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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-3-591-2003</article-id>
<title-group>
<article-title>Haze in the Klang Valley of Malaysia</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Keywood</surname>
<given-names>M. 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>Ayers</surname>
<given-names>G. 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>Gras</surname>
<given-names>J. 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>Boers</surname>
<given-names>C. P.</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>Leong</surname>
<given-names></given-names>
</name>
<xref ref-type="aff" rid="aff3">
<sup>3</sup>
</xref>
</contrib>
</contrib-group><aff id="aff1">
<label>1</label>
<addr-line>CSIRO Atmospheric Research, Australia</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>Atmospheric Research Division KNMI Netherlands</addr-line>
</aff>
<aff id="aff3">
<label>3</label>
<addr-line>Malaysian Meteorological Service, Malaysia</addr-line>
</aff>
<pub-date pub-type="epub">
<day>05</day>
<month>06</month>
<year>2003</year>
</pub-date>
<volume>3</volume>
<issue>3</issue>
<fpage>591</fpage>
<lpage>605</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.net/3/591/2003/acp-3-591-2003.html">This article is available from http://www.atmos-chem-phys.net/3/591/2003/acp-3-591-2003.html</self-uri>
<self-uri xlink:href="http://www.atmos-chem-phys.net/3/591/2003/acp-3-591-2003.pdf">The full text article is available as a PDF file from http://www.atmos-chem-phys.net/3/591/2003/acp-3-591-2003.pdf</self-uri>
<abstract>
<p>Continuous measurements of dry aerosol light scattering (Bsp) were made at two sites in the
      Klang Valley of Malaysia between December 1998 and December 2000.  In addition 24-hour
      PM2.5 samples were collected on a one-day-in-six cycle and the chemical composition of the
      aerosol was determined.  Periods of excessive haze were defined as 24-hour average Bsp
      values greater than 150 Mm&lt;sup&gt;-1&lt;/sup&gt; and these occurred on a number of occasions, between May and
      September 1999, during May 2000, and between July and September 2000. The evidence for
      smoke from biomass burning being a significant contributor to aerosol during periods of
      excessive haze is discussed.  For example, during periods of excessive haze, the chemical
      composition of the aerosol showed enhanced concentrations of elemental carbon, organic
      carbon and non-seasalt potassium.  The diurnal cycle of Bsp and PM10 was disturbed from its
      usual pattern of maxima overnight and minuma during the day with morning and afternoon
      traffic peaks, and instead showed a maximum peak during the middle of the day.  Periods of
      excessive haze were coincident with the presence of forest fires on Sumatra during the
      southwest (SW) monsoon period, the influence of which are demonstrated by transport
      modelling for one week of the SW monsoon of 2000. The study highlights that whilst
      transboundary smoke is a major contributor to poor visibility in the Klang Valley, smoke
      from fires on Peninsular Malaysia is also a contributor.  In addition the uniform concentration
      of non-seasalt sulfate in PM2.5 at both sites over the entire sampling period suggests the
      presence of a domestic source of secondary aerosol production in the Klang Valley.</p>
</abstract>
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