3 research outputs found
Computational Study of the Effect of GlyoxalâSulfate Clustering on the Henryâs Law Coefficient of Glyoxal
We
have used quantum chemical methods to investigate the molecular mechanism
behind the recently reported (Kampf, C. J.; Environ. Sci. Technol. 2013, 47, 4236â4244) strong dependence of the Henryâs
law coefficient of glyoxal (C<sub>2</sub>O<sub>2</sub>H<sub>2</sub>) on the sulfate concentration of the aqueous phase. Although the
glyoxal molecule interacts only weakly with sulfate, its hydrated
forms (C<sub>2</sub>O<sub>3</sub>H<sub>4</sub> and C<sub>2</sub>O<sub>4</sub>H<sub>6</sub>) form strong complexes with sulfate, displacing
water molecules from the solvation shell and increasing the uptake
of glyoxal into sulfate-containing aqueous solutions, including sulfate-containing
aerosol particles. This promotes the participation of glyoxal in reactions
leading to secondary organic aerosol formation, especially in regions
with high sulfate concentrations. We used our computed equilibrium
constants for the complexation reactions to assess the magnitude of
the Henryâs law coefficient enhancement and found it to be
in reasonable agreement with experimental results. This indicates
that the complexation of glyoxal hydrates with sulfate can explain
the observed uptake enhancement
Protein Cross-Linking and Oligomerization through Dityrosine Formation upon Exposure to Ozone
Air pollution is a potential driver
for the increasing prevalence
of allergic disease, and post-translational modification by air pollutants
can enhance the allergenic potential of proteins. Here, the kinetics
and mechanism of protein oligomerization upon ozone (O<sub>3</sub>) exposure were studied in coated-wall flow tube experiments at environmentally
relevant O<sub>3</sub> concentrations, relative humidities and protein
phase states (amorphous solid, semisolid, and liquid). We observed
the formation of protein dimers, trimers, and higher oligomers, and
attribute the cross-linking to the formation of covalent intermolecular
dityrosine species. The oligomerization proceeds fast on the surface
of protein films. In the bulk material, reaction rates are limited
by diffusion depending on phase state and humidity. From the experimental
data, we derive a chemical mechanism and rate equations for a kinetic
multilayer model of surface and bulk reaction enabling the prediction
of oligomer formation. Increasing levels of tropospheric O<sub>3</sub> in the Anthropocene may promote the formation of protein oligomers
with enhanced allergenicity and may thus contribute to the increasing
prevalence of allergies
Novel Tracer Method To Measure Isotopic Labeled Gas-Phase Nitrous Acid (HO<sup>15</sup>NO) in Biogeochemical Studies
Gaseous
nitrous acid (HONO), the protonated form of nitrite, contributes up
to âź60% to the primary formation of hydroxyl radical (OH),
which is a key oxidant in the degradation of most air pollutants.
Field measurements and modeling studies indicate a large unknown source
of HONO during daytime. Here, we developed a new tracer method based
on gas-phase stripping-derivatization coupled to liquid chromatographyâmass
spectrometry (LC-MS) to measure the <sup>15</sup>N relative exceedance,
ĎÂ(<sup>15</sup>N), of HONO in the gas-phase. Gaseous HONO is
quantitatively collected and transferred to an azo dye, purified by
solid phase extraction (SPE), and analyzed using high performance
liquid chromatography coupled to mass spectrometry (HPLC-MS). In the
optimal working range of ĎÂ(<sup>15</sup>N) = 0.2â0.5,
the relative standard deviation of ĎÂ(<sup>15</sup>N) is <4%.
The optimum pH and solvents for extraction by SPE and potential interferences
are discussed. The method was applied to measure HO<sup>15</sup>NO
emissions from soil in a dynamic chamber with and without spiking <sup>15</sup>N labeled urea. The identification of HO<sup>15</sup>NO from
soil with <sup>15</sup>N urea addition confirmed biogenic emissions
of HONO from soil. The method enables a new approach of studying the
formation pathways of HONO and its role for atmospheric chemistry
(e.g., ozone formation) and environmental tracer studies on the formation
and conversion of gaseous HONO or aqueous NO<sub>2</sub><sup>â</sup> as part of the biogeochemical nitrogen cycle, e.g., in the investigation
of fertilization effects on soil HONO emissions and microbiological
conversion of NO<sub>2</sub><sup>â</sup> in the hydrosphere