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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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Aerosol production and growth in the marine boundary-layer.
J. Geophys. Res.-Atmos. 99, 20989-21003 (L. M. Russell,
S. N. Pandis, and J. H. Seinfeld) 1994 (86).
The dependence of cloud condensation nuclei (CCN)
production on the marine dimethylsulfide (DMS) flux is modeled with
a dynamic description of the gas, aerosol, and aqueous phase
processes in a closed air parcel. The results support the
conclusion reached in previous work with a steady state model that
an approximately linear dependence exists between CCN concentration
and DMS flux under typical remote marine conditions. This linearity
does not hold for low DMS fluxes (the threshold is typically near
2.5 mu mol m(-2) day(-1)) because the seasalt particles
heterogeneously convert the available SO2 to sulfate inhibiting the
creation of new particles. The conditions under which this linear
relationship holds are investigated by a series of sensitivity
studies, focusing particular attention on the impact of the timing
and frequency of cloud events. We consider the regimes of the
model's semiempirical parameters, showing that the uncertainty
associated with two such parameters, namely, the nucleation rate
scaling factor and the sulfuric acid accommodation coefficient, is
sufficient to change the predicted CCN production due to DMS from
over 300 cm(-3) day(-1) to none. This sensitivity accounts for most
of the range of results predicted by previous models of the DMS-CCN
system. C1 CARNEGIE MELLON UNIV,DEPT ENGN & PUBL
POLICY,PITTSBURGH,PA 15213. CALTECH,DEPT CHEM ENGN,PASADENA,CA
91125.
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[2]
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The relationship between dms flux and ccn concentration in remote marine
regions.
J. Geophys. Res.-Atmos. 99, 16945-16957 (S. N. Pandis,
L. M. Russell, and J. H. Seinfeld) 1994 (69).
The relationship between the steady state cloud
condensation nuclei (CCN) concentration and the dimethylsulfide
(DMS) emission flux in remote marine regions is investigated by
modeling the principal gas-, aerosol-, and aqueous-phase processes
in the marine boundary layer (MBL). Results are in reasonable
quantitative agreement with the available measurements of DMS, SO2,
H2SO4, CCN, and condensation nuclei (CN) concentrations in remote
marine regions of the globe and suggest that indeed DMS plays a
major role in the particle dynamics of the MBL. For sufficiently
low DMS fluxes practically all the SO2, produced by DMS
photooxidation is predicted to be heterogeneously converted to
sulfate in sea-salt aerosol particles. For DMS fluxes higher than
approximately 2.5 mumole m-2 d-1 a linear relationship is found to
exist between the CCN number concentration and the DMS flux. C1
CALTECH,DEPT CHEM ENGN,PASADENA,CA 91125.
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[3]
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Fluxes of chemical-species to the greenland ice-sheet at summit by fog and dry
deposition.
Geochim. Cosmochim. Acta 58, 3207-3215 (M. H. Bergin,
J. L. Jaffrezo, C. I. Davidson, R. Caldow, and J. Dibb) 1994 (19).
Experiments were performed during June-July 1992 to
determine the impact of dry deposition and fog deposition on
surface snow chemical inventories. The fluxes of SO42-, NO3-, Cl-,
MSA, Na, Ca, and Al were measured by collecting deposited fog on
flat polyethylene plates. Dry deposition fluxes of SO42were
measured using aerodynamic surfaces. Real-time concentrations of
atmospheric particles greater than 0.5 um and greater than 0.01 um
were measured using continuous monitors. Filter samplers were used
to determine daily average atmospheric SO42- and MSA
concentrations. Also, daily surface snow samples were taken and
analyzed for SO42-, NO3-, Cl-, Na+, Ca2+, and NH4+. The real-time
concentration data indicate that aerosol particles greater than 0.5
um are efficiently incorporated into fog droplets. Results also
show that condensation nuclei (CN) are not as greatly affected by
fog as the larger particles. Fog fluxes of SO42- and NO3- have
similar values and are approximately 4 times greater than those of
Cl-, an order of magnitude greater than those of MSA, Na, and Ca,
and two orders of magnitude greater than those of Al. The fog
deposition flux of SO42- appears to be much greater than the dry
deposition flux, based on experimental data. This indicates that
dry deposition has a negligible effect on surface snow SO42-
concentrations on days when there is fog. Such a finding is
consistent with significant increases in surface snow SO42-, NO3-,
and NH4+ inventories seen after fog events. Cl- surface snow
inventories are affected by fog but not as greatly. Variation in
surface snow chemical inventories makes it difficult to obtain
quantitative estimates of daily chemical fluxes. Surface snow Ca2+
and Na+ are relatively unaffected by post snowfall processes due to
low atmospheric concentrations relative to the amount of material
in fresh snow. Model results suggest that the fog fluxes have been
underestimated by the current sampling technique.
C1 CNRS,LAB GLACIOL & GEOPHYS ENVIRONNEMENT,F-38402 ST MARTIN
DHERES,FRANCE. TSI INC,ST PAUL,MN 55126.
UNIV NEW HAMPSHIRE,INST STUDY EARTH OCEANS & SPACE,DURHAM,NH
03824.
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[4]
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Sulfate and msa in the air and snow on the greenland ice-sheet.
J. Geophys. Res.-Atmos. 99, 1241-1253 (J. L. Jaffrezo,
C. I. Davidson, M. Legrand, and J. E. Dibb) 1994 (30).
Sulfate and methanesulfonic acid (MSA) concentrations
in aerosol, surface snow, and snowpit samples have been measured at
two sites on the Greenland Ice Sheet. Seasonal variations of the
concentrations observed for these chemical species in the
atmosphere are reproduced in the surface snow and preserved in the
snowpit sequence. The amplitude of the variations over a year are
smaller in the snow than in the air, but the ratios of the
concentrations are comparable. The seasonal variations for sulfate
are different at the altitude of the Ice Sheet compared to those
observed at sea level, with low concentrations in winter and short
episodes of elevated concentrations in spring. In contrast, the
variations in concentrations of MSA are similar to those measured
at sea level, with a first sequence of elevated concentrations in
spring and another one during summer, and a winter low resulting
from low biogenic production. The ratio MSA/sulfate clearly
indicates the influence of high-latitude sources for the summer
maximum of MSA, but the large impact of anthropogenic sulfate
precludes any conclusion for the spring maximum. The seasonal
pattern observed for these species in a snowpit sampled according
to stratigraphy indicates a deficit in the accumulation of winter
snow at the summit of the Greenland Ice Sheet, in agreement with
some direct observations. A deeper snowpit covering the years
1985-1992 indicates the consistency of the seasonal pattern for MSA
over the years, which may be linked to transport and deposition
processes.
C1 CARNEGIE MELLON UNIV,DEPT CIVIL ENGN,PITTSBURGH,PA 15213. UNIV
NEW HAMPSHIRE,INST STUDY EARTH OCEANS & SPACE,GLACIER RES
GRP,DURHAM,NH 03824.
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[5]
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In-situ nonmethane hydrocarbon measurements on saga-3.
J. Geophys. Res.-Atmos. 98, 16915-16932 (N. M. Donahue
and R. G. Prinn) 1993 (51).
During the third Soviet-American Gas and Aerosol (SAGA
3) expedition to the central Pacific in February to March 1990 we
observed C1 - C5 nonmethane hydrocarbons (NMHCs) both in the
atmosphere and in the ocean. Atmospheric NMHCs project strongly on
two factors: those NMHCs with lifetimes over 1 week (ethane,
ethyne, propane, cyclopropane) display north-south latitudinal
gradients whose magnitudes are proportional to their photochemical
loss rates, which is consistent with a northern hemispheric,
continental source, while those NMHCs with lifetimes under 1 week
(all alkenes and pentane) do not display latitudinal gradients but
do vary in common in a more complicated manner, consistent with a
heterogeneous, marine source. Data taken from a sea water
equilibrator shows that alkene concentrations vary strongly with
wind speed, supporting previous conclusions that sea-air evasion is
a major loss term for mixed layer alkenes. A reasonable balance
exists between sea-air fluxes and atmospheric column removal for
some alkenes (ethene, propene, 1-butene, and 1-pentene), while the
remainder are out of balance, with partial pressures insufficient
to support atmospheric observations. The total NMHC sea-air flux is
about 0.8 mumole m-2 d-1. Both our air and water concentrations
fall near the low end of previously observed ranges. It is argued
that some previous higher atmospheric observations may reflect
systematic problems with canister sampling. During SAGA 3 the role
of NMHCs in the remote atmospheric OH budget was secondary though
important, accounting (in conjunction with NMHC oxidation products)
for 10 to 20% of all OH removal during baseline periods and a
substantially larger fraction during episodes of increased NMHC
mixing ratios.
C1 MIT,CTR GLOBAL CHANGE SCI,CAMBRIDGE,MA 02139.
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[6]
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Ozone observations and a model of marine boundary-layer photochemistry during
saga-3.
J. Geophys. Res.-Atmos. 98, 16955-16968 (A. M. Thompson,
J. E. Johnson, A. L. Torres, T. S. Bates, K. C. Kelly, E. Atlas, J. P.
Greenberg, N. M. Donahue, S. A. Yvon, E. S. Saltzman, B. G. Heikes, B. W.
Mosher, A. A. Shashkov, and V. I. Yegorov) 1993 (92).
A major purpose of the third joint Soviet-American
Gases and Aerosols (SAGA 3) oceanographic cruise was to examine
remote tropical marine O3 and photochemical cycles in detail. On
leg 1, which took place between Hilo, Hawaii, and Pago-Pago,
American Samoa, in February and March 1990, shipboard measurements
were made Of O3, CO, CH4, nonmethane hydrocarbons (NMHC), NO,
dimethyl sulfide (DMS), H2S, H2O2, organic peroxides, and total
column O3. Postcruise analysis was performed for alkyl nitrates
and a second set of nonmethane hydrocarbons. A latitudinal gradient
in O3 was observed on SAGA 3, with O3 north of the intertropical
convergence zone (ITCZ) at 15-20 parts per billion by volume (ppbv)
and less than 12 ppbv south of the ITCZ but never
less-than-or-equal-to 3 ppbv as observed on some previous
equatorial Pacific cruises (Piotrowicz et al., 1986; Johnson et
al., 1990). Total column O3 (230-250 Dobson units (DU)) measured
from the Akademik Korolev was within 8% of the corresponding total
ozone mapping spectrometer (TOMS) satellite observations and
confirmed the equatorial Pacific as a low O3 region. In terms of
number of constituents measured, SAGA 3 may be the most
photochemically complete at-sea experiment to date. A
one-dimensional photochemical model gives a self-consistent picture
of O3-NO-CO-hydrocarbon interactions taking place during SAGA 3. At
typical equatorial conditions, mean O3 is 10 ppbv with a 10-15%
diurnal variation and maximum near sunrise. Measurements of O3, CO,
CH4, NMHC, and H2O constrain model-calculated OH to 9 x 10(5) cm-3
for 10 ppbv O3 at the equator. For DMS (300-400 parts per trillion
by volume (pptv)) this OH abundance requires a sea-to-air flux of
6-8 x 10(9) cm-2 s-1, which is within the uncertainty range of the
flux deduced from SAGA 3 measurements of DMS in seawater (Bates et
al., this issue). The concentrations of alkyl nitrates on SAGA 3
(5-15 pptv total alkyl nitrates) were up to 6 times higher than
expected from currently accepted kinetics, suggesting a largely
continental source for these species. However, maxima in isopropyl
nitrate and bromoform near the equator (Atlas et al., this issue)
as well as for nitric oxide (Torres and Thompson, this issue) may
signify photochemical and biological sources of these species. C1
NATL CTR ATMOSPHER RES,BOULDER,CO 80307.
NOAA,PACIFIC MARINE ENVIRONM LAB,SEATTLE,WA 98115.
HARVARD UNIV,CAMBRIDGE,MA 02138.
UNIV RHODE ISL,GRAD SCH OCEANOG,KINGSTON,RI 02882.
UNIV NEW HAMPSHIRE,DURHAM,NH 03824.
UNIV MIAMI,ROSENSTIEL SCH MARINE & ATMOSPHER SCI,MIAMI,FL 33149.
MAIN GEOPHYS OBSERV,ST PETERSBURG,RUSSIA.
NASA,GODDARDS SPACE FLIGHT CTR,WALLOPS FLIGHT FACIL,WALLOPS ISL,VA
23337. INST APPL PHYS,ATMOSPHER MONITORING LAB,MOSCOW,RUSSIA.
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[7]
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Secondary organic aerosol formation and transport .2. predicting the ambient
secondary organic aerosol-size distribution.
Atmos Environ Pt A-Gen Top 27, 2403-2416 (S. N. Pandis,
A. S. Wexler, and J. H. Seinfeld) 1993 (64).
The size distribution of atmospheric secondary organic
aerosol is simulated by a Lagrangian trajectory model that includes
descriptions of gas-phase chemistry, inorganic and organic aerosol
thermodynamics, condensation/evaporation of aerosol species, dry
deposition and emission of primary gaseous and particulate
pollutants. The model is applied to simulate the dynamics of
aerosol size and composition along trajectories on 27-28 August
1987 during the Southern California Air Quality Study (SCAQS). The
secondary organic aerosol material is predicted to condense almost
exclusively on the submicron aerosol in agreement with the
available measurements, and its size distribution for Claremont,
CA, is predicted to be unimodal with a mass mean diameter of
roughly 0.2 mum. The distributions of the various secondary organic
aerosol species are predicted to be essentially the same. The
secondary organic aerosol (SOA) size distribution is found to
depend crucially on the mass and size distribution of primary
aerosol on which the secondary species condense and on the surface
accommodation coefficient of the condensable species. The SOA size
distribution is predicted not to be significantly affected by
diffusional dry deposition, sources and sinks of ammonia, emissions
of VOC, and secondary aerosol yields from precursor hydrocarbons. A
bimodal secondary organic aerosol size distribution is predicted
only if the submicron primary dust particles reside mainly in the
0.5-1.0 mum diameter size range, or if the condensable species have
a strong preference (an accommodation coefficient difference of two
orders of magnitude) for the 0.51.0 mum diameter particles. The
secondary organic aerosol distribution in Claremont is predicted to
shift slightly towards the larger aerosol particles during the
nighttime hours with its mass mean diameter peaking around midnight
at 0.21 mum and having its minimum in early afternoon at 0. 18 mum.
In coastal locations of the Los Angeles basin, secondary organic
material exists in relatively smaller particles (mass mean diameter
0.16 mum) but in far inland locations it condenses on the available
larger particles (mass mean diameter 0.23 mum).
C1 UNIV DELAWARE,DEPT MECH ENGN,NEWARK,DE 19716.
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[8]
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Fourier-transform infrared-analysis of aerosol formed in the photooxidation of
1-octene.
Atmos Environ Pt A-Gen Top 27, 1471-1477 (E. J. Palen,
D. T. Allen, S. N. Pandis, S. Paulson, J. H. Seinfeld, and R. C. Flagan)
1993 (19).
The chemical composition of aerosol generated in the
photooxidation of 1-octene was examined using infrared microscopy
interfaced with a low pressure impactor. The low pressure impactor
segregated the aerosol into eight size fractions and deposited the
aerosol onto ZnSe impaction substrates. The ZnSe surfaces were
transparent in the mid-infrared region and therefore allowed direct
analysis of the aerosol, with no extraction, using infrared
microscopy. Infrared spectra of the size segregated aerosol showed
strong absorbances due to ketone, alcohol, carboxylic acid and
organonitrate functional groups. Absorbance features were
relatively independent of particle size, with the exception of the
carboxylic acid absorbances, which were found only in the largest
aerosol size fractions. Molar loadings for each of the groups were
estimated, based on model compound calibration standards. The molar
loadings indicate that most aerosol species are multifunctional,
with an average of one ketone group per molecule, an alcohol group
in two of every three molecules and an organonitrate group in one
of every three molecules.
C1 UNIV CALIF LOS ANGELES,DEPT CHEM ENGN,LOS ANGELES,CA 90024.
CALTECH,DEPT CHEM ENGN,PASADENA,CA 91125.
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[9]
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The special issue of atmospheric-environment on arctic air, snow, and ice
chemistry - introduction.
Atmos Environ Pt A-Gen Top 27, 2695-2699 (C. I. Davidson
and R. C. Schnell) 1993 (8).
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[10]
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The dye-3 gas and aerosol sampling program (dgasp) - an overview.
Atmos Environ Pt A-Gen Top 27, 2703-2707 (J. L. Jaffrezo
and C. I. Davidson) 1993 (22).
DGASP was designed as an international effort to study
the processes influencing chemical species that eventually reach
the deep ice in the south of Greenland. These processes include
long-range atmospheric transport, wet and dry deposition to the
snow surface, and changes during aging of the snow. The program
took place during August 1988-July 1989. Experimental work included
sampling of aerosols and gases, collection of fresh and older
surface snow, and sampling of snowpits. The various samples were
analysed for chemical species that are tracers of specific source
categories. Results of the program show that the southern Greenland
Ice Sheet experiences very different airborne concentration
patterns than sea-level arctic sites. Concentrations of SO42-,
trace metals, and other species are episodic and peak in April,
unlike the consistently high concentrations during January-April
seen at lower elevations. Source regions influencing Dye 3 are
variable, and include North America, western Europe, and the Arctic
Basin. The last region is particularly important, as it may contain
relatively high concentrations of chemical constituents from
eastern Europe and western Asia that eventually reach Dye 3. The
seasonal variations in airborne concentrations are generally also
reflected in fresh snow. Similarly, these patterns are seen in
snowpits, although some modifications to the glacial record are
apparent. Other information on the extent of riming, aerosol/gas
partitioning, and aerosol size distributions demonstrate the
complexity of air-snow transfer processes, and illustrate the need
for further research.
C1 CARNEGIE MELLON UNIV,DEPT CIVIL ENGN,PITTSBURGH,PA 15213.
CARNEGIE MELLON UNIV,DEPT ENGN & PUBL POLICY,PITTSBURGH,PA 15213.
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[11]
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Chemical-constituents in the air and snow at dye-3, greenland .1.
seasonal-variations.
Atmos Environ Pt A-Gen Top 27, 2709-2722 (C. I.
Davidson, J. L. Jaffrezo, B. W. Mosher, J. E. Dibb, R. D. Borys, B. A.
Bodhaine, R. A. Rasmussen, C. F. Boutron, U. Gorlach, H. Cachier, J. Ducret,
J. L. Colin, N. Z. Heidam, K. Kemp, and R. Hillamo) 1993 (35).
Chemical constituent concentrations in air and snow
from the Dye 3 Gas and Aerosol Sampling Program show distinct
seasonal patterns. These patterns are different from those observed
at sea-level sites throughout the Arctic. Airborne SO42and
several trace metals of crustal and anthropogenic origin show
strong peaks in the spring, mostly in April, Some species also have
secondary maxima in the fall. The spring peaks are attributed to
transport over the Pole from Eurasian sources, as well as transport
from eastern North America and western Europe. The fall peaks are
attributed primarily to transport from North America, and less
frequent transport from Europe. Airborne Be-7 and Pb-210 show
strong peaks in both spring and fall, suggesting that vertical
atmospheric mixing is favored during these two seasons. Several
other airborne constituents peak at other times. For example, Na
peaks in winter due to transport of seaspray from storms in
ice-free oceanic areas, while MSA peaks in summer due to biogenic
production in the oceans nearby. Many trace gases such as freons
and other chlorine-containing species show roughly uniform
concentrations throughout the year. CO and CH4 show weak peaks in
February-March. Concentrations of chemical constituents in fresh
snow at Dye 3 also show distinct seasonal patterns. SO42- and
several trace metals show springtime maxima, consistent with the
aerosol data. Na shows a winter maximum and MSA shows a summer
maximum in the snow, also consistent with the aerosols. Be-7 and
Pb-210 in the snow do not show any strong variation with season.
Similarly, soot and total carbon in snow do not show strong
variation. When used with dry deposition models, these air and snow
concentration data suggest that dry deposition of submicron aerosol
species has relatively minor influence on constituent levels in the
snowpack at Dye 3 compared to wet deposition inputs(including
scavenging by fog); crustal aerosol, on the other hand, may have a
more significant input by dry deposition. Overall, the results
suggest that gross seasonal patterns of some aerosol species are
constistent in the air and in fresh snow, although individual
episodes in the air are not always reflected in the snow. The
differences in data reported here compared with data sets for
sea-level arctic sites demonstrate the need for sampling programs
on the Ice Sheet in order to properly interpret Greenland glacial
record data.
C1 CNRS,GLACIOL & GEOPHYS ENVIRONNEMENT LAB,F-38402 ST MARTIN
DHERES,FRANCE. UNIV NEW HAMPSHIRE,INST STUDY EARTH OCEANS &
SPACE,DURHAM,NH 03824. DESERT RES INST,CTR ATMOSPHER SCI,RENO,NV
89506.
NOAA,CMDL,BOULDER,CO 80303.
OREGON GRAD INST SCI & TECHNOL,BEAVERTON,OR 97006.
CEA,CNRS,CTR FAIBLES RADIOACT,F-91198 GIF SUR YVETTE,FRANCE. UNIV
PARIS 07,PHYSICOCHIM ATMOSPHERE LAB,F-75251 PARIS,FRANCE. NATL INST
ENVIRONM RES,DK-4000 ROSKILDE,DENMARK.
FINNISH METEOROL INST,SF-00810 HELSINKI,FINLAND.
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[12]
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Chemical-constituents in the air and snow at dye-3, greenland .2. analysis of
episodes in april 1989.
Atmos Environ Pt A-Gen Top 27, 2723-2737 (C. I.
Davidson, J. L. Jaffrezo, B. W. Mosher, J. E. Dibb, R. D. Borys, B. A.
Bodhaine, R. A. Rasmussen, C. F. Boutron, F. M. Ducroz, M. Cachier,
J. Ducret, J. L. Colin, N. Z. Heidam, K. Kemp, and R. Hillamo) 1993
(24).
Detailed examination of a two-week period in April
1989 during the Dye 3 Gas and Aerosol Sampling Program shows that
episodes of relatively high concentration of certain chemical
constituents occur at this time of year. Airborne concentrations of
crustal metals such as Al and Ca can exceed 100 ng m(-3), while
concentrations of SO42can exceed 1000 ng m(-3). Elevated
concentrations of MSA, Be-7 and Pb-210 are also noted.
Consideration of synoptic maps and backward air mass trajectories
suggests that the episodes are due to transport from a variety of
source regions, including Eurasia (transport over the Pole), North
America and western Europe. In addition to elevated airborne
concentrations, levels of these constituents in surface snow are
high during April. However, it is difficult to develop quantitative
relationships between concentrations in air and in snow due to the
difficulty in measuring airborne concentrations at cloud-level;
variations in scavenging by clouds may also be significant. It is
concluded that the springtime maxima in airborne concentrations
resulting from long-range transport from a variety of source
regions are responsible for strong identifiable signals in ice
cores and snowpits from this region.
C1 CNRS,GLACIOL & GEOPHYS ENVIRONNEMENT LAB,F-38402 ST MARTIN
DHERES,FRANCE. UNIV NEW HAMPSHIRE,INST STUDY EARTH OCEANS &
SPACE,DURHAM,NH 03824. DESERT RES INST,CTR ATMOSPHER SCI,RENO,NV
89506.
NOAA,CMDA,BOULDER,CO 80303.
OREGON GRAD INST SCI & TECHNOL,BEAVERTON,OR 97006.
CEA,CNRS,CTR FAIBLES RADIOACT,F-91198 GIF SUR YVETTE,FRANCE. UNIV
PARIS 07,PHYSICOCHIM ATMOSPHERE LAB,F-75251 PARIS,FRANCE. NATL INST
ENVIRONM RES,DK-4000 ROSKILDE,DENMARK.
FINNISH METEOROL INST,SF-00810 HELSINKI,FINLAND.
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[13]
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Trajectory analysis of source regions influencing the south greenland ice-sheet
during the dye-3 gas and aerosol sampling program.
Atmos Environ Pt A-Gen Top 27, 2739-2749 (C. I.
Davidson, J. L. Jaffrezo, M. J. Small, P. W. Summers, M. P. Olson, and R. D.
Borys) 1993 (29).
Backward air mass trajectories for Dye 3, Greenland
(elevation 2.5 km) show source regions that vary with season: the
direction of greatest transport distance is from the southwest in
fall, west in winter, and northwest in spring; the trajectories in
summer do not show a strong preferred direction. Based on 5 d
transit times, the trajectories in fall suggest the importance of
North America as a potential source region, with occasional
trajectories from western Europe, The trajectories in spring,
especially in April, suggest Eurasia (transport over the Pole),
eastern North America, and western Europe as potential source
regions. Less transport of chemical constituents to Dye 3 is
expected in summer when transport distances are shorter. Although
some long-range transport to Greenland occurs in winter, the
stability of the atmosphere over the ice sheet at this time of year
is likely to limit the delivery of chemical constituents to the
surface. Sources outside of these regions can also influence Dye 3
if transit times longer than 5 d are considered. These results are
in contrast to trajectories reported by others for sea-level arctic
locations such as Barrow, Alaska and Mould Bay, Canada, where
transport over the Pole from Eurasia is responsible for high
chemical species concentrations over much of the winter and early
spring. Overall, the trajectories are consistent with aerosol
chemical data for this time period at Dye 3 reported by several
investigators, showing peak concentrations in spring and fall.
C1 CNRS,GLACIOL & GEOPHYS ENVIRONNEMENT LAB,F-38402 ST MARTIN
DHERES,FRANCE. ATMOSPHER ENVIRONM SERV,DOWNSVIEW M3H 5T4,ON,CANADA.
UNIV NEVADA,DESERT RES INST,CTR ATMOSPHER SCI,RENO,NV 89506.
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[14]
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Size variations in heavy-metal concentrations in fresh greenland snow from
january to august 1989.
Atmos Environ Pt A-Gen Top 27, 2773-2779 (C. F. Boutron,
F. M. Ducroz, U. Gorlach, J. L. Jaffrezo, C. I. Davidson, and M. A. Bolshov)
1993 (16).
Concentrations of lead, cadmium, copper and zinc have
been measured in a variety of samples of fresh or slightly aged
snow collected at Dye 3, south Greenland, on a precipitation event
basis from January to August 1989. Measured concentrations are
found to be very variable from one snowfall to another, with high
concentration peaks occurring in April and June. The four metals
are shown to be mainly derived from anthropogenic sources, with the
exception of Cu and Zn for some of the samples. The data obtained
for several snow events are further discussed using 5 days backward
air mass trajectories together with data for various other chemical
species.
C1 UNIV GRENOBLE 1,UFR MECAN,F-38041 GRENOBLE,FRANCE. CARNEGIE
MELLON UNIV,DEPT CIVIL ENGN,PITTSBURGH,PA 15213. RUSSIAN ACAD
SCI,INST SPECT,TROITSK 142092,RUSSIA.
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[15]
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Distributions of atmospheric trace-elements at dye-3, greenland .1.
distribution characteristics and dry deposition velocities.
Atmos Environ Pt A-Gen Top 27, 2787-2802 (R. E. Hillamo,
V. M. Kerminen, W. Maenhaut, J. L. Jaffrezo, S. Balachandran, and C. I.
Davidson) 1993 (41).
Cascade impactor samples were collected at Dye 3 on
the south-central Greenland Ice Sheet during March 1989. The
impactor was calibrated in the laboratory, and the resulting
collection efficiency curves were used to derive the impactor
response for use in a data inversion procedure. The impactor
samples were chemically analysed by proton-induced X-ray emission
(PIXE), and the chemical concentration data were used with the
inversion procedure to generate smooth size distributions for 15
elements. Results show three distinct size distribution categories.
The first category includes elements that mainly originate from gas
to particle conversion, with a substantial fraction-from
anthropogenic combustion (S, Pb, Zn, Br and Ni). These elements
exhibit a unimodal size distribution with geometric mean
aerodynamic diameter close to 0.6 mu m, although S and in shaw a
weak second mode centered at about 2 mu m. Elements in the second
category (Ti, Si, Fe, Mn, Ca, K) exhibit bimodal size
distributions, with geometric mean diameters for the two modes of
0.6 and 2 mu m, respectively. These elements result from a variety
of sources, including crustal erosion as well as combustion from
natural and anthropopenic sources. For elements in the third
category (Al, Cl, Na, Mg), most of the mass occurs in particle
sizes above 1 mu m. Their size distribution is generally unimodal,
with the geometric mean aerodynamic diameter around 2 mu m. These
elements are most likely to be of crustal and/or marine origin. The
best-fit size distributions were used with curves of dry deposition
velocity vs aerodynamic particle diameter to estimate the overall
dry deposition velocity expected from the entire distribution. The
deposition velocities for S, Pb, Zn, Br and Ni are all very low,
with values less than about 0.02 cm s(-1) if hygroscopic growth in
the humid layer is neglected. For those other elements, deposition
velocities are in the range 0.2-0.7 cm s(-1). For those
distributions that are bimodal, the upper mode generally dominates
deposition even when most of he airborne mass is associated with
the lower modes, as in the case of S and Zn.
C1 INST NUCL WETENSCHAPPEN,B-9000 GHENT,BELGIUM.
CARNEGIE MELLON UNIV,DEPT CIVIL ENGN,PITTSBURGH,PA 15213.
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[16]
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Size distributions of atmospheric trace-elements at dye-3, greenland .2.
sources and transport.
Atmos Environ Pt A-Gen Top 27, 2803-2814 (J. L.
Jaffrezo, R. E. Hillamo, C. I. Davidson, and W. Maenhaut) 1993 (10).
Airborne concentrations and size distributions of 15
elements over the Greenland Ice Sheet have been measured during a
one-month period in March 1989. The concentrations are relatively
uniform, varying by less than a factor of three for virtually all
of the elements. Notable exceptions are Na and Cl which vary by
more than an order of magnitude; these differences can probably be
accounted for by the link with transport from the oceans
surrounding Greenland, although a significant fraction of the Na is
of crustal origin in some samples. The size distributions show
strong peaks in the accumulation mode(0.4-1.0 mu m) or the coarse
particle mode (1.0-2.5 mu m); some species show bimodal
distributions with the presence of both modes. The aerosol
chemistry and size distribution data are consistent with back
trajectories and local weather conditions. For example, relatively
high concentrations of Pb, Zn, Ni, Fe, and Mn in the accumulation
mode during one of the runs are associated with trajectories from
industrial regions of the Soviet Arctic. The elements Si, Al, Fe,
K, Ca, Mn, and Ti in the coarse mode are believed to be dominated
by crustal sources. However, some runs show the presence of an
accumulation mode for most of these elements (with the exception of
Al), suggestive of combustion sources. Overall, the results show
that use of an impactor with several submicron size cuts combined
with a suitable data inversion program can provide insights into
the sources and transport of aerosols at remote locations such as
the Greenland Ice Sheet.
C1 CARNEGIE MELLON UNIV,DEPT CIVIL ENGN,PITTSBURGH,PA 15213.
FINNISH METEOROL INST,DEPT AIR QUAL,SF-00810 HELSINKI,FINLAND. INST
NUCL WETTSCHAPPEN,B-9000 GHENT,BELGIUM.
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[17]
|
Assessment of ice particle growth-processes at dye-3, greenland.
Atmos Environ Pt A-Gen Top 27, 2815-2822 (R. D. Borys,
D. Delvecchio, J. L. Jaffrezo, C. I. Davidson, and D. L. Mitchell) 1993
(7).
As part of the DGASP program on the Greenland Ice
Sheet, an investigation was conducted into the nature of ice
particle formation processes that result in the formation of snow.
Ice particle habits were determined using Formvar replicas of
falling snow crystals. From these measurements an assessment of the
primary growth process and altitude of formation was made. Results
indicate that the scavenging of cloud water by falling ice
particles, growth by accretion or riming, rarely occurs. However,
when riming does occur, it is usually associated with warmer air
masses from the south. The occurrence of riming was also observed
to be dependent on the season, with a greater frequency occuring
during warmer months. It was estimated that ice particle riming
contributes less than 5% of the average annual water mass, but up
to 30% of the deposition of some chemical species, deposited to
the Greenland Ice Sheet at Dye 3. Ice particle habits indicate that
they originate at higher altitudes above the ice cap in summer than
in winter. Variations in the magnitude of ice particle riming, the
elevation of origin of ice particles, the meteorology and the
season of the year are all essential when interpreting snow
chemistry and comparing snow and aerosol chemistry at Dye 3. C1
CARNEGIE MELLON UNIV,DEPT CIVIL ENGN,PITTSBURGH,PA 15213.
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[18]
|
Seasonal and geographic variations of methanesulfonic-acid in the arctic
troposphere.
Atmos Environ Pt A-Gen Top 27, 3011-3024 (S. M. Li,
L. A. Barrie, R. W. Talbot, R. C. Harriss, C. I. Davidson, and J. L.
Jaffrezo) 1993 (28).
Measurements in the Arctic troposphere over several
years show that MSA concentrations in the atmospheric boundary
layer, 0.08-6.1 parts per trillion (ppt, molar mixing ratio), are
lower than those over mid-latitude oceans. The seasonal cycle of
MSA at Alert, Canada (82.5 degrees N, 62.3 degrees W), has two
peaks of 6 ppt in March-April and July-August and minima of 0.3 ppt
for the rest of the year. At Dye 3 (65 degrees N, 44 degrees W) on
the Greenland Ice Sheet, a similar seasonal MSA cycle is observed
although the concentrations are much lower with a maximum of 1 ppt.
Around Barrow, Alaska (71.3 degrees N, 156.8 degrees W), MSA is
between 1.0 and 25 ppt in July, higher than 1.5+/-1.0 ppt in
March-April. The mid-tropospheric MSA level of 0.6-1 ppt in the
summer Arctic is much lower than about 6 ppt in the boundary layer.
Al Alert, the ratio of MSA to non-sea-salt (nss) SO42ranges from
0.02 to 1.13 and is about 10 times higher in summer than in spring.
The summer ratios are higher than found over mid-latitude regions
and, when combined with reported sulfur isotope compositions from
the Arctic, suggest that on average a significant fraction (about
16-23%) of Arctic summer boundary layer sulfur is marine biogenic.
The measurements show that the summer Arctic boundary layer has a
significantly higher MSA/nss-SO42- ratio than aloft.
C1 UNIV NEW HAMPSHIRE,COMPLEX SYST RES CTR,INST STUDY EARTH OCEANS
& SPACE,DURHAM,NH 03824. CARNEGIE MELLON UNIV,DEPT CIVIL
ENGN,PITTSBURGH,PA 15213.
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[19]
|
Heterogeneous sulfate production in an urban fog.
Atmos Environ Pt A-Gen Top 26, 2509-2522 (S. N. Pandis,
J. H. Seinfeld, and C. Pilinis) 1992 (34).
Heterogeneous production of sulfate in an urban fog
has been investigated using data collected during the SCAQS program
in the Los Angeles area, for the period of 10-11 December 1987. Fog
was observed during the night of 10 December and the early morning
hours of 11 December near the coast of southern California.
Measurements at several sites (Hawthorne, downtown Los Angeles,
etc.) indicated a significant increase in sulfate concentration
during the afternoon of 11 December. Trajectory analysis suggests
that these high sulfate concentrations were associated with the
arrival at the receptor sites of air parcels that passed through
the fog layer the previous night. To quantify the contribution of
aqueous-phase processes to the above sulfate levels, a detailed
trajectory model was employed to simulate the gas-phase processes
during that episode. The model, using the available information
about SO2 and sulfate emissions, initial conditions and
meteorology, successfully explained the sulfate levels in air
parcels that did not pass through the fog layer, but underestimated
by as much as 2.5 the sulfate levels of the trajectories through
the fog. Sensitivity/uncertainty analysis indicated that the
presence of sulfate beyond that attributable to gas-phase chemistry
(around 10-mu-g m-3) cannot be attributed to uncertainties in the
model parameters (e.g. initial conditions, emissions, mixing
heights, deposition velocities). The episode was then simulated
using a full psand aqueous-phase chemistry model and the analysis
indicated that heterogeneous sulfate formation in fog droplets
under the conditions of the episode can indeed explain the observed
sulfate.
C1 CALTECH,ENVIRONM QUAL LAB,PASADENA,CA 91125.
AERO VIRONMENT INC,MONROVIA,CA 91016.
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[20]
|
Secondary organic aerosol formation and transport.
Atmos Environ Pt A-Gen Top 26, 2269-2282 (S. N. Pandis,
R. A. Harley, G. R. Cass, and J. H. Seinfeld) 1992 (205).
A Lagrangian trajectory model simulating the
formation, transport and deposition of secondary organic aerosol is
developed and applied to the Los Angeles area, for the air
pollution episode of 27-28 August 1987. The predicted secondary
organic aerosol on 28 August 1987 represents 15-22% of the
measured particulate organic carbon at inland locations in the base
case simulations, and 5-8% of that at coastal locations. A
maximum secondary organic aerosol concentration of 6.8-mu-g m-3 is
predicted for Claremont, CA, during this episode. On a daily
average basis at Claremont about 46% of this secondary organic
aerosol is predicted to be a result of the oxidation of non-toluene
aromatics (xylenes, alkylbenzenes, etc.), 19% from toluene, 16%
from biogenic hydrocarbons (alpha-pinene, beta-pinene, etc.), 15%
from alkanes and 4% from alkenes. The major uncertainties in
predicting secondary organic aerosol concentrations are the
reactive organic gas emissions, the aerosol yields and the
partitioning of the condensable gases between the two phases.
Doubling the reactive organic gas (ROG) emissions results in an
increase of the secondary organic aerosol predicted at Claremont by
a factor of 2.3. Predicted secondary organic aerosol levels are
less sensitive to changes in secondary organic aerosol deposition
and NOx emissions than to ROG emissions.
C1 CALTECH,DEPT ENVIRONM ENGN SCI,PASADENA,CA 91125.
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[21]
|
Should bulk cloudwater or fogwater samples obey henry law - reply.
J. Geophys. Res.-Atmos. 97, 6079-6081 (S. N. Pandis and
J. H. Seinfeld) 1992 (3).
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[22]
|
Fourier-transform infrared-analysis of aerosol formed in the photooxidation of
isoprene and beta-pinene.
Atmos Environ Pt A-Gen Top 26, 1239-1251 (E. J. Palen,
D. T. Allen, S. N. Pandis, S. E. Paulson, J. H. Seinfeld, and R. C. Flagan)
1992 (51).
The chemical composition of smog-chamber aerosol
generated during the photo-oxidation of isoprene and beta-pinene
was probed using infrared (i.r.) microscopy interfaced with a low
pressure impactor. The low-pressure impactor employed ZnSe
impaction surfaces which allowed direct analysis, with no
extraction, using i.r. microscopy. The low detection limits of this
technique, coupled with direct sample analysis, permitted the
chemical analysis of aerosol generated at low to moderate
hydrocarbon and ozone loadings. The quantitative analysis of the
i.r. spectra is limited, in part, by the absence of calibration
standards, however, it is clear that the biogenic aerosols
generated in this work were liquid mixtures containing ketone,
aldehyde, alcohol and organonitrate functional groups. Molar
loadings of each of these functional groups were estimated for nine
smog-chamber experiments. For aerosol formed in isoprene
photo-oxidation, aldehyde and ketone groups dominated (1.8 groups
per average molecule) while for aerosol formed in beta-pinene
photo-oxidation, alcohols and ketones dominated (a combined 2.7
groups per average molecule).
C1 UNIV CALIF LOS ANGELES,DEPT CHEM ENGN,LOS ANGELES,CA 90024.
CALTECH,DEPT CHEM ENGN,PASADENA,CA 91125.
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[23]
|
Resuspension of particulate chemical-species at forested sites.
Environ. Sci. Technol. 26, 2428-2435 (Y. L. Wu, C. I.
Davidson, S. E. Lindberg, and A. G. Russell) 1992 (5).
The resuspension rates of particulate chemical species
have been estimated using aerodynamic surrogate surfaces
(symmetrical airfoils) at a mixed deciduous forest site, and also
using throughfall sampling at a loblolly pine forest site. The
airfoils were placed above, within, and below the crown of the
deciduous canopy to determine the vertical variation of deposition
and resuspension. The resuspension rates of SO42-, C2O42-, and Ca
from the airfoils are estimated to be on the order of 10(-6)-10(-5)
s-1. The resuspension rates within the crown are only slightly less
than those above the canopy. This is in contrast to the mean wind
speed, which is much smaller within the crown than above the
canopy. The smaller differences in the resuspension rate compared
with differences in mean wind speed may be due to the effects of
wind gusts which penetrate deep within the canopy. Based on the
throughfall data, the resuspension rates for Ca, Mg, and Na are
also in the range 10(-6)-10(-5) s-1. Overall, these results suggest
that resuspension may need to be taken into account when particle
deposition to vegetation is estimated.
C1 CARNEGIE MELLON UNIV,DEPT MECH ENGN,PITTSBURGH,PA 15213.
CARNEGIE MELLON UNIV,DEPT CIVIL ENGN,PITTSBURGH,PA 15213. OAK RIDGE
NATL LAB,OAK RIDGE,TN 37830.
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[24]
|
A stochastic-model for particle deposition and bounceoff.
Aerosol Sci. Technol. 17, 231-244 (Y. L. Wu, C. I.
Davidson, and A. G. Russell) 1992 (14).
A new model for particle deposition and bounceoff that
combines current knowledge of turbulent bursts with the stochastic
properties of turbulent fluctuations is presented. The model
predictions for deposition velocities agree with experimental
results in the literature for dimensionless particle relaxation
time tau(p)+ > 2. For tau(p)+ > 10, most of the particles delivered
to the edge of the viscous sublayer are able to deposit onto the
surface due to their inertia; the deposition velocity approaches an
asymptotic value because the process becomes limited by the rate or
turbulent delivery to the viscous sublayer. Because of the
penetration of turbulent fluctuations into the viscous sublayer,
the minimum values of vertical velocities needed for particles to
deposit onto the surface are smaller than those predicted by the
free flight model. Most of the deposition occurs from those
turbulent fluctuations at the upper tail of the distribution of the
vertical component of air velocity.
In addition to the deposition velocity the model is able to provide
the distribution of particle velocities on reaching the surface
which is used to compute the fraction of particle bounceoff. The
model predictions for the fractions of rebound agree reasonably
with the measured results from a wind tunnel experiment for tau(p)+
> 2. However, both the deposition velocity and the fraction of
rebound are underestimated by the model for tau(p)+ < 2. Other
mechanisms such as Brownian diffusion must be included in further
revisions to this model in order to obtain satisfactory predictions
for smaller values of tau(p)+.
C1 CARNEGIE MELLON UNIV,DEPT CIVIL ENGN,PITTSBURGH,PA 15213.
CARNEGIE MELLON UNIV,DEPT MECH ENGN,PITTSBURGH,PA 15213.
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[25]
|
Controlled wind-tunnel experiments for particle bounceoff and resuspension.
Aerosol Sci. Technol. 17, 245-262 (Y. L. Wu, C. I.
Davidson, and A. G. Russell) 1992 (14).
The dynamics of particle rebound and resuspension were
examined by using uranine particles, polymer microspheres, spores,
and pollen in wind tunnel experiments. Particle diameters were 5-42
mum. Results show that both the fraction of rebound and the
resuspension rate are strongly dependent on the free stream
velocity, particle size, and relative humidity. The effects of
relative humidity are more significant at lower windspeeds; a
greater relative humidity appears to change the shape of the
distribution of adhesion force. mainly affecting the lower range
but not greatly affecting the upper end of the distribution.
Resuspension rates decrease with time, essentially defining two
regimes. The first regime lasts for < 1 min; after this time, the
most easily resuspended particles have been removed, leaving only
particles with much smaller resuspension rates for the second
regime. At a windspeed of 6 m/s, the upper 20% of the distribution
of turbulent fluctuations is responsible for approximately 65% of
the particle resuspension. Once resuspended, the particles have
trajectories which depend on characteristics of the turbulent
airflow and not on the initial velocity of release from the
surface. Overall, the data show th at resuspension is more
sensitive to the type or particle than to the type of surface;
particle shape and composition may be more important than particle
size.
C1 CARNEGIE MELLON UNIV,DEPT CIVIL ENGN,PITTSBURGH,PA 15213.
CARNEGIE MELLON UNIV,DEPT MECH ENGN,PITTSBURGH,PA 15213.
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[26]
|
Stochastic simulation of diurnal-variations of co, no and no2 concentrations in
occupied residences.
Atmos Environ Pt B-Urban Atm 26, 369-377 (J. E.
Borrazzo, C. I. Davidson, and M. J. Small) 1992 (1).
A stochastic approach to the problem of incorporating
variable emission events in indoor air quality models is proposed.
A nonstationary Poisson process is used to account for the
occurrence of range-top burner use. The combination of this
emission event sequence with a simple one-compartment mass-balance
model results in output that qualitatively agrees with measured
concentrations in two occupied townhouses. Improved monitoring of
stove usage times, gas flow rates and emission factors under field
conditions would allow more effective estimation of model input
parameters and more accurate prediction of concentration
distributions.
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[27]
|
Dry deposition of atmospheric contaminants - the relative importance of
aerodynamic, boundary-layer, and surface resistances.
Aerosol Sci. Technol. 16, 65-81 (Y. L. Wu, C. I.
Davidson, D. A. Dolske, and S. I. Sherwood) 1992 (32).
Measurements of dry deposition were conducted to
potted plants at Claremont, CA, during the Southern California Air
Quality Study and to patches on an equestrian statue at Gettysburg
National Military Park, PA. Simultaneous dry deposition
measurements were also conducted on aerodynamically designed
surrogate surfaces (symmetric airfoils) with predictable boundary
layer characteristics at both locations. Species of interest
include gaseous SO2 and particulate SO42-, NO3-, Ca, and Pb. The
importance of each transport step in the deposition process was
evaluated by combining the data from several types of surfaces with
different surface characteristics. The significance of particle
resuspension was determined by simultaneous sampling with different
exposure times. The results suggest that the relative importance
of aerodynamic, boundary layer, and surface resistances can vary
greatly, depending on the depositing chemical species and the
surface characteristics. Of particular interest is the highly
variable surface resistance which is often the rate-limiting step
in the overall process. Rates of resuspension for several surfaces
including natural vegetation are in the range of 10(-6) to 10(-5)
sec-1 for the aerosol chemical species considered. This implies
that net dry deposition rates depend on the exposure times, which
are not often considered in most ambient dry deposition studies.
C1 ILLINOIS DEPT ENERGY & NAT RESOURCES,ATMOSPHER CHEM SECT,DIV
STATE WATER SURVEY,CHAMPAIGN,IL 61820. US DEPT INTERIOR,DIV
PRESERVAT ASSISTANCE,NATL PK SERV,WASHINGTON,DC 20240.
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[28]
|
Inversion of aerosol data from the epiphaniometer.
J. Aerosol. Sci. 22, 417-428 (S. N. Pandis,
U. Baltensperger, J. K. Wolfenbarger, and J. H. Seinfeld) 1991 (29).
The epiphaniometer is a new instrument for continuous
monitoring of the Fuchs surface of aerosol particles using the
attachment of neutral radioactive Pb-211 atoms to the particles.
Since the Pb-211 atoms have a half-life of 36.1 min, the ability of
the epiphaniometer to detect short-term fluctuations in the Fuchs
surface of the aerosol is limited. To overcome this drawback a
general algorithm developed for the inversion of size distribution
data from conventional aerosol instruments is adapted for the
inversion of data from the epiphaniometer. This algorithm allows
resolution of dramatic changes in the aerosol Fuchs surface
occurring over a time scale of minutes. The method is applied to
data collected during outdoor smog chamber experiments, with
changes in aerosol concentration of several orders of magnitude
occurring within a time period of 5 min. The inverted
epiphaniometer data are in agreement with the corresponding data
from a Scanning Electrical Mobility Spectrometer (SEMS) and an
Optical Particle Counter.
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[29]
|
Should bulk cloudwater or fogwater samples obey henrys law.
J. Geophys. Res.-Atmos. 96, 10791-10798 (S. N. Pandis
and J. H. Seinfeld) 1991 (37).
In this work we prove that mixing of droplets with
different pH that are individually in Henry's law equilibrium with
the surrounding atmosphere always results in a bulk mixture that is
supersaturated with weak acids like S(IV) and HCOOH and bases like
NH3 with respect to the original atmosphere. The degree of
supersaturation of the bulk liquid water sample for a particular
species depends on its dissociation constant, on the initial pH of
the bulk droplet mixture, and on the distribution of the pH and of
the liquid water over the droplet spectrum. High supersaturations
result only when the pH of the bulk droplet mixture exceeds the
pK-alpha of the species, in which pH range large pH differences
among droplets of different sizes lead to large deviations from
Henry's law for the bulk mixture. The deviation is shown to depend
on the ratio of the arithmetic mean to the harmonic mean of the
hydrogen ion concentrations of the droplets with the liquid water
content used as weighting factor in the calculation of the means.
The theory developed can explain observed discrepancies from
Henry's law in atmospheric samples and also other observed
phenomena like the reported increase of pH values of bulk aqueous
samples during storage. C1 CALTECH,ENVIRONM QUAL LAB,PASADENA,CA
91125.
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[30]
|
Aerosol formation in the photooxidation of isoprene and beta-pinene.
Atmos Environ Pt A-Gen Top 25, 997-1008 (S. N. Pandis,
S. E. Paulson, J. H. Seinfeld, and R. C. Flagan) 1991 (129).
Isoprene and beta-pinene, at concentration levels
ranging from a few ppb to a few ppm, were reacted photochemically
with NO(x) in the Caltech outdoor smog chamber facility. Aerosol
formation from the isoprene photooxidation is found to be
negligible even under extreme ambient conditions due to the
relatively high vapor pressure of its products. Aerosol carbon
yield from the beta-pinene photooxidation is as high as 8% and
depends strongly on the initial HC/NO(x) ratio. The average vapor
pressure of the beta-pinene aerosol is estimated to be 37 +/- 24
ppt at 31-degrees-C. Monoterpene photooxidation can be a
significant source of secondary aerosol in rural environments and
in urban areas with extended natural vegetation.
C1 CALTECH,DEPT ENVIRONM ENGN SCI,PASADENA,CA 91125.
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[31]
|
Nonmethane hydrocarbon chemistry in the remote marine boundary-layer.
J. Geophys. Res.-Atmos. 95, 18387-18411 (N. M. Donahue
and R. G. Prinn) 1990 (63).
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[32]
|
Characterization of photochemical aerosols from biogenic hydrocarbons.
J. Aerosol. Sci. 21, S245-S248 (S. E. Paulson, S. N.
Pandis, U. Baltensperger, J. H. Seinfeld, R. C. Flagan, E. J. Palen, D. T.
Allen, C. Schaffner, W. Giger, and A. Portmann) 1990 (10).
An extensive set of outdoor smog chamber experiments
were carried out to study aerosol formation by two representative
biogenic hydrocarbons; isoprene and beta-pinene. The hydrocarbons,
at concentrations ranging from a few ppb to a few ppm, were
photooxidized in the presence of NO(x). Isoprene was found to
produce negligible aerosol at ambient conditions, whereas
beta-pinene aerosol carbon yields were as high as 8%, depending
strongly on the hydrocarbon to NO(x) ratio. Aerosol samples
subjected to infrared absorption spectroscopy revealed that the
dominant aerosol products for both isoprene and beta-pinene are
organic nitrates, organic acids, as well as other carbonyls and
hydroxy compounds. GCMS of the neutral fraction of the beta-pinene
aerosol revealed nopinone and several other compounds with
molecular weights ranging from 138-200 amu, indicating mainly mono-
and dioxygenated products. The average vapor pressure of the
beta-pinene aerosol was estimated to be 37 +/- 24 ppt at
31-degrees-C. Scanning electron micrographs showed that the
particles consist of both liquid droplets and agglomerates of small
(40-60 nm) solid particles. C1 CALTECH,DEPT ENVIRONM
ENGN,PASADENA,CA 91125.
UNIV CALIF LOS ANGELES,DEPT CHEM ENGN,LOS ANGELES,CA 90024. INST
WATER RESOURCES & WATER POLLUT CONTROL EAWAG,CH-8600
DUBENDORF,SWITZERLAND. UNIV ZURICH,INST INORGAN CHEM,CH-8057
ZURICH,SWITZERLAND.
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[33]
|
The smog-fog-smog cycle and acid deposition.
J. Geophys. Res.-Atmos. 95, 18489-18500 (S. N. Pandis,
J. H. Seinfeld, and C. Pilinis) 1990 (21).
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[34]
|
On the interaction between equilibration processes and wet or dry deposition.
Atmos Environ Pt A-Gen Top 24, 2313-2327 (S. N. Pandis
and J. H. Seinfeld) 1990 (8).
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[35]
|
Chemical-composition differences in fog and cloud droplets of different sizes.
Atmos Environ Pt A-Gen Top 24, 1957-1969 (S. N. Pandis,
J. H. Seinfeld, and C. Pilinis) 1990 (63).
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