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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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Testing frontier orbital control: Kinetics of OH with ethane, propane, and
cyclopropane from 180 to 360k.
J. Phys. Chem. A 102, 9847-9857 (J. S. Clarke, J. H.
Kroll, N. M. Donahue, and J. G. Anderson) 1998 (40).
We test the hypothesis that the barrier to a gas-phase
radical-molecule reaction is controlled by an avoided curve
crossing of ground and ionic states of the reactants and products.
We focus on the competing role of orbital overlap and energy
difference on the delocalization energy of the transition state,
comparing the reactions OH + ethane, OH + propane, and OH +
cyclopropane using experimental data and theoretical analysis.
These reactions constitute a homologous series in which the spatial
extent and energy of interacting orbitals change dramatically,
providing for an examination of the relative importance of energy
sind overlap on barrier height control. In addition, contrasting
pictures of barrier height control, either by molecular properties
or by bond properties of the reactants and products, are evaluated.
Our kinetic data, obtained in a high-pressure flow system, cover a
suppressed temperature range (180 - 360 K) in order to isolate the
lowest barrier pathway. The results for ethane and propane are
consistent with barrier height control by the singly occupied
molecular orbital (SOMO) of the OH radical and the highest occupied
molecular orbital (HOMO) of the molecule. These are the
historically defined frontier orbitals. The results for
cyclopropane, however, suggest that it is the interaction of the
SOMO with the second highest occupied molecular orbitals (SHOMOs)
which controls barrier height. The SHOMOs of cyclopropane are
spatially extended relative to the HOMOs; at the transition state
the interaction between OH and the SHOMOs of cyclopropane
overwhelms the interaction between OH and the HOMOs of
cyclopropane. We examine the competition between energy and overlap
of two reacting species and present an alternative definition of
the frontier orbitals not necessarily as the highest energy
orbitals, but rather as the orbitals that delocalize to the
greatest extent at the transition state. C1 Harvard Univ, Dept Chem
& Chem Biol, Cambridge, MA 02138 USA.
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[2]
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Predicting radical-molecule barrier heights: The role of the ionic surface.
J. Phys. Chem. A 102, 3923-3933 (N. M. Donahue, J. S.
Clarke, and J. G. Anderson) 1998 (43).
We present a theory of radical-molecule abstraction
reactions based on the crossing of reactant ground and ionic states
at the transition state. By calculating the evolution of ground-
and ionic-state energies as the reactants approach each other, we
are able to specify the boundary conditions for an avoided curve
crossing problem as the atom is transfered. The lower the
ionic-state energy, the lower in energy the transition state will
be. This drives strong correlations between barrier heights and the
difference of ionicand ground-state energies. This theory
successfully explains the evolution of barrier heights in a series
of reactions involving alkanes and several radicals (OH, O, H, F,
Cl, Br), in which barriers range from 0 to 10 kcal/mol. A
perturbation treatment of the ionic- and ground-state energies
improves the performance of the theory. We compare predicted
curve-crossing heights with observed barriers for both our theory
and for the covalent (singlet-triplet) curve-crossing theory. We
also compare observed barriers with reaction enthalpy. Only the
ionic curve-crossing theory can simultaneously explain both radical
and molecule reactivity. C1 Harvard Univ, Dept Chem & Biol Chem,
Cambridge, MA 02138 USA.
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[3]
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New rate constants for ten OH alkane reactions from 300 to 400 k: An
assessment of accuracy.
J. Phys. Chem. A 102, 3121-3126 (N. M. Donahue, J. G.
Anderson, and K. L. Demerjian) 1998 (39).
OH alkane reactions play a central role in atmospheric
and combustion chemistry, and accurate modeling requires accurate
knowledge of their rate constants over a wide temperature range. We
present data for 10 OH radical - alkane reactions over the
temperature range 300-400 K and then combine our data with other
literature data to find optimally estimated Arrhenius parameters
using a modified Arrhenius form consistent with transition state
theory. This modified form explicitly accounts for the loose modes
in the transition state that cause curvature in Arrhenius plots. It
thus fits data over a wide temperature range in a realistic manner,
allowing precise comparison of data sets covering different
temperature ranges. By comparing our data with other published
data, we establish that most of these rate constants are now known
to better than 5% accuracy over the 300-400 K temperature range.
C1 Harvard Univ, Dept Chem & Biol Chem, Cambridge, MA 02138 USA.
SUNY Albany, Dept Earth Atmospher Sci, Albany, NY 12222 USA.
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[4]
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Direct observation of OH production from the ozonolysis of olefins.
Geophys. Res. Lett. 25, 59-62 (N. M. Donahue, J. H.
Kroll, J. G. Anderson, and K. L. Demerjian) 1998 (75).
Ozone olefin reactions may be a significant source of
OH in the urban atmosphere, but current evidence for OH production
is indirect and contested. We report the first direct observation
of OH radicals from the reaction of ozone with a series of olefins
(ethene, isoprene, trans-2-butene and 2,3 dimethyl-2-butene) in 4-6
torr of nitrogen. Using LIF to directly observe the steady-state of
OH produced by the initial ozone-olefin reaction and subsequently
destroyed by the OH-olefin reaction, we are able to establish OH
yields broadly consistent with indirect values. The identification
of the OH is unequivocal, and there is no indication that it is
produced by a secondary process. To support these observations, we
present a complete ab-initio potential energy surface for the
O-3-ethene reaction, extending from the reactants to available
products.
C1 Harvard Univ, Dept Chem, Cambridge, MA 02138 USA.
SUNY Albany, Dept Earth Atmospher Sci, Albany, NY 12203 USA. SUNY
Albany, Atmospher Sci Res Ctr, Albany, NY 12203 USA.
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[5]
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Isorropia: A new thermodynamic equilibrium model for multiphase multicomponent
inorganic aerosols.
Aquat. Geochem. 4, 123-152 (A. Nenes, S. N. Pandis, and
C. Pilinis) 1998 (128).
A computationally efficient and rigorous thermodynamic
model that predicts the physical state and composition of inorganic
atmospheric aerosol is presented. One of the main features of the
model is the implementation of mutual deliquescence of
multicomponent salt particles, which lowers the deliquescence point
of the aerosol phase. The model is used to examine the behavior of
four types of tropospheric aerosol (marine, urban, remote
continental and non-urban continental), and the results are
compared with the predictions of two other models currently in use.
The results of all three models were generally in good agreement.
Differences were found primarily in the mutual deliquescence
humidity regions, where the new model predicted the existence of
water, and the other two did not. Differences in the behavior
(speciation and water absorbing properties) between the aerosol
types are pointed out. The new model also needed considerably less
CPU time, and always shows stability and robust convergence. C1
Univ Aegean, Dept Environm Sci, 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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[6]
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Response of inorganic pm to precursor concentrations.
Environ. Sci. Technol. 32, 2706-2714 (A. S. Ansari and
S. N. Pandis) 1998 (29).
[ DOI |
.pdf ]
An inorganic aerosol equilibrium model is used to
investigate the response of inorganic particulate matter (PM)
concentrations with respect to the precursor concentrations of
sulfuric acid, ammonia, and nitric acid over a range of
temperatures and relative humidities. Diagrams showing regions of
PM response to precursor concentrations are generated,thus allowing
the qualification of assumptions concerning the response of PM to
sulfate and overall sensitivity to ammonia and nitric acid
availability. The PM concentration level responds nonlinearly to
sulfate and shows overall sensitivity to ammonia and nitric acid
availability for specific atmospheric conditions and precursor
concentrations. The generated diagrams are applied as a means of
approximating the PM response to precursor concentrations for two
urban polluted areas. In both cases, reductions in ammonia
emissions have the most significant impact on the total PM level.
However, such a reduction will result in significant increases in
atmospheric acidity. C1 Carnegie Mellon Univ, Dept Chem Engn &
Engn Publ Policy, Pittsburgh, PA 15213 USA.
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[7]
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Marginal direct climate forcing by atmospheric aerosols.
Atmos. Environ. 32, 2531-2542 (J. J. West, C. Pilinis,
A. Nenes, and S. N. Pandis) 1998 (12).
Previous research on the direct effect of atmospheric
aerosols on climate has estimated the average radiative forcing per
unit sulfate mass, and has used this average to calculate the
magnitude and spatial distribution of sulfate forcing. In this
paper, we posit that radiative forcing is often a nonlinear
function of sulfate mass concentration. In contrast to measures of
average forcing, we introduce the concept of marginal forcing,
which is defined as the change in radiative forcing for an
incremental change in sulfate concentration. A multi-component,
size-resolved aerosol box model is used, which couples an aerosol
chemical equilibrium model with a model for calculating radiative
forcing based on Mie theory. The results for a typical nonurban
continental aerosol show that total aerosol mass and radiative
forcing are nonlinear functions of sulfate concentration. This
nonlinearity is mainly due to the chemical interaction of sulfate
with volatile inorganic components of the aerosol (ammonium,
nitrate, and water). As a result, the marginal forcing varies
significantly as a function of sulfate concentration, from - 550 to
+ 20 W (g SO42-)(-1) at a relative humidity (RH) of 80%. Estimates
of marginal forcing are strongly sensitive to RH. Absolute marginal
forcing also decreases significantly with total nitrate
concentration, increases with total ammonia concentration, and
generally increases with temperature. We estimate hat the bias in
assuming a constant average forcing may cause overestimates in
local continental aerosol radiative forcing by up to 50%, and in
the marginal forcing by a factor of two or more.This bias is
greatest at intermediate sulfate concentration, high RH, high total
nitrate concentration,low total ammonia concentration( greater than
or equal to 2 mu g m(-3)), and low temperature. (C) 1998 Published
by 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. Carnegie Mellon Univ, Dept Civil & Environm Engn,
Pittsburgh, PA 15213 USA. Univ Aegean, Dept Environm Sci, GR-81100
Mytilene, Greece. Univ Miami, Rosenstiel Sch Marine & Atmospher
Sci, Miami, FL 33149 USA.
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[8]
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The effect of organic coatings on the cloud condensation nuclei activation of
inorganic atmospheric aerosol.
J. Geophys. Res.-Atmos. 103, 13111-13123 (C. N. Cruz and
S. N. Pandis) 1998 (79).
Atmospheric aerosols have mixed chemical composition,
with a variety of inorganic (e.g., sulfate, nitrate, ammonium, and
sodium) and organic species often present in a single particle. In
the present study, we investigate experimentally the cloud
condensation nuclei (CCN) activation of submicron aerosol
consisting of an inorganic core (e.g., ammonium sulfate) coated by
an organic film, at typical atmospheric supersaturations. We use
two types of organic coatings on the (NH4)(2)SO4 particles. The
first is glutaric acid, a CCN active organic found in the
atmosphere, and the second species is dioctylphthalate (DOP), a
nonhygroscopic organic. The CCN activation of (NH4)(2)SO4-glutaric
acid particles was measured at a supersaturation of 0.3%, for
different inorganic core sizes and organic film thickness. We found
that a coating of glutaric acid increases the CCN activation of an
(NH4)(2)SO4 particle and that this behavior can be predicted by
Kohler theory. The deviation from Kohler theory for the mixed
aerosol was determined by comparing theoretical and experimental
CCN activation diameters for the particles and was found to be
within experimental error. A thick coating of DOP (at least 70% by
mass) did not hinder the activation of (NH4)(2)SO4 particles at
supersaturations of 0.5 and 1.0%. The values for the measured
activation diameters for the DOP coated (NH4)(2)SO4 particles were
within the experimental error determined by the pure inorganic
experiments, indicating that DOP was most likely acting as inert
mass during activation.
C1 Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA 15213 USA.
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[9]
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Inversion of ultrafine condensation nucleus counter pulse height distributions
to obtain nanoparticle (similar to 3-10 nm) size distributions.
J. Aerosol. Sci. 29, 601-615 (R. J. Weber, M. R.
Stolzenburg, S. N. Pandis, and P. H. McMurry) 1998 (20).
Previous work (Ahn and Liu (1990) J. Aerosol. Sci. 21,
249-261; Brockmann (1981) Ph.D. Thesis, University of Minnesota;
Rebours et al. (1992) J. Aerosol. Sci. 23, S189-S192; Stolzenburg
(1988) Ph.D. thesis, University of Minnesota) has shown that for
particles smaller than about 15 nm, pulse heights produced by the
optical detector in a white-light ultrafine condensation nucleus
counter (UCNC; Stolzenburg and McMurry (1991) Aerosol. Sci.
'Technol. 14, 48-65) decrease with initial particle size. We have
previously reported on the use of pulse heights from this
instrument to determine the concentrations of freshly nucleated
atmospheric nanoparticles in the 3-4 nm diameter range (Weber et
al. (1995) J. Atm. Sci. 52, 2242-2257) Weber et al. (1997) J.
Geophys. Res. 102, 4375-4385). In this paper we report on the
inversion of measured pulse-height distributions to obtain size
distributions of particles in the 3-10 nm diameter range. Using
methods developed by Stolzenburg (Stolzenburg (1988) Ph.D. Thesis,
University of Minnesota) the effect of diffusional broadening is
taken into account so as to obtain monodisperse kernel functions
from measured pulse-height distributions produced by DMA-generated
calibration aerosols in the 3-50 nm diameter range. These kernel
functions are then used with the MICRON algorithm described by
Wolfenbarger and Seinfeld (1990, J. Aerosol. Sci. 21, 227-247) to
obtain size distributions of nanoparticle aerosols from measured
pulse height distributions. Calculations were done to ensure that
assumed pulse-height data generated from selected known size
distributions can be inverted to recover the original size
distribution. Results from these validation studies are discussed.
Applications of the inversion algorithm to data acquired in studies
of homogeneous nucleation in the atmosphere are also presented.
Published by Elsevier Science Ltd.
C1 Brookhaven Natl Lab, Environm Chem Div, Upton, NY 11973 USA.
Aersol Dynam Inc, Albany, CA 94710 USA.
Carnegie Mellon Univ, Dept Chem Engn, Pittsburgh, PA 15213 USA.
Univ Minnesota, Dept Mech Engn, Particle Technol Lab, Minneapolis,
MN 55455 USA.
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[10]
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Vertical gradients of pollutant concentrations and deposition fluxes on a tall
limestone building.
J. Am. Inst. Conserv. 37, 187-210 (V. Etyemezian, C. I.
Davidson, S. Finger, M. F. Striegel, N. Barabas, and J. C. Chow) 1998
(4).
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[11]
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Biomass burning signatures in the atmosphere of central greenland.
J. Geophys. Res.-Atmos. 103, 31067-31078 (J. L.
Jaffrezo, C. I. Davidson, H. D. Kuhns, M. H. Bergin, R. Hillamo, W. Maenhaut,
J. W. Kahl, and J. M. Harris) 1998 (12).
Daily atmospheric concentrations of particulate
oxalate measured at the Summit of the Greenland Ice Sheet are
presented for the summers 1992 - 1995. We believe that four
episodes of elevated concentrations are due to biomass burning
plumes passing over the site. In at least two cases the source
regions of the fires are located in northern Canada. Further
characteristics of the aerosol are examined during one of these
events. A large increase of particle number concentrations in the
accumulation mode can be observed, while the increase is much more
limited for total particle number, The suite of chemical species
enriched in the aerosol includes typical biomass burning tracers
like fine K, large concentrations of ammonium, particulate formate
and acetate, as well as other organic species like glycolate. The
size distributions of K, oxalate, and glycolate are skewed toward
the accumulation mode and exhibit the very same shape as sulfate,
suggesting internal mixing of these species in the same particles.
Molar ratios S/K indicate incorporation of S during transport, most
probably by production of sulfate, Concentrations of these species
were measured in fog samples for radiative events that occurred
during the plume passage. There is a good agreement in the relative
variation of concentrations between the aerosol and fog for oxalate
and glycolate, while the gas phase probably dominates incorporation
in the fog droplets for acetate, formate, chloride, nitrate, and
sulfate (incorporated as SO2, which is further oxidized), The
complexity of the transfer of the organic acids from the atmosphere
to fog is underlined.
C1 Lab Glaciol & Geophys Environm, F-38402 St Martin Dheres,
France. Georgia Inst Technol, Dept Civil & Environm Engn, Atlanta,
GA 30332 USA. Carnegie Mellon Univ, Dept Civil & Environm Engn,
Pittsburgh, PA 15213 USA. NOAA, Climate Monitoring & Diagnost Lab,
Boulder, CO 80303 USA. Finnish Meteorol Inst, FIN-00810 Helsinki,
Finland.
Univ Wisconsin, Dept Geosci, Milwaukee, WI 53211 USA. Inst Nucl
Sci, B-9000 Ghent, Belgium.
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[12]
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Seasonal variations in the origin of lead in snow at dye 3, greenland.
Earth Planet. Sci. Lett. 160, 383-389 (K. J. R. Rosman,
W. Chisholm, C. F. Boutron, J. P. Candelone, J. L. Jaffrezo, and C. I.
Davidson) 1998 (14).
The isotopic composition and concentration of lead has
been measured in fresh and slightly aged snow collected at Dye 3 in
southern Greenland during one full year. The lead concentration
displayed large variations ranging from 14-3016 pg/g in April
(spring) to 3-6 pg/g in September (summer) while the isotopic
ratios changed in regular manner during the year. The Pb-206/Pb-207
ratios were similar to 1.15 from spring to mid-summer snow, and
increased in late summer to early autumn, reaching similar to 1.20
in winter. These isotopic data indicate that the lead in the autumn
to winter snow originated in North America, while that in spring to
mid-summer snow is from Eurasia. (C) 1998 Elsevier Science B.V. All
rights reserved.
C1 Curtin Univ Technol, Dept Appl Phys, Perth, WA 6845, Australia.
CNRS, Lab Glaciol & Geophys Environm, F-38402 St Martin Dheres,
France. Univ Grenoble 1, Inst Univ France, UFR Mecan, F-38041
Grenoble, France. Carnegie Mellon Univ, Dept Civil Engn,
Pittsburgh, PA 15213 USA.
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[13]
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Mass balance for lead in the California south coast air basin: An update.
Environ. Res. 78, 86-93 (R. L. Lankey, C. I. Davidson,
and F. C. McMichael) 1998 (17).
A mass balance for lead for the year 1989 in the South
Coast Air Basin has inputs to the atmosphere of 600 +/- 190 kg/day
and outputs of 580 +/- 160 kg/day, showing rough agreement.
Stationary sources are responsible for only about 5% of the total
lead emissions. The bulk of the lead is emitted from vehicles using
leaded gasoline (37%) and unleaded gasoline (15%), as well as
from resuspension of previously deposited lead on roads (43%).
Over half of the total emitted lead deposits on roads and nearby
soil, while about one-third is carried out of the basin by wind. A
small amount, less than 10%, is deposited on surfaces throughout
the basin. These percentages are approximately the same as those in
a mass balance for the same region calculated for 1972, when lead
emissions from leaded gasoline were about a factor of 70 greater
than leaded gas emissions in 1989. When the lead emissions are used
as inputs to a simple continuously stirred flow reactor model for
the basin, reasonable agreement is obtained between calculated and
measured concentrations. (C) 1998 Academic Press.
C1 Carnegie Mellon Univ, Dept Civil & Environm Engn, Pittsburgh,
PA 15213 USA. Carnegie Mellon Univ, Dept Engn & Publ Policy,
Pittsburgh, PA 15213 USA.
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[14]
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Determination of size-dependent dry particle deposition velocities with
multiple intrinsic elemental tracers.
Environ. Sci. Technol. 32, 1615-1622 (P. F. Caffrey,
J. M. Ondov, M. J. Zufall, and C. I. Davidson) 1998 (36).
Dry deposition flux and aerosol size distribution
measurements were made concurrently aboard the RV Lake Guardian 19
km east of the Chicago shoreline during summer 1994 to assess
atmospheric inputs of minor and trace elements to southern Lake
Michigan. Size-segregated aerosol measurements were made over
consecutive 12-h periods with Micro-Orifice and Noll Rotary
impacters (MOI and NRI), and depositing-particulate collections to
aerodynamically smooth airfoils were made over periods of 3-4 days.
The combination of the MOI and NRI provided size-segregated
particulate samples in 12 discrete intervals between 0.059 and,
nominally, 100 mu m. The samples were analyzed for As, Ca, Mg, Se,
Sb, V, and Zn by instrumental neutron activation analysis and for S
by X-ray-fluorescence. Aerosol and deposition data for individual
elemental constituents were fit with a chemical mass balance
deposition (CMBD) model in which a set of particle-size-specific
deposition velocities (V-d), best reconciling the deposition data,
were determined by iterative (constrained) solution of a series of
six linear equations using the Levenberg-Marquardt method. Under
stable conditions and mean wind speed of 4.0 m s(-1), minimum V-d
values for particles with physical diameters between 0.09 and 0.53
mu m averaged 0.006 +/- 0.005 cm s(-1), wherein uncertainties were
determined by Monte Carlo analysis. This agrees favorably with
Values determined by microscopy for which uncertainties were much
larger and with those predicted by the Williams model for the same
period. The results suggest that physically significant V-d values
are obtainable from a constrained CMBD model.
C1 Univ Maryland, Dept Chem & Biochem, College Pk, MD 20742 USA.
Carnegie Mellon Univ, Dept Civil & Environm Engn, Pittsburgh, PA
15213 USA.
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[15]
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Airborne concentrations and dry deposition fluxes of particulate species to
surrogate surfaces deployed in southern lake michigan.
Environ. Sci. Technol. 32, 1623-1628 (M. J. Zufall,
C. I. Davidson, P. F. Caffrey, and J. M. Ondov) 1998 (38).
Dry deposition flux measurements to surrogate surfaces
and airborne concentration measurements of Zn-containing, S-rich,
and soil particles (analyzed by scanning electron microscopy) and
Al, Ba, Dr, Ca, Cl, Cu, K, Mg, Mn, Na, Ti, and V (analyzed by
neutron activation analysis) were made over southwestern Lake
Michigan in July 1994 and January 1995 to determine atmospheric
inputs of pollutants to the lake. Samples collected in the summer
show that despite relatively tow airborne concentrations of
particles with physical diameters >8 mu m, these particles account
for the majority of the dry deposition mass flux. However, this
sharp contrast is not found during January when particles with
physical diameters of 4-8 mu m dominate both the airborne
concentration and the flux. Dry deposition velocities (flux divided
by airborne concentration) for particles are found to range from
0.0062 cm/s for 0.75-mu m particles to 5.4 cm/s far 24-mu m
particles. C1 Carnegie Mellon Univ, Dept Civil & Environm Engn,
Pittsburgh, PA 15213 USA. Univ Maryland, Dept Chem & Biochem,
College Pk, MD 20742 USA.
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[16]
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Effects of non-equilibrium hygroscopic growth of (nh4)(2)so4 on dry deposition
to water surfaces.
Environ. Sci. Technol. 32, 584-590 (M. J. Zufall, M. H.
Bergin, and C. I. Davidson) 1998 (7).
Growth of hygroscopic aerosols near water surfaces is
believed to enhance dry deposition rates, which are a strong
function of particle size. Previous dry deposition models estimate
hygroscopic growth by assuming equilibrium between aerosols and
water vapor (Williams, R. M. Atmos. Environ. 1982, 16, 1933-1938).
A model is presented here that combines the relative humidity
profile above water surfaces with hygroscopic growth rates for
(NH4)(2)SO4, assuming cases for a deliquescing and metastable
aerosol. Model results show that particles greater than 0.1 mu m in
diameter do not grow to their equilibrium size before depositing to
a hypothetical water surface. As a consequence, equilibrium models
overpredict the effects of hygroscopic growth on deposition
velocities by as much as a factor of 5. In addition, model results
suggest a significant difference in the deposition velocities of
metastable and deliquescing aerosols. Based on measured (NH4)(2)SO4
size distributions, overall deposition velocities calculated from a
thermodynamic equilibrium model, a mass transfer limited
non-equilibrium model with a deliquescing aerosol, and a mass
transfer limited non-equilibrium model with a metastable aerosol
are 0.11, 0.055, and 0.040 cm/s, respectively.
C1 Carnegie Mellon Univ, Dept Civil & Environm Engn, Pittsburgh,
PA 15213 USA. NOAA, Climate Monitoring & Diagnost Lab, Boulder, CO
80303 USA. Brookhaven Natl Lab, Environm Chem Div, Upton, NY 11973
USA.
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