Major Funding:
DOE
EPA
NASA
NSF
Send comments to nmd@andrew.cmu.edu
Last updated: 8 May 2007 by nmd
|
CAPS
|
[1]
|
Product analysis of the OH oxidation of isoprene and 1,3-butadiene in the
presence of NO.
J. Geophys. Res.-Atmos. 107, (M. Sprengnether, K. L.
Demerjian, N. M. Donahue, and J. G. Anderson) 2002 (4).
[1] The oxidation mechanisms of isoprene and butadiene
initiated by OH in the presence of NO have been explored under
wall-less flowing conditions, with products observed a few
seconds after reaction by infrared spectroscopy. Since only similar
to1% of alkene is reacted, any secondary chemistry is negligible.
The use of reaction modulation spectroscopy permits the accurate
measurement of a percent change in high alkene concentration and of
10(13) molecules/cm(3) concentrations for products. Measured
carbonyl species agree with previous studies, while alkyl nitrate
yields are consistent with upper values reported in the literature.
NO sensitivity studies performed exclude the possibility of
competing chemistry. Isoprene is not observed to form 3-methyl
furan, indicating that this is not a prompt oxidation product.
However, butadiene does form furan. In an auxiliary experiment,
peroxy radicals in the second stage of butadiene oxidation are
fully converted to peroxynitrates. Average cross sections for
integrated peroxynitrate bands are determined from this experiment.
C1 SUNY Albany, Atmospher Sci Res Ctr, Albany, NY 12205 USA.
Harvard Univ, Dept Chem & Biol Chem, Cambridge, MA 02138 USA.
|
|
[2]
|
Gas-phase ozonolysis of alkenes: Formation of OH from anti carbonyl oxides.
J. Am. Chem. Soc. 124, 8518-8519 (J. H. Kroll, N. M.
Donahue, V. J. Cee, K. L. Demerjian, and J. G. Anderson) 2002 (16).
|
|
[3]
|
Pressure broadening coefficients for rotational transitions of water in the
380-600 cm(-1) range.
J. Quant. Spectrosc. Radiat. Transf. 72, 775-782 (D. W.
Steyert, W. F. Wang, J. M. Sirota, N. M. Donahue, and D. C. Reuter)
2002 (7).
We present results of recent experiments on the
pressure broadening of pure rotational transitions of (H2O)-O-16
water in the 400-600 cm(-1) range by nitrogen and oxygen. The
average broadening coefficient is about 0.056 cm(-1)/atm for N-2
and about 0.029 cm(-1)/atm for O-2, however, as expected, the
broadening coefficient varies as a strong function of transition.
In general, the broadening decreases with increasing J and K-a,
with a stronger dependence on K-a than on J. On average, air
broadening coefficients obtained from the coefficients presented
here are about 10% lower than those found in HITRAN '96, although,
as detailed below, the differences are a function of quantum
number. (C) 2002 Elsevier Science Ltd. All rights reserved. C1 Univ
Maryland Baltimore Cty, Joint Ctr Earth Syst Technol, Baltimore, MD
21250 USA. Harvard Univ, Dept Chem & Biochem, Cambridge, MA 02138
USA. NASA, Goddard Space Flight Ctr, Extraterr Phys Lab, Greenbelt,
MD 20771 USA.
|
|
[4]
|
Cloud activation of single-component organic aerosol particles.
J. Geophys. Res.-Atmos. 107, (T. M. Raymond and S. N.
Pandis) 2002 (34).
[1] The organic fraction of ambient aerosols is a
complex mixture of hundreds of organic compounds varying in
chemical structure and physical properties. The cloud condensation
nuclei (CCN) activities of single-component organic particles were
experimentally investigated. Activation diameters were determined
using a Tandem Differential Mobility Analyzer and a thermal
diffusion Cloud Condensation Nucleus Counter. Studies were
performed at supersaturations of 0.3 and 1% with dry particle
diameters ranging between 0.02 and 0.2 mum. The focus was on both
hygroscopic secondary organics and hydrophobic primary organics.
Laboratory experiments were performed with sodium chloride,
ammonium sulfate, glutaric acid, adipic acid, pinonic acid,
glutamic acid, leucine, cholesterol, pinic acid, norpinic acid,
hexadecane, hexadecanol, myristic acid, palmitic acid, and stearic
acid. The results were compared with the classical Kohler theory
and a theory that accounts for the limited solubility of many
organics. It was discovered that organic species with bulk
solubilities in water less than 0.01 g cm(-3) can be a good source
of CCN in the atmosphere if their contact angles with water are
zero. Experiments confirmed that Kohler theory works well in
predicting activation of soluble inorganic species and organics
that are wettable by water, while an extension of the theory
appears necessary to account for the low-solubility organic species
that are not wettable by water.
C1 Carnegie Mellon Univ, Dept Chem Engn & Engn & Publ Policy,
Pittsburgh, PA 15213 USA. Carnegie Mellon Univ, Dept Chem Engn,
Pittsburgh, PA 15213 USA.
|
|
[5]
|
Is the size distribution of urban aerosols determined by thermodynamic
equilibrium? an application to southern California.
Atmos. Environ. 36, 2349-2365 (M. Moya, S. N. Pandis,
and M. Z. Jacobson) 2002 (17).
A size-resolved equilibrium model, SELIQUID, is
presented and used to simulate the size-composition distribution of
semi-volatile inorganic aerosol in an urban environment. The model
uses the efflorescence branch of aerosol behavior to predict the
equilibrium partitioning of the aerosol components between the gas
phase and a size-resolved aerosol population over the entire RH
domain. Predictions of SELIQUID are compared against size-resolved
composition measurements at different locations during the Southern
California Air Quality Study. Based on the modeling results, the
size distribution of sub-micrometer nitrate and ammonium can be
determined by thermodynamic equilibrium when the RH > 60%. In
cases where the RH < 60%, the assumption that all aerosol
particles are metastable liquid solutions may introduce
unacceptable errors. On the other hand, the equilibrium assumption,
in some cases at least, introduces errors in the calculation of the
coarse (particles with diameter <1 mum or so) nitrate and ammonium
that increase with particle size. Finally, the inclusion of crustal
species is important in modeling the size distribution of coarse
inorganic aerosols when the concentration of these species is high.
The effect of these crustal species can be complex and
counterintuitive. (C) 2002 Published by Elsevier Science Ltd.
C1 Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA 15213 USA.
Carnegie Mellon Univ, Dept Engn & Publ Policy, Pittsburgh, PA
15213 USA. Univ Nacl Autonoma Mexico, Fac Quim, Mexico City, DF,
Mexico. Stanford Univ, Dept Civil & Environm Engn, Stanford, CA
94305 USA.
|
|
[6]
|
Sources of atmospheric carbonaceous particulate matter in Pittsburgh,
Pennsylvania.
J. Air Waste Manage. Assoc. 52, 732-741 (J. C. Cabada,
S. N. Pandis, and A. L. Robinson) 2002 (28).
The organic carbon (OC)/elemental carbon (EC) tracer
method is applied to the Pittsburgh, PA, area to estimate the
contribution of secondary organic aerosol (SOA) to the monthly
average concentration of organic particulate matter (PM) during
1995. An emissions inventory is constructed for the primary
emissions of OC and EC in the area of interest. The ratio of
primary emissions of OC to those of EC ranges between 2.4 in the
winter months and 1.0 in the summer months. A mass balance model
and ambient measurements were used to assess the accuracy of the
emissions inventory. It is estimated to be accurate to within 50%.
The results from this analysis show a strong monthly dependence of
the SOA contribution to the total organic PM concentration, varying
from near zero during winter months to as much as 50% of the total
OC concentration in the summer.
C1 Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA 15213 USA.
Carnegie Mellon Univ, Dept Mech Engn, Pittsburgh, PA 15213 USA.
|
|
[7]
|
Effects of sampling conditions on the size distribution of fine particulate
matter emitted from a pilot-scale pulverized-coal combustor.
Energy Fuels 16, 302-310 (E. Lipsky, C. O. Stanier,
S. N. Pandis, and A. L. Robinson) 2002 (9).
[ DOI |
.pdf ]
A dilution sampler has been designed and manufactured
to simulate the effects of dilution processes on particulate matter
emissions from coal-fired power plants and other combustion
systems. The sampler allows independent control of the dilution
ratio and residence time. Experiments were performed to examine the
effects of these parameters on the particulate emissions of a
pilot-scale pulverized coal combustor burning a low sulfur
bituminous coal. Measurements included the particle size
distribution in the range from 0.003 to 20 mum and the PM2.5 mass
emission rate. The residence time and dilution ratio do not
influence the particle mass emission rate, but have a significant
effect on the size distribution and the total number of particles
emitted. Increasing the residence time dramatically decreases the
total particle number concentration, and shifts the particle mass
to larger sizes. Increasing the dilution ratio increases the
concentration of ultrafine particles. The effects of residence time
can be explained quantitatively by the coagulation of the emitted
particles; however, the effects of dilution ratio are more complex
because the dilution ratio influences both the coagulation rate and
gas-to-particle conversion.
C1 Carnegie Mellon Univ, Dept Mech Engn, Pittsburgh, PA 15213 USA.
Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA 15213 USA.
|
|
[8]
|
Pilot-scale investigation of the influence of coal-biomass cofiring on ash
deposition.
Energy Fuels 16, 343-355 (A. L. Robinson, H. Junker, and
L. L. Baxter) 2002 (12).
Cofiring biomass with coal is a promising short-term
option for reducing the net CO2 emissions from existing coal-fired
power plants. This paper examines the effects of cofiring biomass
and coal on ash deposition under conditions representative of those
found in the superheater region of pulverized-coal boilers.
Experiments were conducted with blends of eight different
fuels-three types of bituminous coal, sub-bituminous coal, two
types of straw, switchgrass, and wood. For each fuel, reference
tests of unblended fuel establish a baseline against which to
compare the results from the cofiring tests. The deposition rates
for the cofire blends are between the measured deposition rates of
the unblended fuels. Therefore, blending straw with coal reduces
the high deposition rates observed while firing unblended straw,
and cofiring coal with wood results in slightly lower deposition
rates than those that occur while firing unblended coal. The
primary interaction between the biomass and coal during cofiring is
the reaction of the sulfur from the coal with the alkali species
from the biomass. This sulfation reduces the stickiness of the
deposit, which substantially reduces the deposition rate of the
coal-straw blends in comparison to expectations based on the
performance of the unblended fuels. Sulfation also reduces the
chlorine content of the deposits, potentially reducing the
corrosion potential of the deposits. A scaling parameter is
proposed to estimate the deposit chlorine content on the basis of
the properties of the cofire blend; the ratio of fuel-S to
available alkali must be in excess of 5 times the S-to-alkali
stoichiometric ratio to eliminate chlorine from the deposit. The
results demonstrate that cofiring can mitigate some of the fouling
difficulties associated with combustion of high-fouling biofuels.
C1 Sandia Natl Labs, Combust Res Facil, Livermore, CA 94550 USA.
|
|
[9]
|
Predicting global aerosol size distributions in general circulation models.
J. Geophys. Res.-Atmos. 107, (P. J. Adams and J. H.
Seinfeld) 2002 (28).
[1] To better represent the indirect effect of
aerosols on climate, a size-resolved simulation of aerosol
microphysics, size distributions, number and mass concentrations
has been incorporated into the GISS general circulation model
(GCM). The TwO-Moment Aerosol Sectional (TOMAS) microphysics model
used here conserves aerosol number as well as mass. It has high
size resolution, 30 bins between 0.01 and 10 mum diameter. As a
first application, a size-resolved simulation of sulfate has been
performed. The model reproduces important features of the
atmospheric aerosol such as number concentrations that increase
with altitude and land-sea contrasts in aerosol number
concentrations and size distributions. Comparisons with
observations show that simulated size distributions are realistic
and condensation nuclei (CN) concentrations agree with observations
within about 25%. Predicted cloud condensation nuclei (CCN)
concentrations are also in reasonable agreement with observations,
although there are locations for which agreement would be improved
by including other aerosol components such as sea salt and
carbonaceous aerosols. Sensitivity scenarios show that
uncertainties in nucleation and primary emissions from fossil fuels
can have significant effects on predictions of CN and CCN
concentrations. C1 Carnegie Mellon Univ, Dept Civil & Environm
Engn, Pittsburgh, PA 15213 USA. Carnegie Mellon Univ, Dept Engn &
Publ Policy, Pittsburgh, PA 15213 USA. CALTECH, Dept Chem Engn,
Pasadena, CA 91125 USA.
|
This file has been generated by
bibtex2html 1.86.
|