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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-5-2869-2005</article-id>
<title-group>
<article-title>Organic, elemental and inorganic carbon in particulate matter of six urban environments in Europe</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Sillanpää</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>Frey</surname>
<given-names>A.</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>Hillamo</surname>
<given-names>R.</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>Pennanen</surname>
<given-names>A. S.</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>Salonen</surname>
<given-names>R. O.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
</contrib-group><aff id="aff1">
<label>1</label>
<addr-line>Finnish Meteorological Institute, Air Quality Research, Erik Palménin aukio 1, FIN-00560 Helsinki, Finland</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>National Public Health Institute, Department of Environmental Health, Neulaniementie 4, FIN-70210 Kuopio, Finland</addr-line>
</aff>
<pub-date pub-type="epub">
<day>02</day>
<month>11</month>
<year>2005</year>
</pub-date>
<volume>5</volume>
<issue>11</issue>
<fpage>2869</fpage>
<lpage>2879</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/5/2869/2005/acp-5-2869-2005.html">This article is available from http://www.atmos-chem-phys.net/5/2869/2005/acp-5-2869-2005.html</self-uri>
<self-uri xlink:href="http://www.atmos-chem-phys.net/5/2869/2005/acp-5-2869-2005.pdf">The full text article is available as a PDF file from http://www.atmos-chem-phys.net/5/2869/2005/acp-5-2869-2005.pdf</self-uri>
<abstract>
<p>A series of 7-week sampling campaigns were conducted in urban background
sites of six European cities as follows: Duisburg (autumn), Prague (winter),
Amsterdam (winter), Helsinki (spring), Barcelona (spring) and Athens
(summer). The campaigns were scheduled to include seasons of local public
health concern due to high particulate concentrations or findings in
previously conducted epidemiological studies. Aerosol samples were collected
in parallel with two identical virtual impactors that divide air particles
into fine (PM&lt;sub&gt;2.5&lt;/sub&gt;) and coarse (PM&lt;sub&gt;2.5-10&lt;/sub&gt;) size ranges. From the
collected filter samples, elemental (EC) and organic (OC) carbon contents
were analysed with a thermal-optical carbon analyser (TOA); total Ca, Ti,
Fe, Si, Al and K by energy dispersive X-ray fluorescence (ED-XRF); As, Cu,
Ni, V, and Zn by inductively coupled plasma mass spectrometry (ICP/MS);
Ca&lt;sup&gt;2+&lt;/sup&gt;, succinate, malonate and oxalate by ion chromatography (IC); and
the sum of levoglucosan+galactosan+mannosan (&amp;#x2211;MA) by liquid
chromatography mass spectrometry (LC/MS). The campaign means of PM&lt;sub&gt;2.5&lt;/sub&gt;
and PM&lt;sub&gt;2.5-10&lt;/sub&gt; were 8.3-29.6 &amp;micro;g m&lt;sup&gt;-3&lt;/sup&gt; and 5.4-28.7 &amp;micro;g m&lt;sup&gt;-3&lt;/sup&gt;,
respectively. The contribution of particulate organic matter (POM)
to PM&lt;sub&gt;2.5&lt;/sub&gt; ranged from 21% in Barcelona to 54% in Prague, while
that to PM&lt;sub&gt;2.5-10&lt;/sub&gt; ranged from 10% in Barcelona to 27% in Prague.
The contribution of EC was higher to PM&lt;sub&gt;2.5&lt;/sub&gt; (5-9%) than to
PM&lt;sub&gt;2.5-10&lt;/sub&gt; (1-6%) in all the six campaigns. Carbonate (C(CO&lt;sub&gt;3&lt;/sub&gt;),
that interferes with the TOA analysis, was detected in PM&lt;sub&gt;2.5-10&lt;/sub&gt; of
Athens and Barcelona but not elsewhere. It was subtracted from the OC by a
simple integration method that was validated. The CaCO&lt;sub&gt;3&lt;/sub&gt; accounted for
55% and 11% of PM&lt;sub&gt;2.5-10&lt;/sub&gt; in Athens and Barcelona, respectively. It
was anticipated that combustion emissions from vehicle engines affected the
POM content in PM&lt;sub&gt;2.5&lt;/sub&gt; of all the six sampling campaigns, but a
comparison of mass concentration ratios of the selected inorganic and
organic tracers of common sources of organic material to POM suggested also
interesting differences in source dominance during the campaign periods:
Prague (biomass and coal combustion), Barcelona (fuel oil combustion,
secondary photochemical organics) and Athens (secondary photochemical
organics). The on-going toxicological studies will clarify the health
significance of these findings.</p>
</abstract>
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