOIs
Publication statusPublished - 13 Dec 2022

Funding

This research has been supported by the National Aeronautics and Space Administration (grant no. 20-UACO20-0021). Pamela S. Rickly and Andrew W. Rollins acknowledge support from NASA's Upper Atmosphere Composition Observations program. Maximilian Dollner, Manuel Schöberl, and Bernadett Weinzierl have received funding from the European Research Council (ERC) under the European Union's Horizon 2020 research and innovation framework program under grant agreement no. 640458 (A-LIFE) and from the University of Vienna. Hongyu Guo, Pedro Campuzano-Jost, and Jose L. Jimenez were supported by NASA 80NSSC18K0630 and 80NSSC21K1451 and NSF AGS-1822664. Glenn M. Wolfe, Thomas F. Hanisco, Reem A. Hannun, Jason M. St. Clair, and Jin Liao acknowledge support from the NASA Tropospheric Composition program and the NOAA AC4 program (NA17OAR4310004). Samuel R. Hall and Kirk Ullmann are funded under NASA grant 80NSSC18K0638. The National Center for Atmospheric Research is sponsored by the National Science Foundation. We would like to thank the NASA DC-8 crew and management team for support during FIREX-AQ integration and flights. Data from FIREX-AQ are available at https://www-air.larc.nasa.gov/cgi-bin/ArcView/firexaq (last access: 1 October 2021).

Austrian Fields of Science 2012

  • 103039 Aerosol physics
  • 103037 Environmental physics
  • 105208 Atmospheric chemistry

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