The effect of entrainment through atmospheric boundary layer growth on observed and modeled surface ozone in the Colorado Front Range

dc.contributor.authorKaser, L.
dc.contributor.authorPatton, E. G.
dc.contributor.authorPfister, G. G.
dc.contributor.authorWeinheimer, A. J.
dc.contributor.authorMontzka, D. D.
dc.contributor.authorFlocke, F.
dc.contributor.authorThompson, Anne M.
dc.contributor.authorStauffer, R. M.
dc.contributor.authorHalliday, H. S.
dc.date.accessioned2024-06-20T17:32:03Z
dc.date.available2024-06-20T17:32:03Z
dc.date.issued2017
dc.description.abstractOzone concentrations at the Earth's surface are controlled by meteorological and chemical processes and are a function of advection, entrainment, deposition, and net chemical production/loss. The relative contributions of these processes vary in time and space. Understanding the relative importance of these processes controlling surface ozone concentrations is an essential component for designing effective regulatory strategies. Here we focus on the diurnal cycle of entrainment through atmospheric boundary layer (ABL) growth in the Colorado Front Range. Aircraft soundings and surface observations collected in July/August 2014 during the DISCOVER-AQ/FRAPPÉ (Deriving Information on Surface conditions from Column and Vertically Resolved Observations Relevant to Air Quality/Front Range Air Pollution and Photochemistry Éxperiment) campaigns and equivalent data simulated by a regional chemical transport model are analyzed. Entrainment through ABL growth is most important in the early morning, fumigating the surface at a rate of ~5 ppbv/h. The fumigation effect weakens near noon and changes sign to become a small dilution effect in the afternoon on the order of -1 ppbv/h. The chemical transport model WRF-Chem (Weather Research and Forecasting Model with chemistry) underestimates ozone at all altitudes during this study on the order of 10–15 ppbv. The entrainment through ABL growth is overestimated by the model in the order of 0.6–0.8 ppbv/h. This results from differences in boundary layer growth in the morning and ozone concentration jump across the ABL top in the afternoon. This implicates stronger modeled fumigation in the morning and weaker modeled dilution after 11:00 LT.
dc.description.sponsorshipThe data for this paper are available at the FRPPE/DISCOVER-AQ data archive (http://www-air.larc.nasa.gov/missions/discover-aq/discover-aq.html). The authors would like to thank the State of Colorado and National Science Foundation for funding of FRAPPE and NASA for funding of DISCOVER-AQ and Colorado Department of Public Health and Environment (CDPHE) for providing surface ozone concentration observations at the sites in Fort Collins, Golden, Denver, and Chatfield. The authors would also like to acknowledge Audra McClure at NOAA for providing ozone measurements at the BAO tower and David Vangilst for water mixing ratio and potential temperature measurements on the NASA P-3B. We would like to thank Richard Clark at the Millersville University for MPL data in Ft. Collins, Raymond Hoff at the University of Maryland, Baltimore County for MPL data in Golden, Sigma Space for providing a MPL at the Platteville site, and Timothy Berkoff at NASA Langley Research Center for the MPL data analysis in Platteville. We also thank Travis Knepp and James Szykman, both at NASA Langley Research Center for ceilometer data at the BAO tower and in Golden. The authors acknowledge the use of WRF-Chem version 3.6.1 (http://www2.mmm.ucar.edu/wrf/users/download/get_source.html), Stu McKeen at NOAA for the NEI emissions inventory (ftp://aftp.fsl.noaa.gov/divisions/taq/emissions_data_2011/), and the use of WRF-Chem preprocessor tools for fire emissions, biogenic emissions, and chemical boundary conditions provided by the Atmospheric Chemistry Observations and Modeling Lab (ACOM) of NCAR (https://www2.acom.ucar.edu/wrf-chem/wrf-chem-tools-community). The authors gratefully acknowledge the NOAA Air Resources Laboratory (ARL) for the provision of the HYSPLIT transport and dispersion model and READY website (http://www.ready.noaa.gov) used in this publication. A. M. Thompson acknowledges funding from NASA's Earth venture DISCOVER-AQ grant to Penn State University (NNX10AR39G). G. G. Pfister acknowledges funding from the NASA AQAST project (grant NNX11AI51G). The National Center for Atmospheric Research is sponsored by the National Science Foundation.
dc.description.urihttps://agupubs.onlinelibrary.wiley.com/doi/full/10.1002/2016JD026245
dc.format.extent19 pages
dc.genreJournal articles
dc.identifierdoi:10.13016/m2xoc7-swkq
dc.identifier.citationKaser, L., E. G. Patton, G. G. Pfister, A. J. Weinheimer, D. D. Montzka, F. Flocke, A. M. Thompson, R. M. Stauffer, and H. S. Halliday. “The Effect of Entrainment through Atmospheric Boundary Layer Growth on Observed and Modeled Surface Ozone in the Colorado Front Range.” Journal of Geophysical Research: Atmospheres 122, no. 11 (2017): 6075–93. https://doi.org/10.1002/2016JD026245.
dc.identifier.urihttps://doi.org/10.1002/2016JD026245
dc.identifier.urihttp://hdl.handle.net/11603/34731
dc.language.isoen_US
dc.publisherAGU
dc.relation.isAvailableAtThe University of Maryland, Baltimore County (UMBC)
dc.relation.ispartofUMBC Faculty Collection
dc.relation.ispartofUMBC GESTAR II
dc.rightsThis work was written as part of one of the author's official duties as an Employee of the United States Government and is therefore a work of the United States Government. In accordance with 17 U.S.C. 105, no copyright protection is available for such works under U.S. Law.
dc.rightsPublic Domain
dc.rights.urihttps://creativecommons.org/publicdomain/mark/1.0/
dc.subjectdiscover-AQ
dc.subjectentrainment
dc.subjectmodeling
dc.subjectobservations
dc.subjecttropospheric ozone
dc.titleThe effect of entrainment through atmospheric boundary layer growth on observed and modeled surface ozone in the Colorado Front Range
dc.typeText
dcterms.creatorhttps://orcid.org/0000-0002-7829-0920

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