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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>9</issue_number>
		<publication_year>2009</publication_year>
	</journal>
	<doi>10.5194/acp-9-2891-2009</doi>
	<article_url>http://www.atmos-chem-phys.net/9/2891/2009/</article_url>
	<abstract_html>http://www.atmos-chem-phys.net/9/2891/2009/acp-9-2891-2009.html</abstract_html>
	<fulltext_pdf>http://www.atmos-chem-phys.net/9/2891/2009/acp-9-2891-2009.pdf</fulltext_pdf>
	<start_page>2891</start_page>
	<end_page>2918</end_page>
	<publication_date>2009-05-05</publication_date>
	<article_title content_type="html">Interpretation of organic components from Positive Matrix Factorization of aerosol mass spectrometric data</article_title>
	<authors>
		<author numeration="1" affiliations="1,2">
			<name>I. M. Ulbrich</name>
		</author>
		<author numeration="2" affiliations="3">
			<name>M. R. Canagaratna</name>
		</author>
		<author numeration="3" affiliations="4">
			<name>Q. Zhang</name>
		</author>
		<author numeration="4" affiliations="3">
			<name>D. R. Worsnop</name>
		</author>
		<author numeration="5" affiliations="1,2">
			<name>J. L. Jimenez</name>
		</author>
	</authors>
	<affiliations>
		<affiliation numeration="1" content_type="html">Cooperative Institute for Research in the Environmental Sciences (CIRES), Boulder, CO, USA</affiliation>
		<affiliation numeration="2" content_type="html">Department of Chemistry and Biochemistry, University of Colorado, Boulder, CO, USA</affiliation>
		<affiliation numeration="3" content_type="html">Aerodyne Research, Inc., Billerica, MA, USA</affiliation>
		<affiliation numeration="4" content_type="html">Atmos. Sci. Res. Center, University at Albany, State University of New York, Albany, NY, USA</affiliation>
	</affiliations>
	<abstract content_type="html">The organic aerosol (OA) dataset from an Aerodyne Aerosol Mass Spectrometer
(Q-AMS) collected at the Pittsburgh Air Quality Study (PAQS) in September
2002 was analyzed with Positive Matrix Factorization (PMF). Three components
– hydrocarbon-like organic aerosol OA (HOA), a highly-oxygenated OA (OOA-1)
that correlates well with sulfate, and a less-oxygenated, semi-volatile OA
(OOA-2) that correlates well with nitrate and chloride – are identified and
interpreted as primary combustion emissions, aged SOA, and semivolatile,
less aged SOA, respectively. The complexity of interpreting the PMF
solutions of unit mass resolution (UMR) AMS data is illustrated by a
detailed analysis of the solutions as a function of number of components and
rotational forcing. A public web-based database of AMS spectra has been
created to aid this type of analysis. Realistic synthetic data is also used
to characterize the behavior of PMF for choosing the best number of factors,
and evaluating the rotations of non-unique solutions. The ambient and
synthetic data indicate that the variation of the PMF quality of fit
parameter (&lt;i&gt;Q&lt;/i&gt;, a normalized chi-squared metric) vs. number of factors in the
solution is useful to identify the minimum number of factors, but more
detailed analysis and interpretation are needed to choose the best number of
factors. The maximum value of the rotational matrix is not useful for
determining the best number of factors. In synthetic datasets, factors are
&quot;split&quot; into two or more components when solving for more factors than
were used in the input. Elements of the &quot;splitting&quot; behavior are observed
in solutions of real datasets with several factors. Significant structure
remains in the residual of the real dataset after physically-meaningful
factors have been assigned and an unrealistic number of factors would be
required to explain the remaining variance. This residual structure appears
to be due to variability in the spectra of the components (especially OOA-2
in this case), which is likely to be a key limit of the retrievability of
components from AMS datasets using PMF and similar methods that need to
assume constant component mass spectra. Methods for characterizing and
dealing with this variability are needed. Interpretation of PMF factors must
be done carefully. Synthetic data indicate that PMF internal diagnostics and
similarity to available source component spectra together are not sufficient
for identifying factors. It is critical to use correlations between factor
and external measurement time series and other criteria to support factor
interpretations. True components with &lt;5% of the mass are unlikely to
be retrieved accurately. Results from this study may be useful for
interpreting the PMF analysis of data from other aerosol mass spectrometers.
Researchers are urged to analyze future datasets carefully, including
synthetic analyses, and to evaluate whether the conclusions made here apply
to their datasets.</abstract>
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</article>

