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<article language="en">
	<journal>
		<journal_title>Atmospheric Chemistry and Physics Discussions</journal_title>
		<journal_url>www.atmos-chem-phys-discuss.net</journal_url>
		<issn>1680-7367</issn>
		<eissn>1680-7375</eissn>
		<volume_number>10</volume_number>
		<issue_number>2</issue_number>
		<publication_year>2010</publication_year>
	</journal>
	<doi>10.5194/acpd-10-3547-2010</doi>
	<article_url>http://www.atmos-chem-phys-discuss.net/10/3547/2010/</article_url>
	<abstract_html>http://www.atmos-chem-phys-discuss.net/10/3547/2010/acpd-10-3547-2010.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys-discuss.net/10/3547/2010/acpd-10-3547-2010.pdf</fulltext_pdf>
	<start_page>3547</start_page>
	<end_page>3604</end_page>
	<publication_date>2010-02-09</publication_date>
	<article_title content_type="html">Investigation of the correlation between odd oxygen and secondary  organic aerosol in Mexico City and Houston</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>E. C. Wood</name>
			<email>ezrawood@aerodyne.com</email>
		</author>
		<author numeration="2" affiliations="1">
			<name>M. R. Canagaratna</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>S. C. Herndon</name>
		</author>
		<author numeration="4" affiliations="1,12">
			<name>J. H. Kroll</name>
		</author>
		<author numeration="5" affiliations="1">
			<name>T. B. Onasch</name>
		</author>
		<author numeration="6" affiliations="1">
			<name>C. E. Kolb</name>
		</author>
		<author numeration="7" affiliations="1">
			<name>D. R. Worsnop</name>
		</author>
		<author numeration="8" affiliations="2">
			<name>W. B. Knighton</name>
		</author>
		<author numeration="9" affiliations="3">
			<name>R. Seila</name>
		</author>
		<author numeration="10" affiliations="4">
			<name>M. Zavala</name>
		</author>
		<author numeration="11" affiliations="4">
			<name>L. T. Molina</name>
		</author>
		<author numeration="12" affiliations="5,6,13">
			<name>P. F. DeCarlo</name>
		</author>
		<author numeration="13" affiliations="5,6,7">
			<name>J. L. Jimenez</name>
		</author>
		<author numeration="14" affiliations="8">
			<name>A. J. Weinheimer</name>
		</author>
		<author numeration="15" affiliations="8">
			<name>D. J. Knapp</name>
		</author>
		<author numeration="16" affiliations="9">
			<name>B. T. Jobson</name>
		</author>
		<author numeration="17" affiliations="10">
			<name>J. Stutz</name>
		</author>
		<author numeration="18" affiliations="11">
			<name>W. C. Kuster</name>
		</author>
		<author numeration="19" affiliations="11">
			<name>E. J. Williams</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Aerodyne Research, Inc., Billerica, Massachusetts, USA</affiliation>
		<affiliation numeration="2" content_type="html">Department of Chemistry, Montana State University, Bozeman, Montana, USA</affiliation>
		<affiliation numeration="3" content_type="html">United States Environmental Protection Agency, Research Triangle Park, North Carolina, USA</affiliation>
		<affiliation numeration="4" content_type="html">Molina Center for Energy and the Environment, La Jolla, California, USA</affiliation>
		<affiliation numeration="5" content_type="html">Department of Atmospheric and Oceanic Sciences, University of Colorado, Boulder, Colorado, USA</affiliation>
		<affiliation numeration="6" content_type="html">Cooperative Institute for Research in the Environmental Sciences (CIRES), University of Colorado, Boulder, Colorado, USA</affiliation>
		<affiliation numeration="7" content_type="html">Department of Chemistry and Biochemistry, University of Colorado, Boulder, Colorado, USA</affiliation>
		<affiliation numeration="8" content_type="html">National Center for Atmospheric Research, Boulder, Colorado, USA</affiliation>
		<affiliation numeration="9" content_type="html">Department of Civil and Environmental Engineering, Washington State University, Pullman, Washington, USA</affiliation>
		<affiliation numeration="10" content_type="html">Department of Atmospheric and Oceanic Sciences, University of California, Los Angeles, California, USA</affiliation>
		<affiliation numeration="11" content_type="html">NOAA Earth System Research Laboratory, Boulder, Colorado, USA</affiliation>
		<affiliation numeration="12" content_type="html">now at: Department of Civil and Environmental Engineering, Massachusetts Institute of Technology, Cambridge, Massachusetts, USA</affiliation>
		<affiliation numeration="13" content_type="html">now at: Laboratory of Atmospheric Chemistry, Paul Scherrer Institute, Switzerland</affiliation>
	</affiliations>
	<abstract content_type="html">Many recent models underpredict secondary organic aerosol (SOA) particulate
matter (PM) concentrations in polluted regions, indicating serious
deficiencies in the models&apos; chemical mechanisms and/or missing SOA
precursors. Since tropospheric photochemical ozone production is much better
understood, we investigate the correlation of odd-oxygen ([O&lt;sub&gt;x&lt;/sub&gt;]≡[O&lt;sub&gt;3&lt;/sub&gt;]+[NO&lt;sub&gt;2&lt;/sub&gt;]) and the oxygenated component of organic
aerosol (OOA), which is interpreted as a surrogate for SOA. OOA and O&lt;sub&gt;x&lt;/sub&gt; 
measured in Mexico City in 2006 and Houston in 2000 were well correlated
in air masses where both species were formed on similar timescales (less than
8 h) and not well correlated when their formation timescales or location
differed greatly. When correlated, the ratio of these two species ranged from
30 &amp;mu;g m&lt;sup&gt;&amp;minus;3&lt;/sup&gt; ppm&lt;sup&gt;&amp;minus;1&lt;/sup&gt; (STP) in Houston during time periods
affected by large petrochemical plant emissions to as high as
160 &amp;mu;g m&lt;sup&gt;&amp;minus;3&lt;/sup&gt; ppm&lt;sup&gt;&amp;minus;1&lt;/sup&gt; in Mexico City, where typical values
were near 120 &amp;mu;g m&lt;sup&gt;&amp;minus;3&lt;/sup&gt; ppm&lt;sup&gt;&amp;minus;1&lt;/sup&gt;. On several days in Mexico
City, the [OOA]/[O&lt;sub&gt;x&lt;/sub&gt;] ratio decreased by a factor of ~2
between 08:00 and 13:00 LT. This decrease is only partially attributable to
evaporation of the least oxidized and most volatile components of OOA;
differences in the diurnal emission trends and timescales for photochemical
processing of SOA precursors compared to ozone precursors also likely
contribute to the observed decrease. The extent of OOA oxidation increased
with photochemical aging. Calculations of the ratio of the SOA formation rate
to the O&lt;sub&gt;x&lt;/sub&gt; production rate using ambient VOC measurements and
traditional laboratory SOA yields are lower than the observed
[OOA]/[O&lt;sub&gt;x&lt;/sub&gt;] ratios by factors of 5 to 15, consistent with several
other models&apos; underestimates of SOA. Calculations of this ratio using
emission factors for organic compounds from gasoline and diesel exhaust do
not reproduce the observed ratio. Although not succesful in reproducing the
atmospheric observations presented, modeling &lt;i&gt;P&lt;/i&gt;(SOA)/&lt;i&gt;P&lt;/i&gt;(O&lt;sub&gt;x&lt;/sub&gt;) can
serve as a useful test of photochemical models using improved formulation
mechanisms for SOA.</abstract>
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