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<!DOCTYPE article SYSTEM "http://www.atmos-chem-phys-discuss.net/inc/acpd/copernicus.dtd">
<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>5</volume_number>
		<issue_number>5</issue_number>
		<publication_year>2005</publication_year>
	</journal>
	<doi>10.5194/acpd-5-10339-2005</doi>
	<article_url>http://www.atmos-chem-phys-discuss.net/5/10339/2005/</article_url>
	<abstract_html>http://www.atmos-chem-phys-discuss.net/5/10339/2005/acpd-5-10339-2005.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys-discuss.net/5/10339/2005/acpd-5-10339-2005.pdf</fulltext_pdf>
	<start_page>10339</start_page>
	<end_page>10367</end_page>
	<publication_date>2005-10-24</publication_date>
	<article_title content_type="html">Global impact of road traffic emissions on tropospheric ozone</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>S. Matthes</name>
		</author>
		<author numeration="2" affiliations="1">
			<name>V. Grewe</name>
		</author>
		<author numeration="3" affiliations="1">
			<name>R. Sausen</name>
		</author>
		<author numeration="4" affiliations="2">
			<name>G.-J. Roelofs</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Institut für Physik der Atmosphäre, DLR-Oberpfaffenhofen, Wessling, Germany</affiliation>
		<affiliation numeration="2" content_type="html">Institut for Marine Research, University of Utrecht, Utrecht, The Netherlands</affiliation>
	</affiliations>
	<abstract content_type="html">Road traffic is one of the major anthropogenic emission sectors for NO&lt;sub&gt;x&lt;/sub&gt;, CO and
NMHCs (non-methane hydrocarbons). We applied ECHAM4/CBM,
a general circulation model coupled to a chemistry module,
which includes higher hydrocarbons, to investigate
the global impact of road traffic emissions on the atmosphere.
Improving over previous global modelling studies, which concentrated on
road traffic NO&lt;sub&gt;x&lt;/sub&gt; and CO-emissions only, we assess the impact of
NMHC-emissions from road traffic.
It is revealed that NMHC-emissions from road traffic
play a key role for the impact on ozone. They are responsible for
(indirect) long-range transport of NO&lt;sub&gt;x&lt;/sub&gt; from road traffic via
the formation of PAN, which is not found in a simulation without NMHC emissions from road traffic.
Long-range transport of NMHC-induced PAN
impacts on the ozone distribution in northern hemisphere regions far away from the sources, especially in
Arctic and remote maritime regions. There, during subsidence, PAN acts as a source for NO&lt;sub&gt;x&lt;/sub&gt;, caused by
thermal decay. Hence, ozone is produced.
In July total road traffic emissions (NO&lt;sub&gt;x&lt;/sub&gt;, CO and NMHCs) contribute to
the zonally averaged ozone distribution by more than 12%
near the surface in the northern hemisphere
midlatitudes and arctic latitudes. In January road traffic emissions contribute near the
surface in northern and southern extratropics more than 8%.
Sensitivity studies for regional emission show that effective transport of road traffic
emissions occurs mainly in the free troposphere.
In tropical latitudes of America
up to an altitude of 200&amp;nbsp;hPa, global road traffic emissions contribute about 4%
to the ozone concentration.</abstract>
	<references>
	</references>
</article>

