2 research outputs found
Factors Controlling Regioselectivity in the Reduction of Polynitroaromatics in Aqueous Solution
Regioselectivities in the bisulfide reduction of 10
polynitroaromatics (PNAs) to monoamine products
have been determined; four of these compounds have
also been reduced by anoxic sediments in heterogeneous aqueous solution, and the same regioselectivities are observed. Analyses of Austin Model
1−Solvation Model 2 electrostatic potential surfaces
for the radical anions of these polynitroaromatic
compounds provides a reliable method of predicting
the regioselectivity of their reduction. In
particular,
at their minimum-energy geometries in aqueous solution,
it is the more negative nitro group that is selectively
reduced. This is consistent with a mechanism
where regioselection occurs upon kinetic protonation
at the site of maximum negative charge in the radical
anion formed after the first electron transfer to the
neutral PNA. Inclusion of solvation effects is
critical
in order to confidently predict the electrostatic prefer
ence for the reduction of one nitro group over the
others. Sterically uncongested nitroaromatic radical
anions have gas-phase geometries in which the nitro
group is coplanar with the aromatic ring. However,
ortho substituents and solvation effects both
oppose
this tendency and can lead to nitro groups that are
rotated out of the ring plane and
pyramidalized
High Methane Emissions from a Midlatitude Reservoir Draining an Agricultural Watershed
Reservoirs
are a globally significant source of methane (CH<sub>4</sub>), although
most measurements have been made in tropical and
boreal systems draining undeveloped watersheds. To assess the magnitude
of CH<sub>4</sub> emissions from reservoirs in midlatitude agricultural
regions, we measured CH<sub>4</sub> and carbon dioxide (CO<sub>2</sub>) emission rates from William H. Harsha Lake (Ohio, U.S.A.), an agricultural
impacted reservoir, over a 13 month period. The reservoir was a strong
source of CH<sub>4</sub> throughout the year, emitting on average
176 ± 36 mg C m<sup>–2</sup> d<sup>–1</sup>, the
highest reservoir CH<sub>4</sub> emissions profile documented in the
United States to date. Contrary to our initial hypothesis, the largest
CH<sub>4</sub> emissions were during summer stratified conditions,
not during fall turnover. The river–reservoir transition zone
emitted CH<sub>4</sub> at rates an order of magnitude higher than
the rest of the reservoir, and total carbon emissions (i.e., CH<sub>4</sub> + CO<sub>2</sub>) were also greater at the transition zone,
indicating that the river delta supported greater carbon mineralization
rates than elsewhere. Midlatitude agricultural impacted reservoirs
may be a larger source of CH<sub>4</sub> to the atmosphere than currently
recognized, particularly if river deltas are consistent CH<sub>4</sub> hot spots. We estimate that CH<sub>4</sub> emissions from agricultural
reservoirs could be a significant component of anthropogenic CH<sub>4</sub> emissions in the U.S.A