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<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" article-type="research-article" dtd-version="3.0" xml:lang="en">
<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-10-14611-2010</article-id>
<title-group>
<article-title>Variation of particle number size distributions and chemical compositions at  the urban and downwind regional sites in the Pearl River Delta during summertime pollution episodes</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Yue</surname>
<given-names>D. 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>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>Wu</surname>
<given-names>Z. J.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Guo</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>Wen</surname>
<given-names>M. T.</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>Nowak</surname>
<given-names>A.</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>Wehner</surname>
<given-names>B.</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>Wiedensohler</surname>
<given-names>A.</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>Takegawa</surname>
<given-names>N.</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>Kondo</surname>
<given-names>Y.</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>Wang</surname>
<given-names>X. 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>Li</surname>
<given-names>Y. P.</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. 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>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, 100871, China</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>Leibniz Institute for Tropospheric Research, Permoserstrasse 15, 04318 Leipzig, Germany</addr-line>
</aff>
<aff id="aff3">
<label>3</label>
<addr-line>Research Center for Advanced Science and Technology, University of Tokyo, Tokyo 153-8904, Japan</addr-line>
</aff>
<pub-date pub-type="epub">
<day>11</day>
<month>06</month>
<year>2010</year>
</pub-date>
<volume>10</volume>
<issue>6</issue>
<fpage>14611</fpage>
<lpage>14637</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-discuss.net/10/14611/2010/acpd-10-14611-2010.html">This article is available from http://www.atmos-chem-phys-discuss.net/10/14611/2010/acpd-10-14611-2010.html</self-uri>
<self-uri xlink:href="http://www.atmos-chem-phys-discuss.net/10/14611/2010/acpd-10-14611-2010.pdf">The full text article is available as a PDF file from http://www.atmos-chem-phys-discuss.net/10/14611/2010/acpd-10-14611-2010.pdf</self-uri>
<abstract>
<p>In order to characterize the features of particulate pollution
      in the Pearl River Delta (PRD) in the summer, continuous
      measurements of particle number size distributions and
      chemical compositions were simultaneously performed at
      Guangzhou urban site (GZ) and Back-garden downwind regional
      site (BG) in July 2006. Particle number concentration from
      20 nm to 10 μm at BG was
      (1.7±0.8)×10&lt;sup&gt;4&lt;/sup&gt; cm&lt;sup&gt;−3&lt;/sup&gt;, about 40% lower
      than that at GZ, (2.9±1.1)×10&lt;sup&gt;4&lt;/sup&gt; cm&lt;sup&gt;−3&lt;/sup&gt; with
      intensive traffic emissions. The total particle volume
      concentration at BG was
      94±34 μm&lt;sup&gt;3&lt;/sup&gt; cm&lt;sup&gt;−3&lt;/sup&gt;, similar to that at
      GZ, 96±43 μm&lt;sup&gt;3&lt;/sup&gt; cm&lt;sup&gt;−3&lt;/sup&gt;. More 20–100 nm
      particles, significantly affected by the traffic emissions,
      were observed at GZ, while 100–660 nm particle number
      concentrations were similar at both sites as they are more
      regional. PM&lt;sub&gt;2.5&lt;/sub&gt; values were also similar at GZ
      (69±43 μg m&lt;sup&gt;−3&lt;/sup&gt;) and BG
      (69±58 μg m&lt;sup&gt;−3&lt;/sup&gt;), indicating the fine
      particulate pollution in the PRD region to be regional. Two
      kinds of pollution episodes, the accumulation pollution
      episode and the regional transport pollution episode, were
      observed. Fine particles over 100 nm dominated both number
      and volume concentrations of total particles during the late
      periods of these pollution episodes. Accumulation and
      secondary transformations are two main reasons for the
      nighttime accumulation pollution episode. SO&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;&amp;minus;2&lt;/sup&gt;,
      NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;minus;&lt;/sup&gt;, and NH&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt; accounted for about
      60% in 100–660 nm particle mass and PM&lt;sub&gt;2.5&lt;/sub&gt;. When
      south or south-southeast wind prevailed in the PRD region,
      regional transport of pollutants takes place. Regional
      transport contributed about 30% to fine particulate
      pollution at BG during a regional transport case. Secondary
      transformation played an important role during regional
      transport, causing higher increase rates of secondary ions in
      PM&lt;sub&gt;1.0&lt;/sub&gt; than other species and shifting the peaks of
      sulfate and ammonium mass size distributions to larger
      sizes. SO&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;&amp;minus;2&lt;/sup&gt;, NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;minus;&lt;/sup&gt;, and
      NH&lt;sub&gt;4&lt;/sub&gt;&lt;sup&gt;+&lt;/sup&gt; accounted for about 70% and 40% of
      PM&lt;sub&gt;1.0&lt;/sub&gt; and PM&lt;sub&gt;2.5&lt;/sub&gt;, respectively.</p>
</abstract>
<counts><page-count count="27"/></counts>
</article-meta>
</front>
<body/>
<back>
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