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<front>
<journal-meta>
<journal-id journal-id-type="publisher">ACP</journal-id>
<journal-title-group>
<journal-title>Atmospheric Chemistry and Physics</journal-title>
<abbrev-journal-title abbrev-type="publisher">ACP</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">1680-7324</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/acp-8-4499-2008</article-id>
<title-group>
<article-title>Measurement of ambient aerosols in northern Mexico City by single particle mass spectrometry</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Moffet</surname>
<given-names>R. C.</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>de Foy</surname>
<given-names>B.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Molina</surname>
<given-names>L. T.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Molina</surname>
<given-names>M. J.</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>Prather</surname>
<given-names>K. A.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
</contrib-group><aff id="aff1">
<label>1</label>
<addr-line>University of California, San Diego, La Jolla, California, USA</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>Molina Center for Energy and the Environment (MCE2), La Jolla, California, USA</addr-line>
</aff>
<aff id="aff3">
<label>3</label>
<addr-line>Saint Louis University, St. Louis, Missouri, USA</addr-line>
</aff>
<aff id="aff4">
<label>4</label>
<addr-line>Massachusetts Institute of Technology, Cambridge, Massachusetts, USA</addr-line>
</aff>
<pub-date pub-type="epub">
<day>05</day>
<month>08</month>
<year>2008</year>
</pub-date>
<volume>8</volume>
<issue>16</issue>
<fpage>4499</fpage>
<lpage>4516</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>
<self-uri xlink:href="http://www.atmos-chem-phys.net/8/4499/2008/acp-8-4499-2008.html">This article is available from http://www.atmos-chem-phys.net/8/4499/2008/acp-8-4499-2008.html</self-uri>
<self-uri xlink:href="http://www.atmos-chem-phys.net/8/4499/2008/acp-8-4499-2008.pdf">The full text article is available as a PDF file from http://www.atmos-chem-phys.net/8/4499/2008/acp-8-4499-2008.pdf</self-uri>
<abstract>
<p>Continuous ambient measurements with aerosol time-of-flight mass spectrometry
(ATOFMS) were made in an industrial/residential section in the northern part
of Mexico City as part of the Mexico City Metropolitan Area-2006 campaign
(MCMA-2006). Results are presented for the period of 15â€“27 March 2006. The
submicron size mode contained both fresh and aged biomass burning, aged
organic carbon (OC) mixed with nitrate and sulfate, elemental carbon (EC),
nitrogen-organic carbon, industrial metal, and inorganic NaK inorganic
particles. Overall, biomass burning and aged OC particle types comprised 40%
and 31%, respectively, of the submicron mode. In contrast, the supermicron
mode was dominated by inorganic NaK particle types (42%) which represented a
mixture of dry lake bed dust and industrial NaK emissions mixed with soot.
Additionally, aluminosilicate dust, transition metals, OC, and biomass
burning contributed to the supermicron particles. Early morning periods
(2â€“6 a.m.) showed high fractions of inorganic particles from industrial
sources in the northeast, composed of internal mixtures of Pb, Zn, EC and Cl,
representing up to 73% of the particles in the 0.2â€“3&amp;mu;m size range. A
unique nitrogen-containing organic carbon (NOC) particle type, peaking in the
early morning hours, was hypothesized to be amines from local industrial
emissions based on the time series profile and back trajectory analysis. A
strong dependence on wind speed and direction was observed in the single
particle types that were present during different times of the day. The early
morning (3:30â€“10 a.m.) showed the greatest contributions from industrial
emissions. During mid to late mornings (7â€“11 a.m.), weak northerly winds
were observed along with the most highly aged particles. Stronger winds from
the south picked up in the late morning (after 11 a.m.), resulting in a
decrease in the concentrations of the major aged particle types and an
increase in the number fraction of fresh biomass particles. The highest wind
speeds were correlated with the highest number fraction of fresh biomass
particles (up to 76% of the submicron number fraction) when winds were
coming directly from fires that were located south and southeast of the city
based on MODIS fire count data. This study provides a unique clock of hourly
changes in single particle mixing state and sources as a function of
meteorology in Mexico City. These new findings indicate that biomass burning
and industrial emissions can make significant contributions to primary
particle loadings in Mexico City that are strongly coupled with local
meteorology.</p>
</abstract>
<counts><page-count count="18"/></counts>
</article-meta>
</front>
<body/>
<back>
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