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<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>8</volume_number>
		<issue_number>2</issue_number>
		<publication_year>2008</publication_year>
	</journal>
	<doi>10.5194/acpd-8-8059-2008</doi>
	<article_url>http://www.atmos-chem-phys-discuss.net/8/8059/2008/</article_url>
	<abstract_html>http://www.atmos-chem-phys-discuss.net/8/8059/2008/acpd-8-8059-2008.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys-discuss.net/8/8059/2008/acpd-8-8059-2008.pdf</fulltext_pdf>
	<start_page>8059</start_page>
	<end_page>8090</end_page>
	<publication_date>2008-04-23</publication_date>
	<article_title content_type="html">Comparison of emission ratios from on-road sources using a mobile laboratory under various driving and operational sampling modes</article_title>
	<authors>
		<author numeration="1" affiliations="1,2">
			<name>M. Zavala</name>
			<email>miguelz@mce2.org</email>
		</author>
		<author numeration="2" affiliations="3">
			<name>S. C. Herndon</name>
		</author>
		<author numeration="3" affiliations="3">
			<name>E. C. Wood</name>
		</author>
		<author numeration="4" affiliations="3">
			<name>J. T. Jayne</name>
		</author>
		<author numeration="5" affiliations="3">
			<name>D. D. Nelson</name>
		</author>
		<author numeration="6" affiliations="3">
			<name>A. M. Trimborn</name>
		</author>
		<author numeration="7" affiliations="2,8">
			<name>E. Dunlea</name>
		</author>
		<author numeration="8" affiliations="4">
			<name>W. B. Knighton</name>
		</author>
		<author numeration="9" affiliations="5">
			<name>A. Mendoza</name>
		</author>
		<author numeration="10" affiliations="6">
			<name>D. T. Allen</name>
		</author>
		<author numeration="11" affiliations="3">
			<name>C. E. Kolb</name>
		</author>
		<author numeration="12" affiliations="2,7">
			<name>M. J. Molina</name>
		</author>
		<author numeration="13" affiliations="1,2">
			<name>L. T. Molina</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Molina Center for the Energy and the Environment, San Diego, California, USA</affiliation>
		<affiliation numeration="2" content_type="html">Department of Earth, Atmospheric and Planetary Sciences, Massachusetts Institute of Technology, Cambridge, Massachusetts, USA</affiliation>
		<affiliation numeration="3" content_type="html">Center for Atmospheric and Environmental Chemistry; Center for Cloud and Aerosol Chemistry, Aerodyne Research Inc., Billerica, Massachusetts, USA</affiliation>
		<affiliation numeration="4" content_type="html">Department of Chemistry, Montana State University, Bozeman, Montana, USA</affiliation>
		<affiliation numeration="5" content_type="html">Departamento de Ingeniería Química, Tecnológico de Monterrey, Monterrey, México</affiliation>
		<affiliation numeration="6" content_type="html">Center for Energy and Environmental Resources, University of Texas, Austin, Texas, USA</affiliation>
		<affiliation numeration="7" content_type="html">Dept. of Chemistry and Biochemistry, University of California, San Diego, California, USA</affiliation>
		<affiliation numeration="8" content_type="html">now at: National Oceanic and Atmospheric Administration, Climate Program Office, Silver Spring, Maryland, USA</affiliation>
	</affiliations>
	<abstract content_type="html">Mobile sources produce a significant fraction of the total anthropogenic
emissions burden in large cities and have harmful effects on air quality at
multiple spatial scales. Mobile emissions are intrinsically difficult to
estimate due to the large number of parameters affecting the emissions
variability within and across vehicles types. The MCMA-2003 Campaign in
Mexico City has showed the utility of using a mobile laboratory to sample
and characterize specific classes of motor vehicles to better quantify their
emissions characteristics as a function of their driving cycles. The
technique clearly identifies &quot;high emitter&quot; vehicles via individual
exhaust plumes, and also provides fleet average emission rates. We have
applied this technique to Mexicali during the Border Ozone Reduction and Air
Quality Improvement Program for the Mexicali-Imperial Valley in 2005. In
this paper we analyze the variability of measured emission ratios for
emitted NO&lt;sub&gt;x&lt;/sub&gt;, CO, specific VOCs, NH&lt;sub&gt;3&lt;/sub&gt;, and some primary fine
particle components and properties obtained during the Border Ozone
Reduction and Air Quality Improvement Program for the Mexicali-Imperial
Valley in 2005 by deploying a mobile laboratory in roadside stationary
sampling, chase and fleet average operational sampling modes. The
measurements reflect various driving modes characteristic of the urban
fleets. The observed variability for all measured gases and particle
emission ratios is greater for the chase and roadside stationary sampling
than for fleet average measurements. The fleet average sampling mode
captured the effects of traffic conditions on the measured on-road emission
ratios, allowing the use of fuel-based emission ratios to assess the
validity of traditional &quot;bottom-up&quot; emissions inventories. Using the
measured on-road emission ratios, we estimate CO and NO&lt;sub&gt;x&lt;/sub&gt; mobile
emissions of 175&amp;plusmn;62 and 10.4&amp;plusmn;1.3 metric tons/day, respectively,
for the gasoline vehicle fleet in Mexicali. Comparisons with similar on-road
emissions data from Mexico City indicated that fleet average NO emission
ratios were around 20% higher in Mexicali than in Mexico City whereas
HCHO and NH&lt;sub&gt;3&lt;/sub&gt; emission ratios were higher by a factor of 2 in Mexico
City than in Mexicali. Acetaldehyde emission ratios did not differ
significantly whereas selected aromatics VOCs emissions were similar or
smaller in Mexicali. On-road heavy-duty diesel truck (HDDT) nitrogen oxides
emissions were measured near Austin, Texas, as well as in both Mexican
cities, with NO&lt;sub&gt;y&lt;/sub&gt; emission ratios in Austin &lt; Mexico City &lt; Mexicali.</abstract>
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</article>

