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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>Göttingen, Germany</publisher-loc>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.5194/acpd-5-2719-2005</article-id>
<title-group>
<article-title>Comparison of the levels of organic, elemental and inorganic carbon in particulate matter in 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, Sahaajankatu 20 E, FIN-00880 inki, 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>03</day>
<month>05</month>
<year>2005</year>
</pub-date>
<volume>5</volume>
<issue>3</issue>
<fpage>2719</fpage>
<lpage>2747</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-discuss.net/5/2719/2005/acpd-5-2719-2005.html">This article is available from http://www.atmos-chem-phys-discuss.net/5/2719/2005/acpd-5-2719-2005.html</self-uri>
<self-uri xlink:href="http://www.atmos-chem-phys-discuss.net/5/2719/2005/acpd-5-2719-2005.pdf">The full text article is available as a PDF file from http://www.atmos-chem-phys-discuss.net/5/2719/2005/acpd-5-2719-2005.pdf</self-uri>
<abstract>
<p>A series of 7-week sampling campaigns were conducted in urban background
sites in the six European cities as follows: Duisburg 4 October&amp;ndash;21 November 2002
(autumn), Prague 29 November 2002&amp;ndash;16 January 2003 (winter), Amsterdam 24 January&amp;ndash;13
March 2003 (winter), Helsinki 21 March&amp;ndash;12 May 2003 (spring), Barcelona 28
March&amp;ndash;19 May 2003 (spring) and Athens 2 June&amp;ndash;21 July 2003 (summer). The
campaigns were scheduled to include seasons of local public health concern
due to high PM concentrations or findings in previously conducted
epidemiological studies. Aerosol samples were collected in parallel with two
identical virtual impactors (VI), which divide air PM into two size
fractions, PM&lt;sub&gt;2.5&lt;/sub&gt; and PM&lt;sub&gt;2.5-10&lt;/sub&gt;. The filter samples were analysed
with a microbalance, an energy dispersive X-ray fluorescence (ED-XRF), an
ion chromatograph (IC) and a thermo-optical carbon analyser (TOA). The
PM&lt;sub&gt;2.5&lt;/sub&gt; and PM&lt;sub&gt;2.5-10&lt;/sub&gt; campaign means ranged 8.3&amp;ndash;29.6 &amp;micro;g&amp;nbsp;m&lt;sup&gt;-3&lt;/sup&gt;
and 5.4&amp;ndash;28.7 &amp;micro;g&amp;nbsp;m&lt;sup&gt;-3&lt;/sup&gt;, respectively. The &apos;&apos;wet and cool&apos;&apos; seasons
favoured low coarse PM concentration and high fine PM concentration, whereas
the spring and summer led to low fine and high coarse PM concentrations. The
contribution of particulate organic matter (POM) to PM&lt;sub&gt;2.5-10&lt;/sub&gt; was
highest (27%) in Prague and the lowest (10%) in Barcelona, while those
to PM&lt;sub&gt;2.5&lt;/sub&gt; were generally higher, ranging from 21% in Barcelona to
54% in Prague. The contribution of elemental carbon (EC) to PM&lt;sub&gt;2.5-10&lt;/sub&gt;
were relatively low (1&amp;ndash;6%) in all the six European cities but it
contributed somewhat higher (5&amp;ndash;9%) to PM&lt;sub&gt;2.5&lt;/sub&gt;. The differences are
most likely due to variable contributions of local emission sources and
seasonal factors such as domestic heating, vehicle exhausts and
photochemical reactions. Carbonate, which interferes with carbon analysis by
evolving stage at 900&amp;deg;C, was detected in the coarse particles of Athens
and Barcelona and it could be separated reliably from OC by a simple
integrating method. The calcium carbonate in Athens and Barcelona accounted
for 56% and 11% of coarse PM masses, respectively. Carbonate was not
found in other cities or in PM&lt;sub&gt;2.5&lt;/sub&gt;. The mean PM&lt;sub&gt;2.5&lt;/sub&gt; mass portions of
five OC thermal fractions (OC1, OC2, OC3, OC4 and OCP) varied in the range
26&amp;ndash;33%, 6&amp;ndash;10%, 7&amp;ndash;10%, 9&amp;ndash;22% and 29&amp;ndash;50%, respectively, in six
cities. The differences in the mass portion profiles were relatively small
between the cities.</p>
</abstract>
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