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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>10</volume_number>
		<issue_number>2</issue_number>
		<publication_year>2010</publication_year>
	</journal>
	<doi>10.5194/acpd-10-2581-2010</doi>
	<article_url>http://www.atmos-chem-phys-discuss.net/10/2581/2010/</article_url>
	<abstract_html>http://www.atmos-chem-phys-discuss.net/10/2581/2010/acpd-10-2581-2010.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys-discuss.net/10/2581/2010/acpd-10-2581-2010.pdf</fulltext_pdf>
	<start_page>2581</start_page>
	<end_page>2632</end_page>
	<publication_date>2010-02-03</publication_date>
	<article_title content_type="html">Determination of particulate lead during MILAGRO/MCMA-2006 using Aerosol Mass Spectrometry</article_title>
	<authors>
		<author numeration="1" affiliations="1">
			<name>D. Salcedo</name>
		</author>
		<author numeration="2" affiliations="2">
			<name>T. B. Onasch</name>
		</author>
		<author numeration="3" affiliations="3,7">
			<name>A. C. Aiken</name>
		</author>
		<author numeration="4" affiliations="2">
			<name>L. R. Williams</name>
		</author>
		<author numeration="5" affiliations="4">
			<name>B. de Foy</name>
		</author>
		<author numeration="6" affiliations="3">
			<name>M. J. Cubison</name>
		</author>
		<author numeration="7" affiliations="2">
			<name>D. R. Worsnop</name>
		</author>
		<author numeration="8" affiliations="5,6">
			<name>L. T. Molina</name>
		</author>
		<author numeration="9" affiliations="3">
			<name>J. L. Jimenez</name>
			<email>jose.jimenez@colorado.edu</email>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Centro de Investigaciones QuÃ­micas, Universidad AutÃ³noma del Estado de Morelos, Cuernavaca, MÃ©xico</affiliation>
		<affiliation numeration="2" content_type="html">Center for Aerosol and Cloud Chemistry, Aerodyne Research, Billerica, MA, USA</affiliation>
		<affiliation numeration="3" content_type="html">Cooperative Institute for Research in the Environmental Sciences (CIRES) and Department of Chemistry and Biochemistry, University of Colorado, Boulder, CO, USA</affiliation>
		<affiliation numeration="4" content_type="html">Department of Earth and Atmospheric Sciences, Saint Louis University, Saint Louis, MO, USA</affiliation>
		<affiliation numeration="5" content_type="html">Molina Center for Energy and the Environment, La Jolla, CA, USA</affiliation>
		<affiliation numeration="6" content_type="html">Earth Atmospheric and Planetary Sciences Department, Massachusetts Institute of \newline Technology, Cambridge, MA, USA</affiliation>
		<affiliation numeration="7" content_type="html">now at: ETHZ, Zurich, Switzerland</affiliation>
	</affiliations>
	<abstract content_type="html">We report the first measurements of particulate lead (Pb) from Aerodyne
Aerosol Mass Spectrometers, which were deployed in and around Mexico City
during the Megacity Initiative: Local and Global Research Observations
(MILAGRO)/Mexico City Metropolitan Area 2006 (MCMA-2006) field campaigns.
The high resolution mass spectrometer of one of the AMS instruments (HR-AMS)
and the measured isotopic ratios unequivocally prove the detection of Pb in
ambient particles. A substantial fraction of the lead evaporated slowly from
the vaporizer of the instruments, which is indicative of species with low
volatility at 600 &amp;deg;C. A model was developed in order to estimate the
ambient particulate Pb entering the AMS from the signals in the &quot;open&quot; and
the &quot;closed&quot; (or &quot;background&quot;) mass spectrum modes of the AMS. The model
suggests the presence of at least two lead fractions with ~25% of
the Pb signal exhibiting rapid evaporation (1/e decay constant, &amp;tau;&lt;0.1 s)
and ~75% exhibiting slow evaporation (&amp;tau;~2.4 min)
at the T0 urban supersite and a different fraction (70% prompt and 30% slow
evaporation) at a site northwest from the metropolitan area (PEMEX site).
From laboratory experiments with pure Pb(NO&lt;sub&gt;3&lt;/sub&gt;)&lt;sub&gt;2&lt;/sub&gt; particles, we
estimated that the Pb ionization efficiency relative to nitrate (RIE&lt;sub&gt;Pb&lt;/sub&gt;)
is 0.5. Comparison of time series of AMS Pb with other measurements carried out at T0 (using Proton Induced X-ray
Emission (PIXE), Inductively-Coupled Plasma Mass Spectrometry (ICP-MS) and
single-particle counts from an Aerosol Time-of-Fight Mass Spectrometer
(ATOFMS)) shows similar levels (for PIXE and ICP-MS) and substantial
correlation. During part of the campaign, sampling at T0 was alternated
every 10 min with an Aerosol Concentrator, which enabled the detection
of signals for PbCl&lt;sup&gt;+&lt;/sup&gt; and PbS&lt;sup&gt;+&lt;/sup&gt; ions. PbS&lt;sup&gt;+&lt;/sup&gt; displays the
signature of a slowly evaporating species, while PbCl&lt;sup&gt;+&lt;/sup&gt; appears to arise
only from fast evaporation, which is likely due to the higher vapor pressure
of the compounds generating PbCl&lt;sup&gt;+&lt;/sup&gt;. This is consistent with the
evaporation model results. Levels of particulate Pb measured at T0
were similar to previous studies in Mexico City. Pb shows a diurnal
cycle with a maximum in the early morning, which is typical of primary urban
pollutants. Pb shows correlation with Zn, consistent with previous studies,
while the sources of Pb appear to be at least partially disjoint from those
of particulate chloride. Back trajectory analysis of the T0 Pb data suggests
the presence of sources inside the urban area SSW and N of T0, with
different chemical forms of Pb being associated with different source
locations. High signals due to particulate lead were also detected in the
PEMEX site; again, no correlation between Pb and chloride plumes was
observed, suggesting mostly different sources for both species.</abstract>
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</article>

