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<article language="en">
	<journal>
		<journal_title>Atmospheric Chemistry and Physics</journal_title>
		<journal_url>www.atmos-chem-phys.net</journal_url>
		<issn>1680-7316</issn>
		<eissn>1680-7324</eissn>
		<volume_number>9</volume_number>
		<issue_number>11</issue_number>
		<publication_year>2009</publication_year>
	</journal>
	<doi>10.5194/acp-9-3613-2009</doi>
	<article_url>http://www.atmos-chem-phys.net/9/3613/2009/</article_url>
	<abstract_html>http://www.atmos-chem-phys.net/9/3613/2009/acp-9-3613-2009.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys.net/9/3613/2009/acp-9-3613-2009.pdf</fulltext_pdf>
	<start_page>3613</start_page>
	<end_page>3628</end_page>
	<publication_date>2009-06-04</publication_date>
	<article_title content_type="html">Gas/particle partitioning of water-soluble organic aerosol in Atlanta</article_title>
	<authors>
		<author numeration="1" affiliations="1,4">
			<name>C. J. Hennigan</name>
		</author>
		<author numeration="2" affiliations="1,2">
			<name>M. H. Bergin</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>A. G. Russell</name>
		</author>
		<author numeration="4" affiliations="2,3">
			<name>A. Nenes</name>
		</author>
		<author numeration="5" affiliations="2">
			<name>R. J. Weber</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">School of Civil and Environmental Engineering, Georgia Institute of Technology, Georgia, USA</affiliation>
		<affiliation numeration="2" content_type="html">School of Earth and Atmospheric Sciences, Georgia Institute of Technology, Georgia, USA</affiliation>
		<affiliation numeration="3" content_type="html">School of Chemical and Biomolecular Engineering, Georgia Institute of Technology, Georgia, USA</affiliation>
		<affiliation numeration="4" content_type="html">now at: The Center for Atmospheric Particle Studies, Carnegie Mellon University, Pittsburgh, Pennsylvania, USA</affiliation>
	</affiliations>
	<abstract content_type="html">Gas and particle-phase organic carbon compounds soluble in water (e.g., WSOC)
were measured simultaneously in Atlanta throughout the summer of 2007 to
investigate gas/particle partitioning of ambient secondary organic aerosol
(SOA). Previous studies have established that, in the absence of biomass
burning, particulate WSOC (WSOC&lt;sub&gt;&lt;i&gt;p&lt;/i&gt;&lt;/sub&gt;) is mainly from secondary organic
aerosol (SOA) production. Comparisons between WSOC&lt;sub&gt;&lt;i&gt;p&lt;/i&gt;&lt;/sub&gt;, organic carbon (OC)
and elemental carbon (EC) indicate that WSOC&lt;sub&gt;&lt;i&gt;p&lt;/i&gt;&lt;/sub&gt; was a nearly comprehensive
measure of SOA in the Atlanta summertime. WSOC&lt;sub&gt;&lt;i&gt;p&lt;/i&gt;&lt;/sub&gt; and gas-phase WSOC
(WSOC&lt;sub&gt;&lt;i&gt;g&lt;/i&gt;&lt;/sub&gt;) concentrations both exhibited afternoon maxima, indicating that
photochemistry was a major route for SOA formation. An additional nighttime
maximum in the WSOC&lt;sub&gt;&lt;i&gt;g&lt;/i&gt;&lt;/sub&gt; concentration indicated a dark source for oxidized
organic gases, but this was not accompanied by detectable increases in
WSOC&lt;sub&gt;&lt;i&gt;p&lt;/i&gt;&lt;/sub&gt;. To study SOA formation mechanisms, WSOC gas/particle partitioning
was investigated as a function of temperature, RH, NO&lt;sub&gt;x&lt;/sub&gt;, O&lt;sub&gt;3&lt;/sub&gt;, and
organic aerosol mass concentration. No clear relationship was observed
between temperature and partitioning, possibly due to a simultaneous effect
from other temperature-dependent processes. For example, positive temperature
effects on emissions of biogenic SOA precursors and photochemical SOA
formation may have accounted for the observed similar proportional increases
of WSOC&lt;sub&gt;&lt;i&gt;p&lt;/i&gt;&lt;/sub&gt; and WSOC&lt;sub&gt;&lt;i&gt;g&lt;/i&gt;&lt;/sub&gt; with temperature. Relative humidity data
indicated a linear dependence between partitioning and predicted fine
particle liquid water. Lower NO&lt;sub&gt;x&lt;/sub&gt; concentrations were associated with
greater partitioning to particles, but WSOC partitioning had no visible
relation to O&lt;sub&gt;3&lt;/sub&gt; or fine particle OC mass concentration. There was,
however, a relationship between WSOC partitioning and the WSOC&lt;sub&gt;&lt;i&gt;p&lt;/i&gt;&lt;/sub&gt; concentration, suggesting a compositional dependence between
partitioning semi-volatile gases and the absorbing organic aerosol. Combined,
the overall results suggest two dominant SOA formation processes in urban
Atlanta during summer. One was the photochemical production of SOA from
presumably biogenic precursors that increased with the onset of sunrise and
peaked in the afternoon. The other, which showed no apparent diurnal pattern,
involved the partitioning of semi-volatile gases to liquid water, followed by
heterogeneous reactions. The co-emission of water vapor and biogenic VOCs
from vegetation may link these processes.</abstract>
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</article>

