Differences in BVOC oxidation and SOA formation above and below the forest canopy

dc.citation.articleNumber1805
dc.citation.firstpage1828en_US
dc.citation.journalTitleAtmospheric Chemistry and Physicsen_US
dc.citation.volumeNumber17en_US
dc.contributor.authorSchulze, Benjamin C.en_US
dc.contributor.authorWallace, Henry W.en_US
dc.contributor.authorFlynn, James H.en_US
dc.contributor.authorLefer, Barry L.en_US
dc.contributor.authorErickson, Matt H.en_US
dc.contributor.authorJobson, B. Tomen_US
dc.contributor.authorDusanter, Sebastienen_US
dc.contributor.authorGriffith, Stephen M.en_US
dc.contributor.authorHansen, Robert F.en_US
dc.contributor.authorStevens, Philip S.en_US
dc.contributor.authorVanReken, Timothyen_US
dc.contributor.authorGriffin, Robert J.en_US
dc.date.accessioned2017-03-07T17:07:15Z
dc.date.available2017-03-07T17:07:15Z
dc.date.issued2017en_US
dc.description.abstractGas-phase biogenic volatile organic compounds (BVOCs) are oxidized in the troposphere to produce secondary pollutants such as ozone (O3), organic nitrates (RONO2), and secondary organic aerosol (SOA). Two coupled zero-dimensional models have been used to investigate differences in oxidation and SOA production from isoprene and α-pinene, especially with respect to the nitrate radical (NO3), above and below a forest canopy in rural Michigan. In both modeled environments (above and below the canopy), NO3 mixing ratios are relatively small (< 0.5 pptv); however, daytime (08:00–20:00 LT) mixing ratios below the canopy are 2 to 3 times larger than those above. As a result of this difference, NO3 contributes 12 % of total daytime α-pinene oxidation below the canopy while only contributing 4 % above. Increasing background pollutant levels to simulate a more polluted suburban or peri-urban forest environment increases the average contribution of NO3 to daytime below-canopy α-pinene oxidation to 32 %. Gas-phase RONO2 produced through NO3 oxidation undergoes net transport upward from the below-canopy environment during the day, and this transport contributes up to 30 % of total NO3-derived RONO2 production above the canopy in the morning (∼ 07:00). Modeled SOA mass loadings above and below the canopy ultimately differ by less than 0.5 µg m−3, and extremely low-volatility organic compounds dominate SOA composition. Lower temperatures below the canopy cause increased partitioning of semi-volatile gas-phase products to the particle phase and up to 35 % larger SOA mass loadings of these products relative to above the canopy in the model. Including transport between above- and below-canopy environments increases above-canopy NO3-derived α-pinene RONO2 SOA mass by as much as 45 %, suggesting that below-canopy chemical processes substantially influence above-canopy SOA mass loadings, especially with regard to monoterpene-derived RONO2.en_US
dc.identifier.citationSchulze, Benjamin C., Wallace, Henry W., Flynn, James H., et al.. "Differences in BVOC oxidation and SOA formation above and below the forest canopy." <i>Atmospheric Chemistry and Physics,</i> 17, (2017) Copernicus Publications on behalf of the European Geosciences Union: 1828. http://dx.doi.org/10.5194/acp-17-1805-2017.
dc.identifier.doihttp://dx.doi.org/10.5194/acp-17-1805-2017en_US
dc.identifier.urihttps://hdl.handle.net/1911/94020
dc.language.isoengen_US
dc.publisherCopernicus Publications on behalf of the European Geosciences Union
dc.rightsThis work is distributed under the Creative Commons Attribution 3.0 License.en_US
dc.rights.urihttps://creativecommons.org/licenses/by/3.0/us/en_US
dc.titleDifferences in BVOC oxidation and SOA formation above and below the forest canopyen_US
dc.typeJournal articleen_US
dc.type.dcmiTexten_US
dc.type.publicationpublisher versionen_US
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