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<front>
<journal-meta>
<journal-id journal-id-type="publisher">ACPD</journal-id>
<journal-title-group>
<journal-title>Atmospheric Chemistry and Physics Discussions</journal-title>
<abbrev-journal-title abbrev-type="publisher">ACPD</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">1680-7375</issn>
<publisher><publisher-name>Copernicus GmbH</publisher-name>
<publisher-loc>GÃ¶ttingen, Germany</publisher-loc>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.5194/acpd-9-12207-2009</article-id>
<title-group>
<article-title>Modeling organic aerosols during MILAGRO: application of the CHIMERE model and importance of biogenic secondary organic aerosols</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Hodzic</surname>
<given-names>A.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Jimenez</surname>
<given-names>J. L.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Madronich</surname>
<given-names>S.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Aiken</surname>
<given-names>A. C.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Bessagnet</surname>
<given-names>B.</given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Curci</surname>
<given-names>G.</given-names>
</name>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Fast</surname>
<given-names>J.</given-names>
</name>
<xref ref-type="aff" rid="aff5">
<sup>5</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Lamarque</surname>
<given-names>J. F.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Onasch</surname>
<given-names>T. B.</given-names>
</name>
<xref ref-type="aff" rid="aff6">
<sup>6</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Roux</surname>
<given-names>G.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Ulbrich</surname>
<given-names>I. M.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
</contrib-group><aff id="aff1">
<label>1</label>
<addr-line>National Center for Atmospheric Research, Boulder, CO, USA</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>University of Colorado, Boulder, CO, USA</addr-line>
</aff>
<aff id="aff3">
<label>3</label>
<addr-line>Inst. Natl. Environm. Ind. &amp; Risques, INERIS, 60550 Verneuil en Halatte, France</addr-line>
</aff>
<aff id="aff4">
<label>4</label>
<addr-line>Universita&apos; degli Studi dell&apos;Aquila, Italy</addr-line>
</aff>
<aff id="aff5">
<label>5</label>
<addr-line>Pacific Northwest National Laboratory, Richland, WA, USA</addr-line>
</aff>
<aff id="aff6">
<label>6</label>
<addr-line>Aerodyne Research, MA, USA</addr-line>
</aff>
<pub-date pub-type="epub">
<day>19</day>
<month>05</month>
<year>2009</year>
</pub-date>
<volume>9</volume>
<issue>3</issue>
<fpage>12207</fpage>
<lpage>12281</lpage>
<permissions>
<license xlink:type="simple">
<license-p>This is an open-access article ditributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.</license-p>
</license>
</permissions>
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<self-uri xlink:href="http://www.atmos-chem-phys-discuss.net/9/12207/2009/acpd-9-12207-2009.pdf">The full text article is available as a PDF file from http://www.atmos-chem-phys-discuss.net/9/12207/2009/acpd-9-12207-2009.pdf</self-uri>
<abstract>
<p>The meso-scale chemistry-transport model CHIMERE is used to assess our
understanding of major sources and formation processes leading to a fairly
large amount of organic aerosols (OA, including primary OA (POA) and
secondary OA (SOA)) observed in Mexico City during the MILAGRO field project
(March 2006). Chemical analyses of submicron aerosols from aerosol mass
spectrometers (AMS) indicate that organic particles found in the Mexico City
basin contain a large fraction of oxygenated organic species (OOA) which
have strong correspondence with SOA, and that their production actively
continues downwind of the city. The SOA formation is modeled here by the
one-step oxidation of anthropogenic (i.e. aromatics, alkanes), biogenic
(i.e. monoterpenes and isoprene), and biomass-burning SOA precursors and
their partitioning into both organic and aqueous phases. The near-surface
model evaluation shows that predicted OA correlates reasonably well with
measurements during the campaign, however it remains a factor of 2 lower
than the measured total OA. Fairly good agreement is found between predicted
and observed POA within the city suggesting that anthropogenic and biomass
burning emissions are reasonably captured. Consistent with previous studies
in Mexico City, large discrepancies are encountered for SOA, with a factor
of 2â€“10 model underestimate. When only anthropogenic SOA precursors were
considered, the model was able to reproduce within a factor of two the sharp
increase in SOA concentrations during the late morning at both urban and
near-urban locations but the discrepancy increases rapidly later in the day,
consistent with previous results, and is especially obvious when the
column-integrated SOA mass is considered instead of the surface
concentration. The increase in the missing SOA mass in the afternoon
coincides with the sharp drop in POA suggesting a tendency of the model to
excessively evaporate the freshly formed SOA. Predicted SOA concentrations
in our base case were extremely low when photochemistry was not active,
especially overnight, as the SOA formed in the previous day was mostly
quickly advected away from the basin. These nighttime discrepancies were not
significantly reduced when greatly enhanced partitioning to the aerosol
phase was assumed. Model sensitivity results suggest that observed nighttime
SOA concentrations are strongly influenced by a regional background SOA
(~1.5 Î¼g/m&lt;sup&gt;3&lt;/sup&gt;) of biogenic origin which is transported from
the coastal mountain ranges into the Mexico City basin. The relative
contribution of biogenic SOA to monthly mean modeled SOA levels is estimated
to be more than 30% within the city and up to 65â€“90% at the regional
scale (even in the immediate vicinity of the city) which may help explain
the significant amount of modern carbon in the aerosols inside the city
during low biomass burning periods. The anthropogenic emissions of isoprene
and its nighttime oxidation by NO&lt;sub&gt;3&lt;/sub&gt; were also found to enhance the SOA
mean concentrations within the city by an additional 15%. Our results
confirm the large underestimation of the SOA production by traditional
models in polluted regions (estimated as 10â€“20 Tons within the Mexico City
metropolitan area during the daily peak), and emphasize for the first time
the role of biogenic precursors in this region, indicating that they cannot
be neglected in modeling studies.</p>
</abstract>
<counts><page-count count="75"/></counts>
</article-meta>
</front>
<body/>
<back>
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