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Southwest Hydrology: The Resource of Semi-Arid Hydrology Volume 4 Number 2
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Southwest Hydrology: The Resource of Semi-Arid Hydrology Volume 4 Number 2
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Southwest Hydrology: The Resource of Semi-Arid Hydrology Volume 4 Number 2
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CO
Date
3/1/2005
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Southwest Hydrology: The Resource of Semi-Arid Hydrology Volume 4 Number 2
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ON THE GROUND c(onenued) <br />New Approach to Address <br />Acid Rock Drainage <br />Gregory J. Olson and Thomas R. Clark <br />— Little Bear Laboratories Inc., and Terry L <br />Mudder — TIMES Ltd. <br />Mine remediation costs are dramatically <br />increased when acid rock drainage (ARD) <br />is present. Consequently, mining engineers <br />have learned it is best to inhibit ARD <br />production before it begins through proper <br />waste management and source control. <br />ARD results from uncontrolled oxidation <br />of metal sulfides, primarily pyrite (FeS2) <br />in waste rock, tailings, and spent ore. Both <br />oxygen and microorganisms are important <br />in this process. Pyrite exposed to oxygen <br />and water slowly oxidizes, producing <br />ferrous sulfate and sulfuric acid. As the <br />pH becomes more acidic, microorganisms <br />greatly accelerate the oxidation of ferrous <br />sulfate to ferric sulfate, a strong oxidant <br />that readily oxidizes more pyrite and <br />other metal sulfides. The end result is <br />production of drainage <br />waters that have low <br />pH, high concentrations <br />of dissolved solids, and <br />toxic metals. <br />With funding from the <br />U.S. Environmental <br />Protection Agency's <br />Small Business Innovative <br />Research Program and <br />a consortium of eight <br />international mining <br />companies, Little Bear <br />Laboratories Inc. and Placement of waste rock in test pits at Red Dog Mine, Alaska. A <br />TIMES Ltd. are evaluating loaded and treated pit in the foreground shows wire leads from a <br />thermistor placed in a vertical pipe for temperature measurements. <br />a method for ARD source <br />control that focuses on stopping the <br />growth of iron - oxidizing microorganisms <br />and minimizing the chemical oxidation of <br />pyrite and other sulfide minerals. <br />Controlling Biooxidation of Iron <br />Iron - oxidizing bacteria at low pH are <br />extremely sensitive to thiocyanate <br />10 • March /April 2005 • Southwest Hydrology <br />(SCN-), with only a few parts per million <br />in solution being lethal. Thiocyanate is a <br />selective biocide, and is much less toxic <br />to "normal" microflora and higher forms <br />of life. It is relatively stable at low pH <br />and under anaerobic conditions, and at <br />neutral pH under aerobic conditions it is <br />biodegraded to carbon dioxide, sulfate, <br />and nitrate. Thiocyanate is a component <br />of wastewater solutions at many precious - <br />metal mines, therefore these solutions <br />could potentially be used for ARD control <br />following selective treatment to remove <br />constituents other than thiocyanate, such <br />as cyanide and metals. <br />Controlling Chemical Oxidation <br />Even if all biooxidation of iron is <br />inhibited, pyrite and other metal sulfides <br />may still be oxidized by oxygen and ferric <br />iron. However, this chemical oxidation can <br />be greatly reduced by adding phosphate <br />to sulfidic mine waste. Phosphates <br />neutralize acidity and precipitate ferric <br />iron and aluminum ions as phosphates. <br />The removal of iron and aluminum from <br />solution as phosphates precludes acid <br />production by precipitation of these metals <br />as hydroxides. <br />Furthermore, iron phosphate precipitation <br />may also coat unreacted pyrite, further <br />preventing its oxidation. Phosphate is a <br />relatively benign and inexpensive chemical <br />available worldwide. <br />In laboratory tests, combined thiocyanate <br />
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