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Last updated: 8 May 2007 by nmd
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CAPS
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[1]
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Evaluation of secondary organic aerosol formation in winter.
Atmos. Environ. 33, 4849-4863 (R. Strader, F. Lurmann,
and S. N. Pandis) 1999 (73).
Three different methods are used to predict secondary
organic aerosol (SOA) concentrations in the San Joaquin Valley of
California during the winter of 1995-1996 [Integrated Monitoring
Study, (IMS95)]. The first of these methods estimates SOA by using
elemental carbon as a tracer of primary organic carbon. The second
method relies on a Lagrangian trajectory model that simulates the
formation, transport, and deposition of secondary organic aerosol.
The model includes a recently developed gas-particle partitioning
mechanism. Results from both methods are in good agreement with the
chemical speciation of organic aerosol during IMS95 and suggest
that most of the OC measured during IMS95 is of primary origin.
Under suitable conditions (clear skies, low winds, low mixing
heights) as much as 15-20 mu g C m(-3) of SOA can be produced,
mainly due to oxidation of aromatics. The low mixing heights
observed during the winter in the area allow accumulation of SOA
precursors and the acceleration of SOA formation. Clouds and fog
slow down the production of secondary compounds, reducing their
concentrations by a factor of two or three from the above maximum
levels. In addition, it appears that there is significant diurnal
variation of SOA concentration. A strong dependence of SOA
concentrations on temperature is observed, along with the existence
of an optimal temperature for SOA formation. (C) 1999 Elsevier
Science Ltd. All rights reserved.
C1 Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA 15213 USA.
Carnegie Mellon Univ, Dept Engn, Pittsburgh, PA 15213 USA. Carnegie
Mellon Univ, Dept Publ Policy, Pittsburgh, PA 15213 USA. Carnegie
Mellon Univ, Dept Civil Environm Engn, Pittsburgh, PA 15213 USA.
Sonoma Technol Inc, Santa Rosa, CA 95403 USA.
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[2]
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Condensation of organic vapors on an externally mixed aerosol population.
Aerosol Sci. Technol. 31, 392-407 (C. N. Cruz and S. N.
Pandis) 1999 (6).
The condensation of organic vapors on a nearly
monodisperse externally mixed aerosol population was measured in
order to test the hypothesis that organic species may
preferentially condense on specific substrates. The organic species
tested were glutaric acid, a typical secondary organic species, and
DOP, a model organic for primary species. A series of organic and
inorganic substrate pairs were investigated: NaCl, (NH4)(2)SO4,
glutaric acid, and adipic acid. The growth of these aerosol
populations was measured using a Tandem Differential Mobility
Analyzer and the results were analyzed using transition regime mass
transfer theory. The results show that no detectable preferential
condensation occurs for either species on any of the substrates
studied. The implications of these results to SOA formation models
are discussed.
C1 Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA 15213 USA.
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[3]
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Heterogeneous sulfate production in the remote marine environment: Cloud
processing and sea-salt particle contributions.
J. Geophys. Res.-Atmos. 104, 21719-21731 (C. Gurciullo,
B. Lerner, H. Sievering, and S. N. Pandis) 1999 (9).
Heterogeneous sulfate production in the remote marine
boundary layer is studied by combining measurements collected
during the first Southern Hemisphere marine Aerosol
Characterization Experiment (ACE 1)with two numerical models: one
simulating heterogeneous sulfate production in sea-salt aerosol
water (SSAW) and the other simulating cloud processing. The models
calculate oxidation of SO2 by O-3 and H2O2 via aqueous-phase
reactions both in SSAW and in cloud droplets. Model calculations
indicate that as much as 50-75% of the observed non-sea-salt (NSS)
sulfate in particles in the ambient diameter size range of 0.9-16
mu m during the ACE 1 measurement period is due to production in
SSAW, with cloud processing producing the remainder. The initial
alkalinity of the wind-generated sea-salt aerosols can strongly
influence sulfate production. Changing the effective alkalinity of
SSAW from a value typical of seawater to a value based on the
measurements taken at Cape Grim results in a better match to the
observed NSS sulfate size distribution with up to 75% of the
predicted supermicrometer NSS sulfate being due to heterogeneous
conversion in SSAW. The average rates of removal of sulfate due to
dry and wet deposition for the 0.4-16 mu m size range are 38 and 14
ng m(-3) d(-1) respectively.
C1 Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA 15213 USA.
Univ Colorado, Dept Environm & Geog, Denver, CO 80217 USA.
Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA 15213 USA.
Carnegie Mellon Univ, Dept Engn & Publ Policy, Pittsburgh, PA
15213 USA.
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[4]
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An analysis of four models predicting the partitioning of semivolatile
inorganic aerosol components.
Aerosol Sci. Technol. 31, 129-153 (A. S. Ansari and
S. N. Pandis) 1999 (22).
A comparison is conducted between 3 atmospheric
equilibrium models: GFEMN, ISORROPIA, SCAPE2, and SEQUILIB. While
ISORROPIA, SCAPE2, and SEQUILIB simplify the problem at hand in an
effort to reduce computational rigor, GFEMN does not employ many of
the simplifying assumptions used in previous models, thus allowing
it to accurately predict multistage aerosol behavior and
deliquescence depression. We examine model performance for
representative atmospheric environments over an extended
composition, temperature, and RH domain and against observations in
Southern California. The predictions of GFEMN, ISORROPIA, SCAPE2,
and SEQUILIB are in general agreement, but the latter 3 do not
adequately reproduce multistage deliquescence behavior for
multicomponent systems. The most notable differences in model
predictions occur for H+ and aerosol water concentrations;
discrepancies in predictions of aerosol nitrate and total dry
inorganic Phl concentrations are not as significant. The models
predict different deliquescence relative humidities for
multicomponent systems, but for ammonia poor environments, these
discrepancies do not introduce differences in total dry inorganic
PM predictions. Against measurements taken during the Southern
California Air Quality Study (SCAQS), all models qualitatively
reproduce but generally underpredict aerosol nitrate
concentrations. Finally, based on its overall agreement with GFEMN
and its computational efficiency, ISORROPIA appears to be the model
of choice for use in large-scale aerosol transport models. In
places where crustal material comprises a significant portion of
total PM, SCAPE2 is an alternative.
C1 Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA 15213 USA.
Carnegie Mellon Univ, Dept Engn & Publ Policy, Pittsburgh, PA
15213 USA.
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[5]
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Effects of ship emissions on sulphur cycling and radiative climate forcing over
the ocean.
Nature 400, 743-746 (K. Capaldo, J. J. Corbett,
P. Kasibhatla, P. Fischbeck, and S. N. Pandis) 1999 (59).
The atmosphere overlying the ocean is very
sensitive-physically chemically and climatically-to air pollution.
Given that clouds over the ocean are of great climatic
significance, and that sulphate aerosols seem to be an important
control on marine cloud formation(1), anthropogenic inputs of
sulphate to the marine atmosphere could exert an important
influence on climate. Recently, sulphur emissions from fossil fuel
burning by international shipping have been geographically
characterized(2), indicating that ship sulphur emissions nearly
equal the natural sulphur nux from ocean to atmosphere in many
areas(3). Here we use a global chemical transport model to show
that these ship emissions can be a dominant contributor to
atmospheric sulphur dioxide concentrations over much of the world's
oceans and in several coastal regions. The ship emissions also
contribute significantly to atmospheric non-seasalt sulphate
concentrations over Northern Hemisphere ocean regions and parts of
the Southern Pacific Ocean, and indirect radiative forcing due to
ship-emitted particulate matter (sulphate plus organic material) is
estimated to contribute a substantial fraction to the anthropogenic
perturbation of the Earth's radiation budget. The quantification of
emissions from international shipping forces a re-evaluation of our
present understanding of sulphur cycling and radiative forcing over
the ocean.
C1 Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA 15213 USA.
Carnegie Mellon Univ, Dept Engn & Publ Policy, Pittsburgh, PA
15213 USA. Carnegie Mellon Univ, Dept Social & Decis Sci,
Pittsburgh, PA 15213 USA. Duke Univ, Nicholas Sch Environm, Durham,
NC 27708 USA.
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[6]
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The mass accommodation coefficient of ammonium nitrate aerosol.
Atmos. Environ. 33, 2993-3003 (K. G. Dassios and S. N.
Pandis) 1999 (14).
The mass transfer rate of pure ammonium nitrate
between the aerosol and gas phases was quantified experimentally by
the use of the tandem differential mobility analyzer/scanning
mobility particle sizer (TDMA/SMPS) technique. Ammonium nitrate
particles 80-220 nm in diameter evaporated in purified air in a
laminar flow reactor under temperatures of 20-27 degrees C and
relative humidities in the vicinity of 10%. The evaporation rates
were calculated by comparing the initial and final size
distributions. A theoretical expression of the evaporation rate
incorporating the Kelvin effect and the effect of relative humidity
on the equilibrium constant is developed. The measurements were
consistent with the theoretical predictions but there was evidence
of a small kinetic resistance to the mass transfer rate. The
discrepancy can be explained by a mass accommodation coefficient
ranging from 0.8 to 0.5 as temperature increases from 20-27 degrees
C. The corresponding timescale of evaporation for submicron NH,NO,
particles in the atmosphere is of the order of a few seconds to 20
min. (C) 1999 Elsevier Science Ltd. All rights reserved.
C1 Carnegie Mellon Univ, Dept Chem Engn & Engn, Pittsburgh, PA
15213 USA. Carnegie Mellon Univ, Dept Publ Policy, Pittsburgh, PA
15213 USA.
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[7]
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Continued development and testing of a new thermodynamic aerosol module for
urban and regional air quality models.
Atmos. Environ. 33, 1553-1560 (A. Nenes, S. N. Pandis,
and C. Pilinis) 1999 (44).
A computationally efficient and rigorous thermodynamic
model (ISORROPIA) that predicts the physical stale and composition
of inorganic atmospheric aerosol is presented. The advantages of
this particular model render it suitable for incorporation into
urban and regional air quality models. The model is embodied into
the UAM-AERO air quality model, and the performance is compared
with two other thermodynamic modules currently in use, SEQUILIB 1.5
and SEQUILIB 2.1. The new model yields predictions that agree with
experimental measurements and the results of the other models, but
at the same time proves to be much faster and computationally
efficient. Using ISORROPIA accelerates the thermodynamic
calculations by more than a factor of six, while the overall
speed-up of UAM-AERO is at least twofold. This speedup is possible
by the optimal solution of the thermodynamic equations, and the
usage of precalculated tables, whenever possible. (C) 1999 Elsevier
Science Ltd. All rights reserved.
C1 Univ Aegean, Dept Environm Sci, GR-81100 Mytilene, Greece. Univ
Miami, Rosenstiel Sch Marine & Atmospher Sci, Div Marine &
Atmospher Chem, Miami, FL 33149 USA. Carnegie Mellon Univ, Dept
Chem Engn, Pittsburgh, PA 15213 USA. Carnegie Mellon Univ, Dept
Engn & Publ Policy, Pittsburgh, PA 15213 USA.
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[8]
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Global nitrogen and sulfur inventories for oceangoing ships.
J. Geophys. Res.-Atmos. 104, 3457-3470 (J. J. Corbett,
P. S. Fischbeck, and S. N. Pandis) 1999 (62).
We present geographically resolved global inventories
of nitrogen and sulfur emissions from international maritime
transport for use in global atmospheric models. Current inventories
of globally resolved sources of natural and anthropogenic emissions
do not include the significant contribution of SO2 or NOx from
oceangoing ships [Benkovitz et al., 1996]. We estimate the global
inventory of ship emissions,using current emission test data for
ships [Carlton et al., 1995] and a fuel-based approach similar to
that used for automobile inventories [Singer and Harley, 1996].
This study estimates the 1993 global annual NOx and SO2 emissions
from ships to be 3.08 teragrams (Tg, or 10(12) g) as N and 4.24 Tg
S, respectively. Nitrogen emissions from ships are shown to account
for more than 14% of all nitrogen emissions from fossil fuel
combustion, and sulfur emissions exceed 5% of sulfur emitted by
all fuel combustion sources including coal. Ship sulfur emissions
correspond to about 20% of biogenic dimethylsulfide (DMS)
emissions. In regions of the Northern Hemisphere, annual sulfur
emissions from ships can be of the same order of magnitude as
estimates of the annual flux of DMS [Chin et al., 1996] Monthly
inventories of ship sulfur and nitrogen emissions presented in this
paper are geographically characterized on a 2 degrees x 2 degrees
resolution. Temporal and spatial characteristics of the inventory
are presented, Uncertainty in inventory estimates is assessed: the
fifth and ninety-fifth percentile values for global nitrogen
emissions are 2.66 Tg N and 4.00 Tg N, respectively; the fifth and
ninety-fifth percentile values for sulfur emissions are 3.29 Tg S
and 5.61 Tg S, respectively. We suggest that these inventories,
available via the Ship Emissions Assessment (SEA) web site, be used
in models along with the Global Emissions Inventory Activity (GEIA)
inventories for land-based anthropogenic emissions and modeled with
ocean-biogenic inventories for DMS.
C1 Carnegie Mellon Univ, Dept Engn & Publ Policy, Pittsburgh, PA
15213 USA. Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA
15213 USA. Carnegie Mellon Univ, Dept Social & Decis Sci,
Pittsburgh, PA 15213 USA.
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[9]
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Is aerosol production within the remote marine boundary layer sufficient to
maintain observed concentrations?
J. Geophys. Res.-Atmos. 104, 3483-3500 (K. P. Capaldo,
P. Kasibhatla, and S. N. Pandis) 1999 (16).
To evaluate the impact of aerosols on climate we must
consider the aerosol dynamics of the remote marine atmosphere.
Marine aerosols are subject to losses due to precipitation, dry
deposition, and coagulation; yet, observed remote marine aerosol
concentrations and size distributions are relatively constant. This
maintenance of the aerosol distribution requires a particle source.
This work focuses on the potential of H2SO4 nucleation within the
marine boundary layer (MBL) to supply these particles. Spatial and
temporal variability in meteorology and species concentrations are
considered in a mathematical model to evaluate the effect of
natural deviations from average MBL conditions on the highly
nonlinear aerosol system. A dynamic, vertically dimensioned,
size-resolved aerosol model is used with parameterized
heterogeneous chemical processes. The results suggest that MBL
nucleation may be an important source of new particle number in the
remote MEL. However, though our model shows that typical remote MBL
aerosol distributions can on average be maintained by MBL
nucleation and sea-salt emissions, large oscillations in particle
number concentration occur. Because such oscillations are only
occasionally reported in measurements, MBL nucleation may not be
the dominant source of new particles in the remote MEL. The
nucleation events, which cause these oscillations, are predicted to
occur at the top of the MBL after rain and/or entrainment of clean
free tropospheric air. Predictions are particularly sensitive to
the H2SO4 accommodation coefficient, nucleation tuner, and washout
efficiency. Reduction of the accommodation coefficient is shown to
increase the predicted accumulation mode concentration because the
nucleation rate is enhanced. Entrainment of clean free tropospheric
air is shown to increase the frequency of nucleation events within
the MBL and may help to explain the observed correlation between
subsidence and MBL small particles. A small constant addition of
particles from the free troposphere, ocean, etc. suppresses H2SO4
nucleation and can lead to a reduction in total predicted aerosol
number. This is because nucleation events require low total aerosol
surface area and the constant addition of particles reduces the
severity of aerosol surface area minimums. Larger external aerosol
sources can maintain the observed remote MBL aerosol distribution.
However, the temporal and spatial variability of such sources could
have a large impact on aerosol concentrations and requires further
investigation.
C1 Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA 15213 USA.
Duke Univ, Nicholas Sch Environm, Durham, NC 27708 USA. Carnegie
Mellon Univ, Dept Engn & Publ Policy, Pittsburgh, PA 15213 USA.
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[10]
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Prediction of multicomponent inorganic atmospheric aerosol behavior.
Atmos. Environ. 33, 745-757 (A. S. Ansari and S. N.
Pandis) 1999 (51).
Many existing models calculate the composition of the
atmospheric aerosol system by solving a set of algebraic equations
based on reversible reactions derived from thermodynamic
equilibrium. Some models rely on an a priori knowledge of the
presence of components in certain relative humidity regimes, and
often fail to accurately predict deliquescence point depression and
multistage aerosol growth. The present approach, relying on
adjusted thermodynamic parameters of solid salts and a state of the
art activity coefficient model, directly minimizes the Gibbs free
energy (according to thermodynamic equilibrium principles) given
temperature, relative humidity and the total (gas plus aerosol)
ammonia, nitric acid, sulfate, sodium, and hydrochloric acid
concentrations. A direct minimization, while requiring nb
additional assumptions in its algorithm, allows the elimination of
many of the assumptions used in previous models such as divided
relative humidity (rh) and composition domains where only certain
reactions are assumed to occur and constant DRH values despite
varying temperature and composition. Moreover, the current approach
predicts aerosol deliquescence and efflorescence behavior
explaining the existence of supersaturated aerosol solutions. A
comparison is conducted between our approach and available
experimental results under several conditions. The current model
agrees with experimental results for single salt systems although
it shows sensitivity to thermodynamic parameters used in the
minimization algorithm. A set of Delta G(f)(0) for solid salts is
estimated that is consistent with available laboratory measurements
and significantly improves model performance. I;or multicomponent
systems, the current approach with adjusted Delta G(f)(0)
accurately reproduces observed multistage growth patterns and
deliquescence point depression over a broad temperature range.
Finally, the direct Gibbs free energy minimization accurately
reproduces aerosol efflorescence behavior. (C) 1999 Elsevier
Science Ltd. All rights reserved. C1 Carnegie Mellon Univ, Dept
Chem Engn, Pittsburgh, PA 15213 USA. Carnegie Mellon Univ, Dept
Engn & Publ Policy, Pittsburgh, PA 15213 USA.
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[11]
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Radon entry into houses: The importance of scale-dependent permeability.
Health Phys. 77, 183-191 (K. Garbesi, A. L. Robinson,
R. G. Sextro, and W. W. Nazaroff) 1999 (6).
Soil permeability to air can increase substantially
with measurement length scale. We tested the hypothesis that the
scale effect could resolve large model underpredictions of radon
and soil-gas entry into two experimental basement structures
located in natural sandy-loam soil at a field site in Pen Lomond,
CA. Previously, the model input for permeability at the site had
been assessed based on 0.5-m scale measurements. After determining
the soil-structure interaction scale (system scale) to be similar
to 3 m, the model input was changed to reflect 3-m scale
permeability measurements. This adjustment reduced unacceptably
large model underpredictions, of a factor of 3 to 5, to a range
near that of acceptable experimental error, 20 to 40%, The
permeability scale effect may explain large and persistent model
underestimates of radon entry into real houses, The results argue
strongly for determining permeability at a length scale consistent
with that of the system under study.
C1 San Jose State Univ, Dept Environm Studies, San Jose, CA 95192
USA. Carnegie Mellon Univ, Dept Engn & Publ Policy, Pittsburgh, PA
15213 USA. Carnegie Mellon Univ, Dept Mech Engn, Pittsburgh, PA
15213 USA. Lawrence Berkeley Natl Lab, Indoor Environm Dept,
Environm & Energy Technol Div, Berkeley, CA USA. Univ Calif
Berkeley, Dept Civil & Environm Engn, Berkeley, CA 94720 USA.
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[12]
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Effects of variable wind speed and direction on radon transport from soil into
buildings: model development and exploratory results.
Atmos. Environ. 33, 2157-2168 (W. J. Riley, A. L.
Robinson, A. J. Gadgil, and W. W. Nazaroff) 1999 (12).
We describe a novel modeling technique, based on
Duhamel's theorem, to study the effects of time-varying winds on
radon transport in soil near buildings. The technique, implemented
in the model RapidSTART, reduces computational times for transient,
three-dimensional, wind-induced soil-gas and radon transport by
three to four orders of magnitude compared with conventional
finite-difference models. To test model performance, we compared
its predictions to analytical solutions of one-dimensional
soil-column flow, finite-difference simulations of how around a
full-scale house, and measurements of transient soil-gas and radon
entry into an experimental basement structure. These comparisons
demonstrate that RapidSTART accurately simulates time-dependent
radon transport through soil and its entry into buildings. As
demonstrated in a previous study, steady winds can significantly
affect radon entry. In this paper, we extend the findings of that
study by applying RapidSTART to explore the impacts of fluctuating
wind speed and direction on radon entry into a prototypical house.
In soils with moderate to high permeability, wind fluctuations have
a small to moderate effect on the soil-gas radon concentration
field and entry rate into the building. Fluctuating wind direction
dominates the impact on radon entry rates, while fluctuating wind
speed has little effect. For example, in a soil with a permeability
of 10(-10) m(2), diurnal oscillations in wind direction can
increase the predicted radon entry rate by up to 30% compared to
steady-state predictions. (C) 1999 Elsevier Science Ltd. All rights
reserved.
C1 Univ Calif Berkeley, Dept Environm Sci Policy & Management,
Ecosyst Sci Div, Berkeley, CA 94720 USA. Sandia Natl Labs, Combust
Res Facil, Livermore, CA 94551 USA. Lawrence Berkeley Natl Lab,
Indoor Environm Program, Berkeley, CA 94720 USA. Univ Calif
Berkeley, Dept Civil & Environm Engn, Berkeley, CA 94720 USA.
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[13]
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Global concentrations of tropospheric sulfate, nitrate, and ammonium aerosol
simulated in a general circulation model.
J. Geophys. Res.-Atmos. 104, 13791-13823 (P. J. Adams,
J. H. Seinfeld, and D. M. Koch) 1999 (77).
Global sulfate aerosol composition is simulated online
in the Goddard Institute for Space Studies general circulation
model II' (GISS GCM II-prime). Four sulfur species, hydrogen
peroxide, gas phase ammonia, and particulate ammonium are the
prognostic tracer species, the emissions, transport, and deposition
of which are explicitly simulated. Nitric acid fields are
prescribed based on a global chemical transport model. An online
thermodynamic equilibrium calculation determines the partitioning
of ammonia and nitrate between gas and aerosol phases, and the
quantity of aerosol water based on the temperature, relative
humidity, and sulfate concentration in each GCM grid cell. The
total global burden of sulfate, nitrate, ammonium, and aerosol
water is 7.5 Tg and is most sensitive to changes in sulfur
emissions. Tropospheric lifetimes for ammonium and ammonia are 4.2
and 0.9 days, respectively; the tropospheric ammonium burden is
0.30 Tg N, compared with 0.14 Tg N for ammonia. Simulated ammonium
concentrations are generally within a factor of 2 of observations.
Subgrid variability in measured concentrations hinders comparison
of observations to predictions. Ammonium nitrate aerosol plays an
important role in determining total aerosol mass in polluted
continental areas. In the upper troposphere and near the poles,
cold temperatures allow unneutralized nitric acid to condense into
the aerosol phase. Acidic aerosol species tend to be neutralized by
ammonia to a greater degree over continents than over oceans. The
aerosol is most basic and gas phase ammonia concentrations are
highest over India. Water uptake per mole of sulfate aerosol varies
by two orders of magnitude because of changes in relative humidity
and aerosol composition. Spatial variations in aerosol composition
and water uptake have implications for direct and indirect aerosol
radiative forcing.
C1 CALTECH, Dept Chem Engn, Pasadena, CA 91125 USA.
NASA, Goddard Inst Space Studies, New York, NY 10025 USA.
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[14]
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Dry deposition of particles to wave surfaces: I. mathematical modeling.
Atmos. Environ. 33, 4273-4281 (M. J. Zufall, W. P. Dai,
C. I. Davidson, and V. Etyemezian) 1999 (4).
Previous estimates of dry deposition to water surfaces
were generally based on deposition to flat, solid surfaces. This
paper examines the effects of waves on dry deposition rates by
numerically simulating particle trajectories over wave surfaces.
Airflows over two-dimensional sine waves with height-to-length
ratios 2a/lambda, = 0.1, 0.07, and 0.03 were calculated with a
commercial computational fluid dynamics model. Results from the
airflow simulations (velocity, kinetic energy, energy dissipation
rate, and shear stress) provided inputs for a stochastic particle
trajectory model. Particles were released from a height of 300
non-dimensional wall units at different locations along the wave.
For those between 1 and 20 mu m, deposition was found to be
greatest for particles released to the upslope portion of the
wave,followed by the trough, crest and downslope. Overall
deposition rates were enhanced due to the presence of waves.
Increases ranged from 5% (d(p) = 80 mu m) to 100% (d(p) = 1 mu m)
for waves with 2a/lambda = 0.07 and 0.1 and were approximately 50%
greater (d(p) = 1 - 80 mu m) for 2a/lambda = 0.03. Deposition rates
were enhanced due to increases in impaction and turbulent
transport, both of which increase with increasing wave slope.
However, an increased slope also produced regions of low or
reversed flow in the trough and downslope, which decreased
deposition rates. Due to these competing effects with respect to
wave slope, deposition rates did not increase monotonically with
wave slope. (C) 1999 Elsevier Science Ltd. All rights reserved. C1
Carnegie Mellon Univ, Dept Civil & Environm Engn, Pittsburgh, PA
15213 USA.
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[15]
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Dry deposition of particles to wave surfaces: II. wind tunnel experiments.
Atmos. Environ. 33, 4283-4290 (M. J. Zufall, W. P. Dai,
and C. I. Davidson) 1999 (5).
Wind tunnel measurements of particle dry deposition to
wavy and flat surfaces were made to estimate the enhancement of
deposition rates due to waves on water surfaces. Measurements were
made of 4.0 and 6.7 mu m uranine particles at wind speeds of 5 and
10 m s(-1) to sinusoidal waves with height to length ratios
2a/lambda = 0.1 and 0.03 and to flat surfaces. Results showed that
deposition was greatest to the upslope portion of the wave,
accounting for 40-45% of the total mass, followed by the trough
(30%), downslope (15%), and crest (10-15%). These results
generally agreed within experimental variability with modeling
predictions (Zufall et al., 1999). Deposition was enhanced at the
upslope due to the effects of particle interception and impaction
on the wave. Total deposition to the wave surfaces was greater than
deposition to the flat surface for a large majority of the cases.
The average increase in deposition to both wave surfaces for both
particle sizes and wind speeds over deposition to the flat surface
was 80%. (C) 1999 Elsevier Science Ltd. All rights reserved.
C1 Carnegie Mellon Univ, Dept Civil & Environm Engn, Pittsburgh,
PA 15213 USA.
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