Secondary organic aerosol formation from ambient air in an oxidation flow reactor in central Amazonia

Secondary organic aerosol (SOA) formation from ambient air was studied using an oxidation flow reactor (OFR) coupled to an aerosol mass spectrometer (AMS) during both the wet and dry seasons at the Observations and Modeling of the Green Ocean Amazon (GoAmazon2014/5) field campaign. Measurements w...

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Main Authors: B. B. Palm, S. S. de Sá, D. A. Day, P. Campuzano-Jost, W. Hu, R. Seco, S. J. Sjostedt, J.-H. Park, A. B. Guenther, S. Kim, J. Brito, F. Wurm, P. Artaxo, R. Thalman, J. Wang, L. D. Yee, R. Wernis, G. Isaacman-VanWertz, A. H. Goldstein, Y. Liu, S. R. Springston, R. Souza, M. K. Newburn, M. L. Alexander, S. T. Martin, J. L. Jimenez
Format: Article
Language:English
Published: Copernicus Publications 2018-01-01
Series:Atmospheric Chemistry and Physics
Online Access:https://www.atmos-chem-phys.net/18/467/2018/acp-18-467-2018.pdf
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author B. B. Palm
B. B. Palm
S. S. de Sá
D. A. Day
D. A. Day
P. Campuzano-Jost
P. Campuzano-Jost
W. Hu
W. Hu
R. Seco
S. J. Sjostedt
J.-H. Park
J.-H. Park
A. B. Guenther
A. B. Guenther
S. Kim
J. Brito
J. Brito
F. Wurm
P. Artaxo
R. Thalman
R. Thalman
J. Wang
L. D. Yee
R. Wernis
G. Isaacman-VanWertz
G. Isaacman-VanWertz
A. H. Goldstein
A. H. Goldstein
Y. Liu
Y. Liu
S. R. Springston
R. Souza
M. K. Newburn
M. L. Alexander
S. T. Martin
S. T. Martin
J. L. Jimenez
J. L. Jimenez
spellingShingle B. B. Palm
B. B. Palm
S. S. de Sá
D. A. Day
D. A. Day
P. Campuzano-Jost
P. Campuzano-Jost
W. Hu
W. Hu
R. Seco
S. J. Sjostedt
J.-H. Park
J.-H. Park
A. B. Guenther
A. B. Guenther
S. Kim
J. Brito
J. Brito
F. Wurm
P. Artaxo
R. Thalman
R. Thalman
J. Wang
L. D. Yee
R. Wernis
G. Isaacman-VanWertz
G. Isaacman-VanWertz
A. H. Goldstein
A. H. Goldstein
Y. Liu
Y. Liu
S. R. Springston
R. Souza
M. K. Newburn
M. L. Alexander
S. T. Martin
S. T. Martin
J. L. Jimenez
J. L. Jimenez
Secondary organic aerosol formation from ambient air in an oxidation flow reactor in central Amazonia
Atmospheric Chemistry and Physics
author_facet B. B. Palm
B. B. Palm
S. S. de Sá
D. A. Day
D. A. Day
P. Campuzano-Jost
P. Campuzano-Jost
W. Hu
W. Hu
R. Seco
S. J. Sjostedt
J.-H. Park
J.-H. Park
A. B. Guenther
A. B. Guenther
S. Kim
J. Brito
J. Brito
F. Wurm
P. Artaxo
R. Thalman
R. Thalman
J. Wang
L. D. Yee
R. Wernis
G. Isaacman-VanWertz
G. Isaacman-VanWertz
A. H. Goldstein
A. H. Goldstein
Y. Liu
Y. Liu
S. R. Springston
R. Souza
M. K. Newburn
M. L. Alexander
S. T. Martin
S. T. Martin
J. L. Jimenez
J. L. Jimenez
author_sort B. B. Palm
title Secondary organic aerosol formation from ambient air in an oxidation flow reactor in central Amazonia
title_short Secondary organic aerosol formation from ambient air in an oxidation flow reactor in central Amazonia
title_full Secondary organic aerosol formation from ambient air in an oxidation flow reactor in central Amazonia
title_fullStr Secondary organic aerosol formation from ambient air in an oxidation flow reactor in central Amazonia
title_full_unstemmed Secondary organic aerosol formation from ambient air in an oxidation flow reactor in central Amazonia
title_sort secondary organic aerosol formation from ambient air in an oxidation flow reactor in central amazonia
publisher Copernicus Publications
series Atmospheric Chemistry and Physics
issn 1680-7316
1680-7324
publishDate 2018-01-01
description Secondary organic aerosol (SOA) formation from ambient air was studied using an oxidation flow reactor (OFR) coupled to an aerosol mass spectrometer (AMS) during both the wet and dry seasons at the Observations and Modeling of the Green Ocean Amazon (GoAmazon2014/5) field campaign. Measurements were made at two sites downwind of the city of Manaus, Brazil. Ambient air was oxidized in the OFR using variable concentrations of either OH or O<sub>3</sub>, over ranges from hours to days (O<sub>3</sub>) or weeks (OH) of equivalent atmospheric aging. The amount of SOA formed in the OFR ranged from 0 to as much as 10 µg m<sup>−3</sup>, depending on the amount of SOA precursor gases in ambient air. Typically, more SOA was formed during nighttime than daytime, and more from OH than from O<sub>3</sub> oxidation. SOA yields of individual organic precursors under OFR conditions were measured by standard addition into ambient air and were confirmed to be consistent with published environmental chamber-derived SOA yields. Positive matrix factorization of organic aerosol (OA) after OH oxidation showed formation of typical oxidized OA factors and a loss of primary OA factors as OH aging increased. After OH oxidation in the OFR, the hygroscopicity of the OA increased with increasing elemental O : C up to O : C ∼ 1.0, and then decreased as O : C increased further. Possible reasons for this decrease are discussed. The measured SOA formation was compared to the amount predicted from the concentrations of measured ambient SOA precursors and their SOA yields. While measured ambient precursors were sufficient to explain the amount of SOA formed from O<sub>3</sub>, they could only explain 10–50 % of the SOA formed from OH. This is consistent with previous OFR studies, which showed that typically unmeasured semivolatile and intermediate volatility gases (that tend to lack C = C bonds) are present in ambient air and can explain such additional SOA formation. To investigate the sources of the unmeasured SOA-forming gases during this campaign, multilinear regression analysis was performed between measured SOA formation and the concentration of gas-phase tracers representing different precursor sources. The majority of SOA-forming gases present during both seasons were of biogenic origin. Urban sources also contributed substantially in both seasons, while biomass burning sources were more important during the dry season. This study enables a better understanding of SOA formation in environments with diverse emission sources.
url https://www.atmos-chem-phys.net/18/467/2018/acp-18-467-2018.pdf
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spelling doaj-6b8d0bc528824232a2ff1919fed137ed2020-11-24T20:52:27ZengCopernicus PublicationsAtmospheric Chemistry and Physics1680-73161680-73242018-01-011846749310.5194/acp-18-467-2018Secondary organic aerosol formation from ambient air in an oxidation flow reactor in central AmazoniaB. B. Palm0B. B. Palm1S. S. de Sá2D. A. Day3D. A. Day4P. Campuzano-Jost5P. Campuzano-Jost6W. Hu7W. Hu8R. Seco9S. J. Sjostedt10J.-H. Park11J.-H. Park12A. B. Guenther13A. B. Guenther14S. Kim15J. Brito16J. Brito17F. Wurm18P. Artaxo19R. Thalman20R. Thalman21J. Wang22L. D. Yee23R. Wernis24G. Isaacman-VanWertz25G. Isaacman-VanWertz26A. H. Goldstein27A. H. Goldstein28Y. Liu29Y. Liu30S. R. Springston31R. Souza32M. K. Newburn33M. L. Alexander34S. T. Martin35S. T. Martin36J. L. Jimenez37J. L. Jimenez38Cooperative Institute for Research in Environmental Sciences, University of Colorado, Boulder, CO, USADept. of Chemistry, University of Colorado, Boulder, CO, USASchool of Engineering and Applied Sciences, Harvard University, Cambridge, MA, USACooperative Institute for Research in Environmental Sciences, University of Colorado, Boulder, CO, USADept. of Chemistry, University of Colorado, Boulder, CO, USACooperative Institute for Research in Environmental Sciences, University of Colorado, Boulder, CO, USADept. of Chemistry, University of Colorado, Boulder, CO, USACooperative Institute for Research in Environmental Sciences, University of Colorado, Boulder, CO, USADept. of Chemistry, University of Colorado, Boulder, CO, USADept. of Earth System Science, University of California, Irvine, CA, USAEarth System Research Laboratory, National Oceanic and Atmospheric Administration, Boulder, CO, USANational Center for Atmospheric Research, Boulder, CO, USAnow at: Climate and Air Quality Research Department, National Institute of Environmental Research (NIER), Incheon, 22689, Republic of KoreaDept. of Earth System Science, University of California, Irvine, CA, USADiv. of Atmospheric Sciences & Global Change, Pacific Northwest National Laboratory, Richland, WA, USADept. of Earth System Science, University of California, Irvine, CA, USAInstitute of Physics, University of São Paulo, São Paulo, Brazilnow at: Laboratory for Meteorological Physics (LaMP), Université Clermont Auvergne, 63000 Clermont-Ferrand, FranceInstitute of Physics, University of São Paulo, São Paulo, BrazilInstitute of Physics, University of São Paulo, São Paulo, BrazilEnvironmental and Climate Sciences Department, Brookhaven National Laboratory, Upton, NY, USAnow at: Department of Chemistry, Snow College, Richfield, UT, USAEnvironmental and Climate Sciences Department, Brookhaven National Laboratory, Upton, NY, USADepartment of Environmental Science, Policy, and Management, University of California, Berkeley, CA, USADepartment of Civil and Environmental Engineering, University of California, Berkeley, CA, USADepartment of Environmental Science, Policy, and Management, University of California, Berkeley, CA, USAnow at: Department of Civil and Environmental Engineering, Virginia Tech, Blacksburg, VA, USADepartment of Environmental Science, Policy, and Management, University of California, Berkeley, CA, USADepartment of Civil and Environmental Engineering, University of California, Berkeley, CA, USASchool of Engineering and Applied Sciences, Harvard University, Cambridge, MA, USAnow at: Department of Environmental Science, Policy, and Management, University of California, Berkeley, CA, USAEnvironmental and Climate Sciences Department, Brookhaven National Laboratory, Upton, NY, USAUniversity of the State of Amazonas, Manaus, BrazilEnvironmental and Molecular Sciences Laboratory, Pacific Northwest National Laboratory, Richland, WA, USAEnvironmental and Molecular Sciences Laboratory, Pacific Northwest National Laboratory, Richland, WA, USASchool of Engineering and Applied Sciences, Harvard University, Cambridge, MA, USADepartment of Earth and Planetary Sciences, Harvard University, Cambridge, MA, USACooperative Institute for Research in Environmental Sciences, University of Colorado, Boulder, CO, USADept. of Chemistry, University of Colorado, Boulder, CO, USASecondary organic aerosol (SOA) formation from ambient air was studied using an oxidation flow reactor (OFR) coupled to an aerosol mass spectrometer (AMS) during both the wet and dry seasons at the Observations and Modeling of the Green Ocean Amazon (GoAmazon2014/5) field campaign. Measurements were made at two sites downwind of the city of Manaus, Brazil. Ambient air was oxidized in the OFR using variable concentrations of either OH or O<sub>3</sub>, over ranges from hours to days (O<sub>3</sub>) or weeks (OH) of equivalent atmospheric aging. The amount of SOA formed in the OFR ranged from 0 to as much as 10 µg m<sup>−3</sup>, depending on the amount of SOA precursor gases in ambient air. Typically, more SOA was formed during nighttime than daytime, and more from OH than from O<sub>3</sub> oxidation. SOA yields of individual organic precursors under OFR conditions were measured by standard addition into ambient air and were confirmed to be consistent with published environmental chamber-derived SOA yields. Positive matrix factorization of organic aerosol (OA) after OH oxidation showed formation of typical oxidized OA factors and a loss of primary OA factors as OH aging increased. After OH oxidation in the OFR, the hygroscopicity of the OA increased with increasing elemental O : C up to O : C ∼ 1.0, and then decreased as O : C increased further. Possible reasons for this decrease are discussed. The measured SOA formation was compared to the amount predicted from the concentrations of measured ambient SOA precursors and their SOA yields. While measured ambient precursors were sufficient to explain the amount of SOA formed from O<sub>3</sub>, they could only explain 10–50 % of the SOA formed from OH. This is consistent with previous OFR studies, which showed that typically unmeasured semivolatile and intermediate volatility gases (that tend to lack C = C bonds) are present in ambient air and can explain such additional SOA formation. To investigate the sources of the unmeasured SOA-forming gases during this campaign, multilinear regression analysis was performed between measured SOA formation and the concentration of gas-phase tracers representing different precursor sources. The majority of SOA-forming gases present during both seasons were of biogenic origin. Urban sources also contributed substantially in both seasons, while biomass burning sources were more important during the dry season. This study enables a better understanding of SOA formation in environments with diverse emission sources.https://www.atmos-chem-phys.net/18/467/2018/acp-18-467-2018.pdf