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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>7</volume_number>
		<issue_number>6</issue_number>
		<publication_year>2007</publication_year>
	</journal>
	<doi>10.5194/acpd-7-18269-2007</doi>
	<article_url>http://www.atmos-chem-phys-discuss.net/7/18269/2007/</article_url>
	<abstract_html>http://www.atmos-chem-phys-discuss.net/7/18269/2007/acpd-7-18269-2007.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys-discuss.net/7/18269/2007/acpd-7-18269-2007.pdf</fulltext_pdf>
	<start_page>18269</start_page>
	<end_page>18317</end_page>
	<publication_date>2007-12-20</publication_date>
	<article_title content_type="html">Fast airborne aerosol size and chemistry measurements with the high resolution aerosol mass spectrometer during the MILAGRO Campaign</article_title>
	<authors>
		<author numeration="1" affiliations="1,2">
			<name>P. F. DeCarlo</name>
		</author>
		<author numeration="2" affiliations="1">
			<name>E. J. Dunlea</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>J. R. Kimmel</name>
		</author>
		<author numeration="4" affiliations="1,3">
			<name>A. C. Aiken</name>
		</author>
		<author numeration="5" affiliations="1">
			<name>D. Sueper</name>
		</author>
		<author numeration="6" affiliations="4">
			<name>J. Crounse</name>
		</author>
		<author numeration="7" affiliations="4">
			<name>P. O. Wennberg</name>
		</author>
		<author numeration="8" affiliations="5">
			<name>L. Emmons</name>
		</author>
		<author numeration="9" affiliations="6">
			<name>Y. Shinozuka</name>
		</author>
		<author numeration="10" affiliations="6">
			<name>A. Clarke</name>
		</author>
		<author numeration="11" affiliations="6">
			<name>J. Zhou</name>
		</author>
		<author numeration="12" affiliations="7">
			<name>J. Tomlinson</name>
		</author>
		<author numeration="13" affiliations="7">
			<name>D. R. Collins</name>
		</author>
		<author numeration="14" affiliations="5">
			<name>D. Knapp</name>
		</author>
		<author numeration="15" affiliations="5">
			<name>A. J. Weinheimer</name>
		</author>
		<author numeration="16" affiliations="5">
			<name>D. D. Montzka</name>
		</author>
		<author numeration="17" affiliations="5">
			<name>T. Campos</name>
		</author>
		<author numeration="18" affiliations="1,3">
			<name>J. L. Jimenez</name>
			<email>jose.jimenez@colorado.edu</email>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Cooperative Institute for Research in Environmental Science (CIRES) University of Colorado, Boulder, CO, USA</affiliation>
		<affiliation numeration="2" content_type="html">Dept. of Atmospheric and Oceanic Science, Univ. of Colorado at Boulder, Boulder, CO, USA</affiliation>
		<affiliation numeration="3" content_type="html">Dept. of Chemistry and Biochemistry, University of Colorado at Boulder, Boulder, CO, USA</affiliation>
		<affiliation numeration="4" content_type="html">California Institute of Technology, Pasadena, CA, USA</affiliation>
		<affiliation numeration="5" content_type="html">National Center for Atmospheric Research, Boulder, CO, USA</affiliation>
		<affiliation numeration="6" content_type="html">Department of Oceanography, University of Hawaii, USA</affiliation>
		<affiliation numeration="7" content_type="html">Department of Meteorology, Texas A&amp;M University, College Station, TX, USA</affiliation>
	</affiliations>
	<abstract content_type="html">The concentration, size, and composition of non-refractory submicron aerosol
(NR-PM&lt;sub&gt;1&lt;/sub&gt;) was measured over Mexico City and central Mexico with a
High-Resolution Time-of-Flight Aerosol Mass Spectrometer (HR-ToF-AMS)
onboard the NSF/NCAR C-130 aircraft as part of the MILAGRO field campaign.
This was the first aircraft deployment of the HR-ToF-AMS, in which the
instrument performed very well, and provided 12 s data. The aerosol
mass from the AMS correlates strongly with other aerosol measurements on
board the aircraft. Organic aerosol (OA) species dominate the NR-PM&lt;sub&gt;1&lt;/sub&gt;
mass. OA correlates strongly with CO and HCN indicating that pollution
(mostly secondary OA, SOA) and biomass burning (BB) are the main OA sources.
The OA to CO ratio indicates a typical value for aged air of around 80 μg m&lt;sup&gt;&amp;minus;3&lt;/sup&gt; (STP) ppm&lt;sup&gt;&amp;minus;1&lt;/sup&gt;. This is within the range observed in outflow
from the Northeastern US, which could be due to a compensating effect
between higher BB but lower biogenic VOC emissions during this study. The
O/C atomic ratio for OA is calculated from the HR mass spectra and shows a
clear increase with photochemical age, as SOA forms rapidly and quickly
overwhelms primary urban OA, consistent with Volkamer et al. (2006) and
Kleinman et al. (2007b). BB OA is marked
by signals at &lt;i&gt;m/z&lt;/i&gt; 60 and 73, and also by a signal enhancement at large &lt;i&gt;m/z&lt;/i&gt;
indicative of larger molecules or more resistance to fragmentation. The main
inorganic components show different spatial patterns and size distributions.
Sulfate is regional in nature with clear volcanic and petrochemical/power
plant sources, while the urban area is not a major source for this species.
Nitrate is enhanced significantly in the urban area and immediate outflow,
and is strongly correlated with CO indicating a strong urban source. The
importance of nitrate decreases with distance from the city likely due to
evaporation. BB does not appear to be a strong source of nitrate despite its
high emissions of nitrogen oxides, presumably due to low ammonia emissions.
NR-chloride often correlates with HCN indicating a fire source, although
other sources likely contribute as well. This is the first aircraft study of
the regional evolution of aerosol chemistry from a tropical megacity.</abstract>
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</article>

