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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>Göttingen, Germany</publisher-loc>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.5194/acpd-11-1891-2011</article-id>
<title-group>
<article-title>Characterization and source apportionment of submicron aerosol with aerosol mass spectrometer during the PRIDE-PRD 2006 campaign</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Xiao</surname>
<given-names>R.</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>Takegawa</surname>
<given-names>N.</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>Zheng</surname>
<given-names>M.</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>Kondo</surname>
<given-names>Y.</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>Miyazaki</surname>
<given-names>Y.</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>Miyakawa</surname>
<given-names>T.</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>Hu</surname>
<given-names>M.</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>Shao</surname>
<given-names>M.</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>Zeng</surname>
<given-names>L.</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>Gong</surname>
<given-names>Y.</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>Lu</surname>
<given-names>K.</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>Deng</surname>
<given-names>Z.</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>Zhao</surname>
<given-names>Y.</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>Zhang</surname>
<given-names>Y. H.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
</contrib-group><aff id="aff1">
<label>1</label>
<addr-line>State Key Joint Laboratory of Environmental Simulation and Pollution Control, College of Environmental Sciences and Engineering, Peking University, Beijing, China</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>Research Center for Advanced Science and Technology, University of Tokyo, Tokyo, Japan</addr-line>
</aff>
<aff id="aff3">
<label>3</label>
<addr-line>Institute of Low Temperature Science, Hokkaido University, Sapporo, Japan</addr-line>
</aff>
<aff id="aff4">
<label>4</label>
<addr-line>Research Institute of Chemical Defence, Beijing, China</addr-line>
</aff>
<aff id="aff5">
<label>5</label>
<addr-line>Air Quality Research Center, University of California, Davis, California, USA</addr-line>
</aff>
<pub-date pub-type="epub">
<day>19</day>
<month>01</month>
<year>2011</year>
</pub-date>
<volume>11</volume>
<issue>1</issue>
<fpage>1891</fpage>
<lpage>1937</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/11/1891/2011/acpd-11-1891-2011.pdf">The full text article is available as a PDF file from http://www.atmos-chem-phys-discuss.net/11/1891/2011/acpd-11-1891-2011.pdf</self-uri>
<abstract>
<p>Size-resolved chemical compositions of non-refractory submicron
      aerosol were measured using an Aerodyne quadrupole aerosol mass
      spectrometer (Q-AMS) at the rural site Back Garden (BG), located
      ~50 km northwest of Guangzhou in July 2006. This paper
      characterized the submicron aerosol particles of regional air
      pollution in Pearl River Delta (PRD) in the Southern China. Organics
      and sulfate dominated the submicron aerosol compositions, with average
      mass concentrations of 11.8&amp;plusmn;8.4 &amp;mu;g m&lt;sup&gt;−3&lt;/sup&gt; and
      13.5&amp;plusmn;8.7 &amp;mu;g m&lt;sup&gt;−3&lt;/sup&gt;, respectively. Unlike other
      air masses, the air masses originated from Southeast-South and passing
      through the PRD urban areas exhibited distinct bimodal size
      distribution characteristics for both organics and sulfate: the first
      mode peaked at vacuum aerodynamic diameters (&lt;i&gt;D&lt;/i&gt;&lt;sub&gt;va&lt;/sub&gt;)~200 nm and the second mode occurred at &lt;i&gt;D&lt;/i&gt;&lt;sub&gt;va&lt;/sub&gt; from
      300–700 nm. With the information from AMS, it was found from this
      study that the first mode of organics in PRD regional air masses was
      contributed by both secondary organic aerosol formation and
      combustion-related emissions, which is different from most findings in
      other urban areas (first mode of organics primarily from
      combustion-related emissions). The analysis of AMS mass spectra data
      by positive matrix factorization (PMF) model identified three sources
      of submicron organic aerosol including hydrocarbon-like organic
      aerosol (HOA), low volatility oxygenated organic aerosol (LV-OOA) and
      semi-volatile oxygenated organic aerosol (SV-OOA). The strong
      correlation between HOA and EC indicated primary combustion emissions
      as the major source of HOA while a close correlation between SV-OOA
      and semi-volatile secondary species nitrate as well as between LV-OOA
      and nonvolatile secondary species sulfate suggested secondary aerosol
      formation as the major source of SV-OOA and LV-OOA at the BG
      site. However, LV-OOA was more aged than SV-OOA as its spectra was
      highly correlated with the reference spectra of fulvic acid, an
      indicator of aged and oxygenated aerosol. The origin of HOA and OOA
      (the sum of LV-OOA and SV-OOA) has been further confirmed by the
      statistics that primary organic carbon (POC) and secondary organic
      carbon (SOC), estimated by the EC tracer method, were closely
      correlated with HOA and OOA, respectively. The results of the EC
      tracer method and of the PMF model revealed that primary organic
      aerosol (POA) constituted ~34–47% of OA mass and secondary
      organic aerosol (SOA) constituted ~53–66% of regional
      organic aerosol in PRD during summer reason. The presence of abundant
      SOA was consistent with water soluble organic carbon (WSOC) results
      (accounting for ~60% of OC on average) by Miyazaki
      et al. (2009) for the same campaign. OOA correlated well with WSOC
      at the BG site, indicating that most OOA were water soluble. More
      specifically, approximately 86% of LV-OOA and 61% of SV-OOA were
      estimated as water soluble species on the basis of carbon content
      comparison.</p>
</abstract>
<counts><page-count count="47"/></counts>
</article-meta>
</front>
<body/>
<back>
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