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dc.contributor.authorHeald, Colette L.
dc.contributor.authorCollett, J. L., Jr.
dc.contributor.authorLee, T.
dc.contributor.authorBenedict, K. B.
dc.contributor.authorSchwandner, F. M.
dc.contributor.authorLi, Y.
dc.contributor.authorClarisse, L.
dc.contributor.authorHurtmans, D. R.
dc.contributor.authorDamme, M. Van
dc.contributor.authorClerbaux, C.
dc.contributor.authorCoheur, P. -F.
dc.contributor.authorPhilip, S.
dc.contributor.authorMartin, R. V.
dc.contributor.authorPye, H. O. T.
dc.date.accessioned2013-03-15T19:35:36Z
dc.date.available2013-03-15T19:35:36Z
dc.date.issued2012-11
dc.date.submitted2012-10
dc.identifier.issn1680-7324
dc.identifier.issn1680-7316
dc.identifier.urihttp://hdl.handle.net/1721.1/77926
dc.description.abstractWe use in situ observations from the Interagency Monitoring of PROtected Visual Environments (IMPROVE) network, the Midwest Ammonia Monitoring Project, 11 surface site campaigns as well as Infrared Atmospheric Sounding Interferometer (IASI) satellite measurements with the GEOS-Chem model to investigate inorganic aerosol loading and atmospheric ammonia concentrations over the United States. IASI observations suggest that current ammonia emissions are underestimated in California and in the springtime in the Midwest. In California this underestimate likely drives the underestimate in nitrate formation in the GEOS-Chem model. However in the remaining continental United States we find that the nitrate simulation is biased high (normalized mean bias > = 1.0) year-round, except in Spring (due to the underestimate in ammonia in this season). None of the uncertainties in precursor emissions, the uptake efficiency of N[subscript 2]O[subscript 5] on aerosols, OH concentrations, the reaction rate for the formation of nitric acid, or the dry deposition velocity of nitric acid are able to explain this bias. We find that reducing nitric acid concentrations to 75% of their simulated values corrects the bias in nitrate (as well as ammonium) in the US. However the mechanism for this potential reduction is unclear and may be a combination of errors in chemistry, deposition and sub-grid near-surface gradients. This "updated" simulation reproduces PM and ammonia loading and captures the strong seasonal and spatial gradients in gas-particle partitioning across the United States. We estimate that nitrogen makes up 15−35% of inorganic fine PM mass over the US, and that this fraction is likely to increase in the coming decade, both with decreases in sulfur emissions and increases in ammonia emissions.en_US
dc.description.sponsorshipNational Oceanic and Atmospheric Administration. Oceans and Human Health Initiative (NA12OAR4310064)en_US
dc.language.isoen_US
dc.publisherCopernicus GmbHen_US
dc.relation.isversionofhttp://dx.doi.org/10.5194/acp-12-10295-2012en_US
dc.rightsCreative Commons Attributionen_US
dc.rights.urihttp://creativecommons.org/licenses/by/3.0/en_US
dc.sourceCopernicusen_US
dc.titleAtmospheric ammonia and particulate inorganic nitrogen over the United Statesen_US
dc.typeArticleen_US
dc.identifier.citationHeald, C. L. et al. “Atmospheric Ammonia and Particulate Inorganic Nitrogen over the United States.” Atmospheric Chemistry and Physics 12.21 (2012): 10295–10312.en_US
dc.contributor.departmentMassachusetts Institute of Technology. Department of Civil and Environmental Engineeringen_US
dc.contributor.mitauthorHeald, Colette L.
dc.relation.journalAtmospheric Chemistry and Physicsen_US
dc.eprint.versionFinal published versionen_US
dc.type.urihttp://purl.org/eprint/type/JournalArticleen_US
eprint.statushttp://purl.org/eprint/status/PeerRevieweden_US
dspace.orderedauthorsHeald, C. L.; J. L. Collett Jr., C. L.; Lee, T.; Benedict, K. B.; Schwandner, F. M.; Li, Y.; Clarisse, L.; Hurtmans, D. R.; Van Damme, M.; Clerbaux, C.; Coheur, P.-F.; Philip, S.; Martin, R. V.; Pye, H. O. T.en
dc.identifier.orcidhttps://orcid.org/0000-0003-2894-5738
mit.licensePUBLISHER_CCen_US
mit.metadata.statusComplete


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