Abstract
- Topic #8
Advances
in Organic Characterization and Quantification Applicable to Organic
Aerosols
Topic
Leader: Reinhard Niessner
Contributors: Markus Kalberer,
Kimberly Prather, Paul
Ziemann (click
on name to link to abstract text)
On-line
(& in situ) Chemical Analysis of Organic Aerosol
Reinhard
Niessner
Institute of Hydrochemistry, Technical University of Munich
For
many years, aerosol scientists and/or analysts have asked for
on-line & in situ measurement techniques. The reason for this
demand is easily understood: artifact-free sampling and immediate
analysis allows the direct observation of fast processes; e.g.,
aerosol formation or degradation of even labile aerosol species.
In favourable cases, a further dimension can be opened: a tomographic
information, which means x,y,z-oriented chemical analysis.
This review summarizes the principal techniques available with
their special characteristics rather than what has been published
so far. The intrinsic possibilities of a principle will be discussed,
especially in view of new instrumentation (laser, synchrotron,
surface-enhanced effects, intracavity arrangement, antibody, PCR,
high-parallel detection schemes etc.).
Analytes: organic particulate matter in a size range of 3
nm < dp < 150 µm
-
Molecules > 1 kDalton ; viable bioaerosols, proteins, peptides,
natural polymers (low vapour pressure material)
- Molecules < 1 kDalton (high vapour pressure substances)
- Functional groups, inert or labile bonds, chirality, spin
density ; chemically reactive or inert.
It
is important to realize the presence of organo-metallic species
in ambient aerosol. In case of a needed phase transfer, rapid
sampling becomes important (gaseous state c liquid state).
The measurement techniques are based on:
interaction of electromagnetic radiation in a wavelength range
of 1 nm < l < 1 mm with aerosol particles
- absorption of radiation as only detection principle (transmission,
optothermal effects, ESR)
- emission of radiation as only detection principle (Raman,
fluorescence, backscattering, laser plasma emission)
- formation of charged particles or fragments as detection principle
(photoelectron emission, mass spectrometry, photofragmentation);
particle – particle interaction
-
detection is based on ballistic measurement of particles (photons,
ions, electrons, atoms) after aerosol collision (RBS. phoretic
techniques)
-
detection is based on measurement of quantifiable adduct formation
(strong interaction : antibodies or peptides (ELISA, PCR); weak
interaction (water condensation)
-
detection is based on multiple effects in a multi-dimensional
space (smell, viability or reproducibility).
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Laser-mass
spectrometry of organic aerosols identification of specific
compounds and bulk properties
Markus
Kalberer, ETH Zurich
Depending on the scientific focus, single compound analysis or
measurement of bulk properties is preferable in organic aerosol
analysis. Studying toxic compounds (carcinogenic, mutagenic) compounds
such as PAHs, compound specific analysis and quantification is
required. Two-step laser time-of-fight mass spectrometry (L2MS)
is a fast and one of the most sensitive methods measuring aerosol-bound
PAHs and very selective due to the REMPI ionisation process. This
allows measuring PAHs in several particle size classes with 10-15min
time resolution, a time scale within which short term emission
peaks close to sources such as a busy road can be followed.
Recent quantification methods can give estimates of PAH concentrations
on aerosols (Kalberer et al, 2002, 2003a). These measurements
showed that most PAHs in the mass range up to m/z280 have a half-life
<3hrs.
Other
laser ionisation MS techniques, e.g., (matrix assisted) laser
desorption/ionisation MS (MALDI, LDI), are less specific ionisation
methods.
This apparent disadvantage, however, allows capturing mass analysis
of the particle bulk, because a wide range of compound classes
are ionized. Recent measurements of smog chamber generated secondary
organic aerosols (SOA) with this technique showed that high molecular
weight compounds based on acetal polymers up to a mass of about
m/z1000 comprise a major fraction of the SOA mass formed from
aromatic precursors (Kalberer et al, 2003b).
Functional
groups, important factors for the particle's hygroscopic or optical
properties, however, are easier accessible with optical methods,
such as IR or VU-VIS. Also for such questions the determination
of an average chemical composition is probably more suited than
single compound
analyses. Time resolved measurements of SOA show that the functional
group distribution is varying significantly over time demonstrating
the continuously changing chemical composition of particles with
age.
M.
Kalberer, B. D. Morrical, M. Sax, R. Zenobi. Picogram Quantification
of Polycyclic Aromatic Hydrocarbons adsorbed on Aerosol Particles
by Two-Step Laser Mass Spectrometry, Anal. Chem., 74 (14):
3492-3497, 2002.
M.
Kalberer, S. Henne, A. Prevot, M. Steinbacher. Vertical transport
and degradation of polycyclic aromatic hydrocarbons in an Alpine
valley. Atmos. Environ., submitted, 2003a.
M.
Kalberer, D.Paulsen, M.Sax, M.Steinbacher, J.Dommen, R. Fisseha,
A. Prevot, V.Frankevich, R.Zenobi, U.Baltensperger. First
Identification of Polymers as Major Components of Atmospheric
Organic Aerosols. submitted, 2003b.
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Organic
Aerosol Analysis Using Thermal Desorption Aerosol Mass Spectrometry
Paul J. Ziemann, Air Pollution Research Center, University
of California, Riverside
In
the past few years, a large variety of mass spectrometry-based
instruments have been developed and employed for studies of the
chemical composition of ambient atmospheric aerosol particles.
One
approach that is particularly well suited for the analysis of
organic aerosols involves the use of thermal desorption to vaporize
the organic components prior to analysis using mass spectrometry.
The
most widely used instrument of this type is the Aerodyne Aerosol
Mass Spectrometer (AMS), which is commercially available and can
analyze organic aerosol size and composition in real time. The
AMS consists of an aerosol inlet, a particle sizing chamber, and
a particle detection section. Particles are sampled from ambient
pressure and focused by an aerodynamic lens into a narrow beam
as they enter high vacuum. Particle aerodynamic diameter is determined
by measuring the time a particle takes to reach the vaporizer
after passing through a mechanical beam chopper. Particle chemical
composition is determined via flash vaporization followed by electron
ionization and quadrupole mass spectrometry. The separation of
the particle vaporization and the vapor ionization steps enables
linear chemical composition detection even for complex mixtures.
A
similar instrument, called a thermal desorption particle beam
mass spectrometer (TDPBMS), has been developed by the Ziemann
group at UC-Riverside and primarily used for laboratory studies
of secondary organic aerosol formation and diesel emissions. As
with the AMS, particles are focused in an aerodynamic lens, sampled
into a high vacuum chamber where they impact on a heated surface,
and the resulting vapor is analyzed by a quadrupole mass spectrometer
using electron ionization. One important difference between the
TDPBMS and the AMS is that, in addition to operating in a real-time
analysis mode, the vaporizer of the TDPBMS can be cooled so that
particles can be collected and subsequently analyzed as they desorb
under slow heating (temperature-programmed thermal desorption).
This method separates components according to volatility and thus
provides composition information as a function of component vapor
pressure. The TDPBMS is not as sensitive as the AMS, however,
and so normally cannot be used for ambient analysis. Furthermore,
the TDPBMS does not incorporate a means to size-select particles
for analysis. Recently, these problems have been addressed by
coupling the TDPBMS to fine and ultrafine Particle Concentrators
developed by the Sioutas group at USC, which has made possible
its use for ambient organic aerosol analysis.
A
different method has been developed for semi-continuous analysis
of organic aerosols by Hering at Aerosol Dynamics and Goldstein
at UC-Berkeley. This method employs an impactor to collect fine
particles on a metal surface, which is subsequently flash-heated
to desorb the organic components. The vapor is collected on the
front a gas chromatograph-mass spectrometer column for subsequent
analysis. This technique provides much more speciated information
than the AMS or TDPBMS, but is not a real-time analyzer, and requires
derivatization methods for the analysis of polar compounds.
In
this talk I will discuss the capabililties, advantages and disadvantages
of these methods for organic aerosol analysis and ways in which
their performance might be improved.
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On-line
analysis of organic species using single particle mass spectrometry
Kimberly
A. Prather, University of California, San Diego
Single particle mass spectrometry is a growing area of research,
due to the fact it can provide unique insights into the mixing
state of ambient aerosol particles (Sipin, 2003). Depending on
the application, a number of different instrumental designs have
been developed, each with its own advantages and disadvantages.
Much of the focus of on-line single particle ambient measurements
has been on inorganic particles. Under standard conditions of
high laser fluence, extensive fragmentation can occur during the
laser desorption process; often times these fragmentation patterns
can be used to identify the compounds of interest upon comparison
with mass spectral libraries (Silva, 2000). A number of groups
have shown these techniques are capable of providing information
on molecular organic species in individual particles (Angelino,
2001; Smith, 2002). New methods have been developed to reduce
fragmentation, including two-step LDI and VUV photoionization
(Morrical, 1998; Woods, 2001). Because the particles are analyzed
on-line in less than 1 ms, these techniques hold promise for studying
the partitioning of semivolatile organic compounds (SVOC). The
potential for using single particle mass spectrometry for source
apportionment will be discussed. Finally, fundamental differences
in organic versus elemental carbon single particle mass spectral
signatures can be used to differentiate between EC, OC, and EC/OC
particles; a discussion of how this information might be used
to provide insight into discrepancies in other standard EC/OC
measurements will be presented. This presentation will focus on
the potential for obtaining information on organic aerosols, detailing
the advantages and disadvantages of this approach compared to
alternative analysis techniques.
Angelino, S., D. T. Suess, et al. (2001). "Formation of aerosol
particles from reactions of secondary and tertiary alkylamines:
Characterization by aerosol time-of-flight mass spectrometry."
Environmental Science & Technology 35(15): 3130-3138.
Morrical,
B. D., D. P. Fergenson, et al. (1998). "Coupling two-step
laser desorption/ionization with aerosol time-of-flight mass spectrometry
for the analysis of individual organic particles." Journal
of the American Society for Mass Spectrometry 9(10): 1068-1073.
Silva,
P. J. and K. A. Prather (2000). "Interpretation of mass spectra
from organic compounds in aerosol time-of-flight mass spectrometry."
Analytical Chemistry 72(15): 3553-3562.
Sipin,
M. F., S. A. Guazzotti, et al. (2003). "Recent advances and
some remaining challenges in analytical chemistry of the atmosphere."
Analytical Chemistry 75(12): 2929-2940.
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