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<article language="en">
	<journal>
		<journal_title>Atmospheric Chemistry and Physics</journal_title>
		<journal_url>www.atmos-chem-phys.net</journal_url>
		<issn>1680-7316</issn>
		<eissn>1680-7324</eissn>
		<volume_number>9</volume_number>
		<issue_number>16</issue_number>
		<publication_year>2009</publication_year>
	</journal>
	<doi>10.5194/acp-9-6077-2009</doi>
	<article_url>http://www.atmos-chem-phys.net/9/6077/2009/</article_url>
	<abstract_html>http://www.atmos-chem-phys.net/9/6077/2009/acp-9-6077-2009.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys.net/9/6077/2009/acp-9-6077-2009.pdf</fulltext_pdf>
	<start_page>6077</start_page>
	<end_page>6093</end_page>
	<publication_date>2009-08-21</publication_date>
	<article_title content_type="html">Effect of regional precursor emission controls on long-range ozone  transport – Part 1: Short-term changes in ozone air quality</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>J. J. West</name>
			<email>jasonwest@unc.edu</email>
		</author>
		<author numeration="2" affiliations="2,4">
			<name>V. Naik</name>
		</author>
		<author numeration="3" affiliations="3">
			<name>L. W. Horowitz</name>
		</author>
		<author numeration="4" affiliations="3">
			<name>A. M. Fiore</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">University of North Carolina, Chapel Hill, NC, USA</affiliation>
		<affiliation numeration="2" content_type="html">Princeton University, Princeton, NJ, USA</affiliation>
		<affiliation numeration="3" content_type="html">NOAA Geophysical Fluid Dynamics Laboratory, Princeton, NJ, USA</affiliation>
		<affiliation numeration="4" content_type="html">now at: ATMOS Research and Consulting, Lubbock, TX, USA</affiliation>
	</affiliations>
	<abstract content_type="html">Observations and models demonstrate that ozone and its precursors can be
transported between continents and across oceans. We model the influences of
10% reductions in anthropogenic nitrogen oxide (NO&lt;sub&gt;x&lt;/sub&gt;) emissions from
each of nine world regions on surface ozone air quality in that region and
all other regions. In doing so, we quantify the relative importance of
long-range transport between all source-receptor pairs, for direct
short-term ozone changes. We find that for population-weighted
concentrations during the three-month &quot;ozone-season&quot;, the strongest
inter-regional influences are from Europe to the Former Soviet Union, East
Asia to Southeast Asia, and Europe to Africa. The largest influences per
unit of NO&lt;sub&gt;x&lt;/sub&gt; reduced, however, are seen for source regions in the
tropics and Southern Hemisphere, which we attribute mainly to greater
sensitivity to changes in NO&lt;sub&gt;x&lt;/sub&gt; in the lower troposphere, and secondarily
to increased vertical convection to the free troposphere in tropical
regions, allowing pollutants to be transported further. Results show, for
example, that NO&lt;sub&gt;x&lt;/sub&gt; reductions in North America are ~20% as
effective per unit NO&lt;sub&gt;x&lt;/sub&gt; in reducing ozone in Europe during summer, as
NO&lt;sub&gt;x&lt;/sub&gt; reductions from Europe itself. Reducing anthropogenic emissions of
non-methane volatile organic compounds (NMVOCs) and carbon monoxide (CO) by
10% in selected regions, can have as large an impact on long-range ozone
transport as NO&lt;sub&gt;x&lt;/sub&gt; reductions, depending on the source region. We find
that for many source-receptor pairs, the season of greatest long-range
influence does not coincide with the season when ozone is highest in the
receptor region. Reducing NO&lt;sub&gt;x&lt;/sub&gt; emissions in most source regions causes a
larger decrease in export of ozone from the source region than in ozone
production outside of the source region.</abstract>
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