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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>Göttingen, Germany</publisher-loc>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.5194/acp-8-2701-2008</article-id>
<title-group>
<article-title>Spatiotemporal variations of ambient PM&lt;sub&gt;10&lt;/sub&gt; source contributions in Beijing in 2004 using positive matrix factorization</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Xie</surname>
<given-names>S. D.</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>Liu</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>Chen</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>Hua</surname>
<given-names>L.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
</contrib-group><aff id="aff1">
<label>1</label>
<addr-line>College of Environmental Sciences and Engineering, State Key Joint Laboratory of Environmental  Simulation and Pollution Control, Peking University, Beijing 100871, People&apos;s Republic of China</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>Beijing Municipal Environmental Monitoring Center, Beijing 100044, People&apos;s Republic of China</addr-line>
</aff>
<pub-date pub-type="epub">
<day>22</day>
<month>05</month>
<year>2008</year>
</pub-date>
<volume>8</volume>
<issue>10</issue>
<fpage>2701</fpage>
<lpage>2716</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.net/8/2701/2008/acp-8-2701-2008.pdf">The full text article is available as a PDF file from http://www.atmos-chem-phys.net/8/2701/2008/acp-8-2701-2008.pdf</self-uri>
<abstract>
<p>Source contributions to ambient PM&lt;sub&gt;10&lt;/sub&gt; (particles with an aerodynamic diameter
of 10 μm or less) in Beijing, China were determined with positive matrix
factorization (PMF) based on ambient PM&lt;sub&gt;10&lt;/sub&gt; composition data including
concentrations of organic carbon (OC), elemental carbon (EC), ions and metal
elements, which were simultaneously obtained at six sites through January,
April, July and October in 2004. Results from PMF indicated that seven major
sources of ambient PM&lt;sub&gt;10&lt;/sub&gt; were urban fugitive dust, crustal soil, coal
combustion, secondary sulfate, secondary nitrate, biomass burning with
municipal incineration, and vehicle emission, respectively. In paticular,
urban fugitive dust and crustal soil as two types of dust sources with
similar chemical characteristics were differentiated by PMF. Urban fugitive
dust contributed the most, accounting for 34.4% of total PM&lt;sub&gt;10&lt;/sub&gt; mass on an
annual basis, with relatively high contributions in all four months, and even
covered 50% in April. It also showed higher contributions in southwestern
and southeastern areas than in central urban areas. Coal combustion was found
to be the primary contributor in January, showing higher contributions in
urban areas than in suburban areas with seasonal variation peaking in winter,
which accounted for 15.5% of the annual average PM&lt;sub&gt;10&lt;/sub&gt; concentration.
Secondary sulfate and secondary nitrate combined as the largest contributor
to PM&lt;sub&gt;10&lt;/sub&gt; in July and October, with strong seasonal variation peaking in
summer, accounting for 38.8% and 31.5% of the total PM&lt;sub&gt;10&lt;/sub&gt; mass in July and
October, respectively. Biomass burning with municipal incineration
contributions were found in all four months and accounted for 9.8% of the
annual average PM&lt;sub&gt;10&lt;/sub&gt; mass concentration, with obviously higher contribution in
October than in other months. Incineration sources were probably located in
southwestern Beijing. Contribution from vehicle emission accounted for 5.0%
and exhibited no significant seasonal variation. In sum, PM&lt;sub&gt;10&lt;/sub&gt; source
contributions in Beijing showed not only significant seasonal variations but
also spatial differences.</p>
</abstract>
<counts><page-count count="16"/></counts>
</article-meta>
</front>
<body/>
<back>
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