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<article language="en">
	<journal>
		<journal_title>Atmospheric Chemistry and Physics Discussions</journal_title>
		<journal_url>www.atmos-chem-phys-discuss.net</journal_url>
		<issn>1680-7367</issn>
		<eissn>1680-7375</eissn>
		<volume_number>10</volume_number>
		<issue_number>1</issue_number>
		<publication_year>2010</publication_year>
	</journal>
	<doi>10.5194/acpd-10-1383-2010</doi>
	<article_url>http://www.atmos-chem-phys-discuss.net/10/1383/2010/</article_url>
	<abstract_html>http://www.atmos-chem-phys-discuss.net/10/1383/2010/acpd-10-1383-2010.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys-discuss.net/10/1383/2010/acpd-10-1383-2010.pdf</fulltext_pdf>
	<start_page>1383</start_page>
	<end_page>1416</end_page>
	<publication_date>2010-01-20</publication_date>
	<article_title content_type="html">Mercury air-borne emissions from 5 municipal solid waste landfills in Guiyang and Wuhan, China</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>Z. G. Li</name>
		</author>
		<author numeration="2" affiliations="1">
			<name>X. Feng</name>
			<email>fengxinbin@vip.skleg.cn</email>
		</author>
		<author numeration="3" affiliations="1">
			<name>P. Li</name>
		</author>
		<author numeration="4" affiliations="2">
			<name>L. Liang</name>
		</author>
		<author numeration="5" affiliations="1">
			<name>S. L. Tang</name>
		</author>
		<author numeration="6" affiliations="1">
			<name>S. F. Wang</name>
		</author>
		<author numeration="7" affiliations="1">
			<name>X. W. Fu</name>
		</author>
		<author numeration="8" affiliations="1">
			<name>G. L. Qiu</name>
		</author>
		<author numeration="9" affiliations="1">
			<name>L. H. Shang</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">State Key Laboratory of Environmental Geochemistry, Institute of Geochemistry, Chinese Academy of Sciences, Guiyang 550002, China</affiliation>
		<affiliation numeration="2" content_type="html">Cebam Analytical, Inc., 3927 Aurora Avenue N, Seattle, WA 98103, USA</affiliation>
	</affiliations>
	<abstract content_type="html">A detailed study on atmospheric mercury emissions from municipal solid
      waste (MSW) landfills in China is necessary to understand mercury
      behavior in this source category, simply because China disposes of
      bulk MSW by landfilling and a large quantity of mercury enters into
      landfills. Between 2003 and 2006, mercury airborne emissions through
      different pathways, as well as mercury speciation in landfill gas
      (LFG) were measured at 5 MSW landfills in Guiyang and Wuhan,
      China. The results showed that mercury content in the substrate
      fundamentally affected the magnitude of mercury emissions, resulting
      in the highest emission rate (as high as
      57 651 ng Hg m&lt;sup&gt;&amp;minus;2&lt;/sup&gt; h&lt;sup&gt;&amp;minus;1&lt;/sup&gt;) at the working face and in
      un-covered waste areas, and the lowest measured at soil covers and
      vegetation areas (less than
      20 ng Hg m&lt;sup&gt;&amp;minus;2&lt;/sup&gt; h&lt;sup&gt;&amp;minus;1&lt;/sup&gt;). Meteorological parameters, especially
      solar radiation, influenced the diurnal pattern of mercury surface-air
      emissions. Total gaseous mercury (TGM) in LFG varied from 2.0 to
      1406.0 ng m&lt;sup&gt;&amp;minus;3&lt;/sup&gt;, monomethyl mercury (MMHg) and dimethyl mercury
      (DMHg) in LFG averaged at 1.93 and 9.21 ng m&lt;sup&gt;&amp;minus;3&lt;/sup&gt;, and accounted
      for 0.51% and 1.79% of the TGM in the LFG, respectively. Total
      mercury emitted from the five landfills ranged from 17 to
      3285 g yr&lt;sup&gt;&amp;minus;1&lt;/sup&gt;, with the highest from the working face, then soil
      covering, and finally the vent pipes.</abstract>
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</article>

