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Volume 13, issue 1
Atmos. Chem. Phys., 13, 359-391, 2013
© Author(s) 2013. This work is distributed under
the Creative Commons Attribution 3.0 License.
Atmos. Chem. Phys., 13, 359-391, 2013
© Author(s) 2013. This work is distributed under
the Creative Commons Attribution 3.0 License.

Research article 14 Jan 2013

Research article | 14 Jan 2013

Impacts of transported background pollutants on summertime western US air quality: model evaluation, sensitivity analysis and data assimilation

M. Huang6,1, G. R. Carmichael1, T. Chai2, R. B. Pierce3, S. J. Oltmans4, D. A. Jaffe5, K. W. Bowman6, A. Kaduwela7, C. Cai7, S. N. Spak8,1, A. J. Weinheimer9, L. G. Huey10, and G. S. Diskin11 M. Huang et al.
  • 1Center for Global and Regional Environmental Research, University of Iowa, Iowa City, IA 52242, USA
  • 2NOAA/OAR/ARL, College Park, MD 20740, USA
  • 3NOAA/NESDIS, Madison, WI 53706, USA
  • 4NOAA/ESRL, Boulder, CO 80305, USA
  • 5University of Washington, Bothell, WA 98011, USA
  • 6Jet Propulsion Laboratory, California Institute of Technology, Pasadena, CA 91109, USA
  • 7California Air Resources Board, Sacramento, CA 95812, USA
  • 8Public Policy Center, University of Iowa, Iowa City, IA 52242, USA
  • 9National Center for Atmospheric Research, Boulder, CO 80305, USA
  • 10School of Earth and Atmospheric Sciences, Georgia Institute of Technology, Atlanta, GA 30332, USA
  • 11NASA Langley Research Center, Hampton, VA 23681, USA

Abstract. The impacts of transported background (TBG) pollutants on western US ozone (O3) distributions in summer 2008 are studied using the multi-scale Sulfur Transport and dEposition Modeling system. Forward sensitivity simulations show that TBG contributes ~30–35 ppb to the surface Monthly mean Daily maximum 8-h Average O3 (MDA8) over Pacific Southwest (US Environmental Protection Agency (EPA) Region 9, including California, Nevada and Arizona) and Pacific Northwest (EPA Region 10, including Washington, Oregon and Idaho), and ~10–17 ppm-h to the secondary standard metric "W126 monthly index" over EPA Region 9 and ~3–4 ppm-h over Region 10. The strongest TBG impacts on W126 occur over the grass/shrub-covered regions. Among TBG pollutants, O3 is the major contributor to surface O3, while peroxyacetyl nitrate is the most important O3 precursor species. W126 shows larger responses than MDA8 to perturbations in TBG and stronger non-linearity to the magnitude of perturbations. The TBG impacts on both metrics overall negatively correlate to model vertical resolution and positively correlate to the horizontal resolution.

The mechanisms that determine TBG contributions and their variation are analyzed using trajectories and the receptor-based adjoint sensitivity analysis, which demonstrate the connection between the surface O3 and O3 aloft (at ~1–4 km) 1–2 days earlier. The probabilities of airmasses originating from Mt. Bachelor (2.7 km) and 2.5 km above Trinidad Head (THD) entraining into the boundary layer reach daily maxima of 66% and 34% at ~03:00 p.m. Pacific Daylight Time (PDT), respectively, and stay above 50% during 09:00 a.m.–04:00 p.m. PDT for those originating 1.5 km above California's South Coast.

Assimilation of the surface in-situ measurements significantly reduced the errors in the modeled surface O3 during a long-range transport episode by ~5 ppb on average (up to ~17 ppb) and increased the estimated TBG contributions by ~3 ppb. Available O3 vertical profiles from Tropospheric Emission Spectrometer (TES), Ozone Monitoring Instrument (OMI) and THD sonde identified this transport event, but assimilation of these observations in this case did not efficiently improve the O3 distributions except near the sampling locations, due to their limited spatiotemporal resolution and/or possible uncertainties.

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