10 research outputs found
Modeling Secondary Organic Aerosol Production from Photosensitized Humic-like Substances (HULIS)
Humic-like
substances (HULIS) are ubiquitous in atmospheric aerosols.
Despite experimental evidence that HULIS can catalyze secondary organic
aerosol (SOA) formation through photosensitizer chemistry, the potential
contribution of this pathway to ambient SOA has not been quantified.
In this study, GAMMA, a photochemical box model, was used to analyze
the experimental data of Monge et al. (Proc. Natl. Acad. Sci. U. S. A. 2012, 109, 6840ā6844) to quantify the kinetics of uptake of limonene by particles
containing humic acid, a laboratory proxy for HULIS. The results indicate
that limonene is taken up by irradiated particles containing humic
acid efficiently, with a reactive uptake coefficient of 1.6 Ć
10<sup>ā4</sup>. Consequently, simulations of limoneneāHULIS
photosensitizer chemistry under ambient conditions, simultaneously
with other aqueous SOA formation processes, show that this pathway
could contribute up to 65% of the total aqueous SOA at pH 4. The potential
importance of this pathway warrants further laboratory studies and
representation of this SOA source in atmospheric models
Photochemical Aging of Light-Absorbing Secondary Organic Aerosol Material
Dark reactions of methylglyoxal with
NH<sub>4</sub><sup>+</sup> in aqueous aerosols yield light-absorbing
and surface-active products
that can influence the physical properties of the particles. Little
is known about how the product mixture and its optical properties
will change due to photolysis as well as oxidative aging by O<sub>3</sub> and OH in the atmosphere. Here, we report the results of
kinetics and product studies of the photochemical aging of aerosols
formed by atomizing aqueous solutions of methylglyoxal and ammonium
sulfate. Experiments were performed using aerosol flow tube reactors
coupled with an aerosol chemical ionization mass spectrometer (AerosolāCIMS)
for monitoring gas- and particle-phase compositions. Particles were
also impacted onto quartz windows in order to assess changes in their
UVāvisible absorption upon oxidation. Photooxidation of the
aerosols leads to the formation of small, volatile organic acids including
formic acid, acetic acid, and glyoxylic acid. The atmospheric lifetime
of these species during the daytime is predicted to be on the order
of minutes, with photolysis being an important mechanism of degradation.
The lifetime with respect to O<sub>3</sub> oxidation was observed
to be on the order of hours. O<sub>3</sub> oxidation also leads to
a net increase in light absorption by the particles due to the formation
of additional carbonyl compounds. Our results are consistent with
field observations of high brown carbon absorption in the early morning
Surface Disordering and Film Formation on Ice Induced by Formaldehyde and Acetaldehyde
Small
aldehydes, such as formaldehyde (HCHO) and acetaldehyde (CH<sub>3</sub>CHO), are known to contribute significantly to the OH and
O<sub>3</sub> budgets in polar atmospheres via chemical interaction
with snow and ice surfaces. However, our understanding of how these
small aldehydes interact with ice surfaces is rather limited. In this
work, ellipsometry was used to study the interaction of gas-phase
HCHO and CH<sub>3</sub>CHO with ice under partial pressure and temperature
conditions akin to polar snowpack interstitial space. Both HCHO and
CH<sub>3</sub>CHO were found to induce surface change consistent with
the formation of a disordered interfacial layer (DIL) at temperatures
below which no intrinsic DIL is expected to exist (<i>T</i> < 238 K). For HCHO, induced surface disorder showed both temperature
and partial pressure dependence. For CH<sub>3</sub>CHO, temperature
seemed to be the dominant factor; a DIL surface transition was observed
in the presence of CH<sub>3</sub>CHO at 223 ± 2 K, in agreement
with earlier findings that partitioning behavior of CH<sub>3</sub>CHO is different above and below this transition temperature. Exposure
to HCHO or CH<sub>3</sub>CHO was also observed to cause the formation
of opaque domains on the ice surface, which may correspond to hydrate
formation
Modeling Photosensitized Secondary Organic Aerosol Formation in Laboratory and Ambient Aerosols
Photosensitized reactions involving
imidazole-2-carboxaldehyde
(IC) have been experimentally observed to contribute to secondary
organic aerosol (SOA) growth. However, the extent of photosensitized
reactions in ambient aerosols remains poorly understood and unaccounted
for in atmospheric models. Here we use GAMMA 4.0, a photochemical
box model that couples gas-phase and aqueous-phase aerosol chemistry,
along with recent laboratory measurements of the kinetics of IC photochemistry,
to analyze IC-photosensitized SOA formation in laboratory and ambient
settings. Analysis of the laboratory results of Aregahegn et al. (2013)
suggests that photosensitized production of SOA from limonene, isoprene,
α-pinene, β-pinene, and toluene by <sup>3</sup>IC* occurs
at or near the surface of the aerosol particle. Reactive uptake coefficients
were derived from the experimental data using GAMMA 4.0. Simulations
of aqueous aerosol SOA formation at remote ambient conditions including
IC photosensitizer chemistry indicate less than 0.3% contribution
to SOA growth from direct reactions of <sup>3</sup>IC* with limonene,
isoprene, α-pinene, β-pinene, and toluene, and an enhancement
of less than 0.04% of SOA formation from other precursors due to the
formation of radicals in the bulk aerosol aqueous phase. Other, more
abundant photosensitizer species, such as humic-like substances (HULIS),
may contribute more significantly to aqueous aerosol SOA production
Aerosol Brown Carbon from Dark Reactions of Syringol in Aqueous Aerosol Mimics
We
performed a laboratory investigation of the chemical processing
of syringol, a representative model phenolic compound emitted from
wood burning, in concentrated aqueous salt solutions mimicking tropospheric
aerosol particles. For solutions containing chloride salts, we observed
the formation of light-absorbing organic products (ābrown carbonā),
accompanied by a phase separation, within 10 h under dark conditions.
Products were characterized at the molecular level using ultraperformance
liquid chromatography interfaced to diode array detection and high-resolution
quadrupole time-of-flight mass spectrometry equipped with electrospray
ionization and matrix-assisted laser desorption/ionization interfaced
to high-resolution time-of-flight mass spectrometry. The ultravioletāvisible
spectra, together with high-resolution mass spectra results, suggest
that syringol can be oxidized by dissolved oxygen, and the presence
of Cl<sup>ā</sup> promotes this reaction. Our results provide
new insights into the evolution of aerosol optical properties during
aging, specifically the formation of aerosol brown carbon in biomass-burning
plumes
Simulating Aqueous-Phase Isoprene-Epoxydiol (IEPOX) Secondary Organic Aerosol Production During the 2013 Southern Oxidant and Aerosol Study (SOAS)
The lack of statistically robust
relationships between IEPOX (isoprene
epoxydiol)-derived SOA (IEPOX SOA) and aerosol liquid water and pH
observed during the 2013 Southern Oxidant and Aerosol Study (SOAS)
emphasizes the importance of modeling the whole system to understand
the controlling factors governing IEPOX SOA formation. We present
a mechanistic modeling investigation predicting IEPOX SOA based on
Community Multiscale Air Quality (CMAQ) model algorithms and a recently
introduced photochemical box model, simpleGAMMA. We aim to (1) simulate
IEPOX SOA tracers from the SOAS Look Rock ground site, (2) compare
the two model formulations, (3) determine the limiting factors in
IEPOX SOA formation, and (4) test the impact of a hypothetical sulfate
reduction scenario on IEPOX SOA. The estimated IEPOX SOA mass variability
is in similar agreement (<i>r</i><sup>2</sup> ā¼ 0.6)
with measurements. Correlations of the estimated and measured IEPOX
SOA tracers with observed aerosol surface area (<i>r</i><sup>2</sup> ā¼ 0.5ā0.7), rate of particle-phase reaction
(<i>r</i><sup>2</sup> ā¼ 0.4ā0.7), and sulfate
(<i>r</i><sup>2</sup> ā¼ 0.4ā0.5) suggest an
important role of sulfate in tracer formation via both physical and
chemical mechanisms. A hypothetical 25% reduction of sulfate results
in ā¼70% reduction of IEPOX SOA formation, reaffirming the importance
of aqueous phase chemistry in IEPOX SOA production
Observation of Organic Molecules at the Aerosol Surface
Organic molecules
at the gas-particle interface of atmospheric
aerosols influence the heterogeneous chemistry of the aerosol and
impact climate properties. The ability to probe the molecules at the
aerosol particle surface in situ therefore is important but has been
proven challenging. We report the first successful observations of
molecules at the surface of laboratory-generated aerosols suspended
in air using the surface-sensitive technique second harmonic light
scattering (SHS). As a demonstration, we detect trans-4-[4-(dibutylamino)Āstyryl]-1-methylpyridinium
iodide and determine its population and adsorption free energy at
the surface of submicron aerosol particles. This work illustrates
a new and versatile experimental approach for studying how aerosol
composition may affect the atmospheric properties
Ammonium Addition (and Aerosol pH) Has a Dramatic Impact on the Volatility and Yield of Glyoxal Secondary Organic Aerosol
Glyoxal
is an important precursor to secondary organic aerosol
(SOA) formed through aqueous chemistry in clouds, fogs, and wet aerosols,
yet the gas-particle partitioning of the resulting mixture is not
well understood. This work characterizes the volatility behavior of
the glyoxal precursor/product mix formed after aqueous hydroxyl radical
oxidation and droplet evaporation under cloud-relevant conditions
for 10 min, thus aiding the prediction of SOA via this pathway (SOA<sub>Cld</sub>). This work uses kinetic modeling for droplet composition,
droplet evaporation experiments and temperature-programmed desorption
aerosolāchemical ionization mass spectrometer analysis of gas-particle
partitioning. An effective vapor pressure (<i>p</i>ā²<sub>L,eff</sub>) of ā¼10<sup>ā7</sup> atm and an enthalpy
of vaporization (Ī<i>H</i><sub>vap,eff</sub>) of ā¼70
kJ/mol were estimated for this mixture. These estimates are similar
to those of oxalic acid, which is a major product. Addition of ammonium
until the pH reached 7 (with ammonium hydroxide) reduced the <i>p</i>ā²<sub>L,eff</sub> to <10<sup>ā9</sup> atm
and increased the Ī<i>H</i><sub>vap,eff</sub> to >80
kJ/mol, at least in part via the formation of ammonium oxalate. pH
7 samples behaved like ammonium oxalate, which has a vapor pressure
of ā¼10<sup>ā11</sup> atm. We conclude that ammonium
addition has a large effect on the gas-particle partitioning of the
mixture, substantially enhancing the yield of SOA<sub>Cld</sub> from
glyoxal
Aqueous-Phase Secondary Organic Aerosol and Organosulfate Formation in Atmospheric Aerosols: A Modeling Study
We have examined aqueous-phase secondary organic aerosol
(SOA)
and organosulfate (OS) formation in atmospheric aerosols using a photochemical
box model with coupled gas-phase chemistry and detailed aqueous aerosol
chemistry. SOA formation in deliquesced ammonium sulfate aerosol is
highest under low-NO<i><sub>x</sub></i> conditions, with
acidic aerosol (pH = 1) and low ambient relative humidity (40%). Under
these conditions, with an initial sulfate loading of 4.0 μg
m<sup>ā3</sup>, 0.9 μg m<sup>ā3</sup> SOA is predicted
after 12 h. Low-NO<i><sub>x</sub></i> aqueous-aerosol SOA
(aaSOA) and OS formation is dominated by isoprene-derived epoxydiol
(IEPOX) pathways; 69% or more of aaSOA is composed of IEPOX, 2-methyltetrol,
and 2-methyltetrol sulfate ester. 2-Methyltetrol sulfate ester comprises
>99% of OS mass (66 ng m<sup>ā3</sup> at 40% RH and pH 1).
In urban (high-NO<sub><i>x</i></sub>) environments, aaSOA
is primarily formed via reversible glyoxal uptake, with 0.12 μg
m<sup>ā3</sup> formed after 12 h at 80% RH, with 20 μg
m<sup>ā3</sup> initial sulfate. OS formation under all conditions
studied is maximum at low pH and lower relative humidities (<60%
RH), i.e., when the aerosol is more concentrated. Therefore, OS species
are expected to be good tracer compounds for aqueous aerosol-phase
chemistry (vs cloudwater processing)
Photoactivated Production of Secondary Organic Species from Isoprene in Aqueous Systems
Photoactivated reactions of organic
species in atmospheric aerosol
particles are a potentially significant source of secondary organic
aerosol material (SOA). Despite recent progress, the dominant chemical
mechanisms and rates of these reactions remain largely unknown. In
this work, we characterize the photophysical properties and photochemical
reaction mechanisms of imidazole-2-carboxaldehyde (IC) in aqueous
solution, alone and in the presence of isoprene. IC has been shown
previously in laboratory studies to participate in photoactivated
chemistry in aerosols, and it is a known in-particle reaction product
of glyoxal. Our experiments confirmed that the triplet excited state
of IC is an efficient triplet photosensitizer, leading to photosensitization
of isoprene in aqueous solution and promoting its photochemical processing
in aqueous solution. Phosphorescence and transient absorption studies
showed that the energy level of the triplet excited state of IC (<sup>3</sup>IC*) was approximately 289 kJ/mol, and the lifetime of <sup>3</sup>IC* in water under ambient temperature is 7.9 μs, consistent
with IC acting as an efficient triplet photosensitizer. Laser flash
photolysis experiments displayed fast quenching of <sup>3</sup>IC*
by isoprene, with a rate constant of (2.7 ± 0.3) Ć 10<sup>9</sup> M<sup>ā1</sup> s<sup>ā1</sup>, which is close
to the diffusion-limited rate in water. Mass spectrometry analysis
showed that the products formed include ICāisoprene adducts,
and chemical mechanisms are discussed. Additionally, oxygen quenches <sup>3</sup>IC* with a rate constant of (3.1 ± 0.1) Ć 10<sup>9</sup> M<sup>ā1</sup> s<sup>ā1</sup>