HR: 1340h
AN: B23D-1582 [Abstracts]
TI: Oxidation of humic substances supports denitrification reactions in agricultural soils.
AU: * Van Trump, J I
EM: vantrump@berkeley.edu
AF: University of California, Berkeley, Department of Plant and Microbial Biology
271 Koshland Hall, Berkeley, CA 94750,
AU: Coates, J D
EM: jcoates@nature.berkeley.edu
AF: University of California, Berkeley, Department of Plant and Microbial Biology
271 Koshland Hall, Berkeley, CA 94750,
AB:
Humic substances (HS) are a ubiquitous, recalcitrant, and diverse class of compounds arising from degradation
and condensation of plant and microbial biopolymers. Many bacteria oxidize hydroquinones within humic
substances to their quinone analogs, providing electrons for respiratory processes such as nitrate reduction.
Microbial hydroquinone oxidation contributes to the redox state of HS and supports denitrification, which may be of
import to agricultural soils where nitrate retention is critical and HS are prevalent. Most probable number counts
were performed on soils collected from a Nebraska farm, with the model humic hydroquinone 2,6-
anthrahydroquinone disulfonate (AHDS) serving as an electron donor and nitrate as the electron acceptor.
Results indicated that AHDS oxidizing, nitrate reducing bacteria were present in soils from bluegrass fields
(104 cells/g) and aspen groves (106 cells/g), as well as in plots of corn (106 cells/g), and soybean
treated (106 cells/g) and un-treated (105 cells/g) with pig slurry. These results demonstrate that
microorganisms participating in the proposed metabolism are prevalent within agricultural soils. Upflow glass
columns were constructed, containing a support matrix of glass beads amended with 10% w/w soil from the corn
plot previously mentioned. All columns were subjected to a continual flow of phosphate-buffered water amended
with sodium nitrate. Above the point source for nitrate injection, phosphate-buffered water containing electron
donor treatments were continually injected. The impacts of electron donor treatments (no donor, oxidized HS,
reduced HS, and acetate) on denitrification and other geochemical parameters were observed. Column studies
were able to resolve effects of electron donor treatment both spatially as a function of distance from the injection
point source, and temporally, as a function of time of donor treatment. Four sample ports in each column were
routinely analyzed for concentrations of nitrate, nitrite, Fe(II), and humic-born hydroquinones. All data were
analyzed with respect to dilution factors obtained through analysis of a conservative bromide tracer present in
electron donor medium. Addition of oxidized HS, reduced HS, and acetate all resulted in significant loss of nitrate
from the columns. Significant nitrite accumulation was not observed. Of all the electron donor treatments,
reduced HS, enriched for hydroquinone-containing functional moieties, supported the greatest degree of
denitrification. The participation of excess hydroquinones in denitrification accounted for approximately 104% of
the difference in nitrate reduction between reduced and oxidized HS treatments. This electron balance allowed
for assignment of respiratory activity due to hydroquinone oxidation, rather than degradation of humic substances
or associated electron-donating compounds. These results suggest that denitrification reactions catalyzed by
microbial oxidation of reduced HS may be prevalent in agricultural soils. Likewise, these results demonstrate for
the first time that respiratory behavior due to hydroquinone oxidation, as well as impact upon local geochemistry,
can be analyzed in complex flow-through model systems.
DE: 0469 Nitrogen cycling
DE: 4802 Anoxic environments (0404, 1803, 4834, 4902)
DE: 4806 Carbon cycling (0428)
DE: 4851 Oxidation/reduction reactions (0471)
SC: Biogeosciences [B]
MN: 2007 Fall Meeting