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. 1999 Apr;65(4):1548-55.
doi: 10.1128/AEM.65.4.1548-1555.1999.

Microbiological and geochemical characterization of fluvially deposited sulfidic mine tailings

Affiliations

Microbiological and geochemical characterization of fluvially deposited sulfidic mine tailings

B Wielinga et al. Appl Environ Microbiol. 1999 Apr.

Abstract

The fluvial deposition of mine tailings generated from historic mining operations near Butte, Montana, has resulted in substantial surface and shallow groundwater contamination along Silver Bow Creek. Biogeochemical processes in the sediment and underlying hyporheic zone were studied in an attempt to characterize interactions consequential to heavy-metal contamination of shallow groundwater. Sediment cores were extracted and fractionated based on sediment stratification. Subsamples of each fraction were assayed for culturable heterotrophic microbiota, specific microbial guilds involved in metal redox transformations, and both aqueous- and solid-phase geochemistry. Populations of cultivable Fe(III)-reducing bacteria were most prominent in the anoxic, circumneutral pH regions associated with a ferricrete layer or in an oxic zone high in organic carbon and soluble iron. Sulfur- and iron-oxidizing bacteria were distributed in discrete zones throughout the tailings and were often recovered from sections at and below the anoxic groundwater interface. Sulfate-reducing bacteria were also widely distributed in the cores and often occurred in zones overlapping iron and sulfur oxidizers. Sulfate-reducing bacteria were consistently recovered from oxic zones that contained high concentrations of metals in the oxidizable fraction. Altogether, these results suggest a highly varied and complex microbial ecology within a very heterogeneous geochemical environment. Such physical and biological heterogeneity has often been overlooked when remediation strategies for metal contaminated environments are formulated.

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Figures

FIG. 1
FIG. 1
Miles Crossing research site map showing the location of cores A through F.
FIG. 2
FIG. 2
Pore water chemistry at sites A (left) and B (right) as a function of depth. The upper panel shows field-measured parameters, pH, and DO content. Concentrations of sulfate, copper, and iron are presented in the lower panel. The depth of the water table (WT) is denoted by the dashed line.
FIG. 3
FIG. 3
Solid-phase Cu (top) and Fe (bottom) concentrations at sites A (left) and B (right) as a function of depth. The various fractions are operationally defined based on selective extractions as reducible (amorphous and crystalline oxides), oxidizable (sulfides and organic), and total metals in all fractions. The depth of the water table (WT) is denoted by the dashed line.
FIG. 4
FIG. 4
MPN-determined cell densities of iron- and sulfur-oxidizing bacteria as a function of depth. Symbols: ●, acidophilic iron-oxidizing bacteria; ○, neutrophilic sulfur-oxidizing bacteria. Capital letters denote the core site location.
FIG. 5
FIG. 5
Abundance of iron-reducing bacteria (●) and manganese-reducing bacteria (○) in Silver Bow Creek tailings as a function of depth at coring locations A and B.
FIG. 6
FIG. 6
Vertical concentration profile showing the percent total carbon (bars) and MPN estimates for sulfate-reducing bacteria (⧫) observed at sites A and B.

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