ABSTRACT
- TOPIC #2
Analytical
Challenges
Topic
Leader: Monica Mazurek
Contributor: Berndt Simoneit and Michelle Schantz
Detection
and measurement of organic compounds at the molecular level is
now a routine practice for many air quality ambient monitoring
studies. Molecular tracer analysis provides a powerful approach
for linking major emissions with observed concentrations of fine
particles. Quantitative estimates of major emissions to observed
fine particle ambient mass concentrations are developed by using
mass ratios of marker concentrations to the total organic aerosol
ambient mass. Rogge et al., (1993) first described the molecular
marker approach for fine particle apportionment work using ambient
marker concentrations and emissions profiles measured for metropolitan
Los Angeles. Further development of the mathematical model was
published by Schauer et al., (1996) linking emissions inventories,
emissions sources chemical compositions, and ambient concentrations
of organic molecular tracers. Identification of molecular markers
in ambient fine particles is incorporated into current research
and monitoring activities on the sources and compositions of fine
particles, including the current Supersites project funded by
the U.S. Environmental Protection Agency.
Typically,
a single molecular marker compound comprises only a minute fraction
of the organics fine particle mass fraction with ambient ratios
of marker mass to total organics in units of ng m-3 and mg m-3,
respectively. For example, ambient mass ratios of hopane fossil
fuel biomarkers to organics range can range from [0.08-2.14]x10-3
for metropolitan New York City (Mazurek et al, 2004) to [0.87-3.50]x10-3
for metropolitan Los Angeles (Schauer et al., 1996). Consequently,
the analytical protocol for detecting and quantifying a molecular
marker within ambient particulate matter must be sensitive and
precise.
This
workshop session addresses the current state-of-the-science for
molecular maker analysis in aerosol complex mixtures. Nearly two
decades have passed since the gas chromatography/mass spectrometry
based analytical protocol was developed by Mazurek and coworkers
and applied to ambient fine particle samples (Mazurek et al.,
1987; Mazurek and Simoneit, 1981; Rogge et al., 1993)and emission
source samples (Mazurek et al, 1989, 1993; Hildemann et al., 1991)
over the period 1982 to 1984 in metropolitan Los Angeles. Many
innovations in molecular level analysis have occurred since this
time involving advances in instrumentation, separation of complex
organic mixtures, improvements in measurement accuracy and precision,
and in strategies for improved interpretation mass spectrometric
data for target marker compounds. Invited presentations in “Session
2. Analytical Challenges” focus on 1) components of the
collection and analytical protocol necessary for identification
and quantitation of molecular markers in fine particle samples;
2) standard reference materials, new standards for aerosol marker
compounds, and results of intercomparison laboratory trials for
molecular markers in urban dust standard matrix reference material;
and 3) advanced mass spectrometric interpretation methods for
target compounds in complex organic mixtures from airborne particles.
Individual abstracts for the invited presentations are presented
in the following section.
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1)
A Critical Assessment of the Molecular-Level Analytical Protocol
for Ambient Fine Particles
Monica A. Mazurek, Department of
Civil and Environmental Engineering, Rutgers University, 623 Bowser
Road, Piscataway, NJ, 08854-8014.
Organic
molecular tracers in fine particulate matter constituent only
a minute fraction of aerosol mass. Given the sub parts-per-billion
concentrations of organic marker compounds present in most urban
atmospheres, the analytical protocol for detection and measurement
is detailed and requires high precision and accuracy. An essential
feature of the molecular analysis protocol involves a thorough
quality assurance/quality control (QA/QC) plan. The QA/QC plan
examines sampling, and filter handling and preparation steps evaluated
also at the molecular level with identical instrumentation for
compound detection and quantification. Typically, quadrupole electron-impact
mass detection is used with pre-separation by high resolution
gas chromatography.
Although
the GC/MS molecular marker technology was developed in the early
1980’s, no general criteria have been developed for how
accurately and precisely a marker compound must be measured, what
are critical detection limits, or what surrogate analytes must
be incorporated into a sample to monitor method, instrument, and
analyst performance. Each of these factors is critical for producing
molecular marker measurements of known quality (Budde, 2001).
Finally, additional method validation steps, including laboratory
duplicate sample aliquots, performance check standards, and field
duplicate samples, generally are not conducted for molecular marker
characterization work, but are essential to improving ambient
mass concentration measurements. This presentation addresses these
analytical protocol elements as key challenge areas for molecular
marker measurement and identification in fine particle samples.
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2) Reference Material and Quality Assurance Needs to Support
Organic Speciation Measurements in Air Particulate Matter
Stephen A. Wise and Michele M. Schantz, National
Institute of Standards and Technology (NIST), Analytical Chemistry
Division, 100 Bureau Drive Stop 8392, Gaithersburg, MD 20899-8392;
Joellen Lewtas, USEPA, NERL, Manchester Lab, 7411 Beach Dr. E.,
Port Orchard, WA 98366.
One
of the first environmental matrix Standard Reference Materials
(SRMs) developed by the National Institute of Standards and Technology
(NIST) for determination of organic species was SRM 1649 Urban
Dust, an ambient total suspended particulate matter sample collected
in Washington DC in the late 1970’s. Since SRM 1649 was
issued in 1981, it has found widespread use in the particulate
matter (PM) measurement community, and NIST has assigned values
for over 100 organic species in this material. However, there
is a growing need for additional reference materials to support
organic speciation of PM, particularly for the fine particulate
matter fraction and representative of contemporary combustion
sources. NIST is collaborating with the U.S. Environmental Protection
Agency (EPA), with input from a group of investigators involved
in EPA’s PM research program and related studies, to develop
additional SRMs and to provide interlaboratory comparison exercises
to improve the accuracy and comparability of organic speciation
measurements. SRM activities include development of both PM matrix
and calibration solution SRMs for organic species of interest
in PM characterization. For development of a future PM-matrix
SRM, efforts are underway to obtain a suitable quantity of a fine
PM either through collection of fine PM or size fractionation
of existing total suspended particulate material to provide fine
particulate fraction. We are also assessing the suitability of
a fine PM on filter media SRM, which was developed for carbon
measurements, for organic speciation measurements. Calibration
solution SRMs containing a wide range of organic species are under
development including: polycyclic aromatic hydrocarbons (PAHs)
(two redesigned solutions with an expanded list of 53 PAHs and
alkyl-substituted PAHs), aliphatic hydrocarbons, nitro-substituted
PAHs (redesigned and expanded list of compounds), hopanes/steranes,
and 13C-labeled levoglucosan for use as an internal standard.
In addition to the SRMs developed in conjunction with EPA, several
additional PM-matrix SRMs for organic speciation are currently
in progress including: SRM 2585 Organic Contaminants in House
Dust and SRM 1650b Diesel Particulate Matter. In addition to the
SRM development activities, two NIST/EPA interlaboratory comparison
studies have been conducted to assess and improve the comparability
measurements of organic species in PM. This presentation will
discuss these SRM and quality assurance activities and their potential
impact on improving the accuracy of organic speciation measurements
for PM characterization.
This
work has been funded in part by the U S Environmental Protection
Agency. It has been subjected to Agency review and approved for
publication.
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3)
Characterization of novel organic tracers in aerosols by mass
spectrometry
Berndt R. T. Simoneit, Oceanic and Atmospheric
Sciences, Oregon State University, 104 Oceanography Administration
Building, Corvallis, OR 97331-5503.
Organic
compounds in aerosols are useful as tracers for assessment of
sources, alteration and fate in indoor, urban and global air sheds.
Indoor and urban pollution research has been reported mainly in
the U.S. and European literature and both organic and inorganic
tracers have been applied. Although, this meeting is focused on
urban air pollution, it should be emphasized that aerosol particulate
matter (PM) is also of global concern in climate change research
and organic matter plays a key role. Initial studies of long-range
transport of organic compounds in continental aerosols over the
oceans were in the Atlantic (Simoneit, 1977) and Pacific (SEAREX
program). The subsequent hiatus is currently followed by new major
programs of global change research (i.e., ACE-Asia) and organic
tracers are an important aspect.
Progress
in defining new organic tracers in aerosols was mainly due to
instrument development (GC-MS sensitivity) and the applications
of the biomarker compounds elucidated in the geologic record by
organic geochemists, the natural compounds characterized by natural
product chemists, and the synthetic compounds from the chemical
industry (Simoneit,1999). Mass spectrometry (MS) is the analytical
method of choice and compound identifications must be coupled
initially with comparisons to authentic standards or structure
proofs by MS, NMR and syntheses. It is now routine to analyze
total extracts (both organic or aqueous) directly by GC-MS after
suitable derivatization of the polar compounds. Preparation of
separated polarity fractions (by LC or TLC) remains an option
for selected samples to gain additional functional group information.
Derivatization is typically carried out by methylation and /or
trimethylsilylation. This can involve MS interpretation because
the derivatives (especially TMS) are not necessarily in the library
or the free compound or acetate derivative MS may be archived.
High temperature GC-MS can also be applied for high molecular
weight compound identification ( e.g., wax esters to C40, alkanes
to C100).
The processes of MS interpretation and data evaluation (identification
of the compounds in a mixture analyzed by GC-MS) will be illustrated
here with some examples. Smoke from burning of contemporary (biomass,
refuse, etc.) and fossil fuels is a global problem and the mass
spectrometric identification of tracers for this process is discussed
(Simoneit el al., 1999). Soil resuspension and erosion is another
unquantified emission source and its contribution to the ACE-Asia
aerosols is presented in another example (Simoneit et al., 2003).
Also, a brief discussion of what not to do with organic tracer
analyses is included (Simoneit, 2003). The total extract GC-MS
analysis method with selected derivatization is a powerful tool
for determining aliphatic homologous lipids, natural products,
fossil fuel components, secondary oxidation products, PAH, UCM,
phenols, saccharides, etc. and thus attaining an overview of the
major and key organic tracers in aerosol PM.
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