Contaminated sediments from the Milltown Reservoir in western Montana
release arsenic and various heavy metals (e.g., Cu, Cd, Pb, Zn, Mn) in
to an underlying alluvial aquifer as redox conditions in the sediments
change with seasonally fluctuating water levels. Porewater analyses i
ndicate that sulfate is depleted with depth. In this study, the feasib
ility of inducing As(III) precipitation through bacterial reduction of
sulfate; was evaluated in laboratory microcosms established under str
ictly anaerobic conditions. As(III), Fe(II), and sulfate concentration
s were routinely monitored in the aqueous phase as sulfate was reduced
to sulfide. Both As(III) and Fe(II) concentrations in the sediment mi
crocosms decreased as sulfide was made available. Energy-dispersive x-
ray (EDS) analysis indicated that some of the arsenic was precipitated
as an iron-arsenic-sulfide solid phase. The precipitation of arsenic
observed in this laboratory study suggests that bacterial sulfate redu
ction may be a process by which heavy metals are immobilized in sedime
nts; however, even though the Milltown sediments contained sulfate-red
ucing bacteria, their activity appears to be both sulfate and carbon l
imited.