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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-10-17153-2010</article-id>
<title-group>
<article-title>Primary aerosol emission trends for China, 1990â€“2005</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Lei</surname>
<given-names>Y.</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>Zhang</surname>
<given-names>Q.</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>He</surname>
<given-names>K. B.</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>Streets</surname>
<given-names>D. G.</given-names>
</name>
<xref ref-type="aff" rid="aff4">
<sup>4</sup>
</xref>
</contrib>
</contrib-group><aff id="aff1">
<label>1</label>
<addr-line>State Key Joint Laboratory of Environment Simulation and Pollution Control, Department of  Environmental Science and Engineering, Tsinghua University, Beijing 100084, China</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>School of Engineering and Applied Science, Harvard University, Cambridge, Massachusetts, USA</addr-line>
</aff>
<aff id="aff3">
<label>3</label>
<addr-line>Center for Earth System Science, Tsinghua University, Beijing, China</addr-line>
</aff>
<aff id="aff4">
<label>4</label>
<addr-line>Decision and Information Sciences Division, Argonne National Laboratory, Argonne, Illinois, USA</addr-line>
</aff>
<pub-date pub-type="epub">
<day>12</day>
<month>07</month>
<year>2010</year>
</pub-date>
<volume>10</volume>
<issue>7</issue>
<fpage>17153</fpage>
<lpage>17212</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/10/17153/2010/acpd-10-17153-2010.pdf">The full text article is available as a PDF file from http://www.atmos-chem-phys-discuss.net/10/17153/2010/acpd-10-17153-2010.pdf</self-uri>
<abstract>
<p>An inventory of anthropogenic primary aerosol emissions in China was
developed for 1990â€“2005 using a technology-based approach. Taking into
account changes in the technology penetration within industry sectors and
improvements in emission controls driven by stricter emission standards,
a dynamic methodology was derived and implemented to estimate inter-annual
emission factors. Emission factors of PM&lt;sub&gt;2.5&lt;/sub&gt; decreased by
7%â€“69% from 1990 to 2005 in different industry sectors of China, and
emission factors of TSP decreased by 18%â€“80% as well. Emissions of
PM&lt;sub&gt;2.5&lt;/sub&gt;, PM&lt;sub&gt;10&lt;/sub&gt; and TSP presented similar trends: increased
in the first six years of 1990s and decreased until 2000, then increased
again in the following years. Emissions of TSP reached a historical high
(35.5 Tg) in 1996, while the peak of PM&lt;sub&gt;10&lt;/sub&gt; (18.8 Tg) and
PM&lt;sub&gt;2.5&lt;/sub&gt; (12.7 Tg) emissions occurred in 2005. Although various
emission trends were identified across sectors, the cement industry and
biofuel combustion in the residential sector were consistently the largest
sources of PM&lt;sub&gt;2.5&lt;/sub&gt; emissions, accounting for 53%â€“62% of
emission over the study period. The non-metallic mineral product industry,
including the cement, lime and brick industries, accounted for 54%â€“63%
of national TSP emissions. There were no significant trends of BC and OC
emissions until 2000, but the increase after 2000 brought the historical high
of BC (1.51 Tg) and OC (3.19 Tg) emissions in 2005. Although significant
improvements in the estimation of primary aerosols are presented, there still
exist large uncertainties. More accurate and detailed activity information
and emission factors based on local tests are essential to further improve
emission estimates, this especially being so for the brick and coke
industries, as well as for coal-burning stoves and biofuel usage in the
residential sector.</p>
</abstract>
<counts><page-count count="60"/></counts>
</article-meta>
</front>
<body/>
<back>
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