Je. Kostka et al., The impact of structural Fe(III) reduction by bacteria on the surface chemistry of smectite clay minerals, GEOCH COS A, 63(22), 1999, pp. 3705-3713
Although clay mineral reduction is thought to occur primarily as a result o
f the activity of indigenous microorganisms in soil, most research has focu
sed on chemical mechanisms of Fe reduction within clay minerals. Here we sh
ow that bacteria isolated from soils and sediments catalyze the rapid reduc
tion of structural Fe(III) in the smectite clay minerals. The extent of Fe(
III) reduction is large, from 46% to >90%. Furthermore, the effects of stru
ctural Fe(III) reduction by bacteria on the surface chemistry of smectites
are dramatic. Swelling pressure, as measured by water content, was shown to
decrease by 40% to 44% in smectites reduced by bacteria as compared to una
ltered or reoxidized smectites. Particle surface area decreased by 26% to 4
6% in response to bacterial reduction, and the surface charge density as me
asured by the ratio of cation exchange capacity to specific surface area in
creased over the same scale. Measurements of swelling pressure in smectite
saturated with the organic cation trimethylphenylammonium (TMPA) indicated
that the hydrophilic character of the clay mineral surface was enhanced upo
n reduction. The valence state of Fe in the octahedral layer of smectite, a
s revealed through reflectance spectra, correlated to the amount of Fe(III)
reduced in bacterial cultures, providing information on the mechanism of i
ntervalence electron transfer in bacterially reduced clay minerals. The ext
ent of reduction and surface chemical effects catalyzed by bacteria in this
study are similar in magnitude to those observed previously for potent ino
rganic reductants. Given that clay minerals dominate the solid phase of por
ous media and that Fe(III)-reducing bacteria are abundant in soils and aqua
tic sediments, these data suggest that bacterial clay mineral reduction may
play an important role in soil biogeochemistry, affecting processes such a
s nutrient cycles and the fate of organic contaminants. Copyright (C) 1999
Elsevier Science Ltd.