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REV07329
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Entry Properties
Last modified
8/25/2016 1:08:12 AM
Creation date
11/21/2007 9:42:06 AM
Metadata
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Template:
DRMS Permit Index
Permit No
M1988112
IBM Index Class Name
Revision
Doc Date
3/25/1999
Doc Name
SECTION 4
Type & Sequence
TR26
Media Type
D
Archive
No
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• 4.3 Applicable Treatment Processes -Biological Treatment <br />Biological treatment offers a second category of treatment process that has been used in <br />industrial and mining settings. Recent industrial studies show the ability to treat sulfate-rich <br />streams by stimulating the growth of sulfate reducing bacteria (SRB), which use sulfate to <br />generate energy by transforming sulfate to sulfide (Hilton et al., 1986; Mazee et al., 1986). The <br />amount of methane and/or sludge produced is variable and is part of the treatment options <br />evaluation. Biological treatment has a long history of use for treatment of organic wastewaters. <br />In aerobic treatment, air is added to the wastewater through mixing or diffusion to provide <br />oxygen as an electron acceptor so that the bacteria can degrade the organic compounds (electron <br />donors). For high-strength waste constituents, anaerobic treatment (under conditions of no <br />oxygen present) is used. Under anoxic conditions, the concentration of oxygen is too low for <br />use by bacteria. When oxygen is depleted, these facultative bacteria will then use other electron <br />acceptors. In natural endvontnents, bacteria use different constituents in a speciftc sequence that <br />depends directly on the amount of energy released at each step (Stamm and Morgan, 1981). <br />• Oxygen will be used first, followed by nitrate, iron, manganese, sulfate, and finally by carbon <br />dioxide under anaerobic and methanogenic conditions. Many of the sulfate-reducing bacteria are <br />strict anaerobes and cannot live in an environment where oxygen is present. <br />Therefore, to remove sulfate from the groundwater using biological treatment, it is necessary to <br />add an electron donor (organic constituent) to the groundwater and either rely on the natural <br />bacteria in the water or inoculate the water with bacteria. The bacteria will use each available <br />electron acceptor in the order of energy benefit, until that constituent is depleted. This process <br />can take place in situ or in an aboveground bioreactor. In either case, the biochemical <br />mechanisms aze the same. <br />The time-scale for implementation of biological treatment technologies is different than other <br />water treatment methods (e.g., nanofiltration) because the mechanism for removal of constituents <br />depends on a base level of biological activity. Microbes that can reduce sulfate and oxidize <br />• manganese exist in all natural environments, but aze typically limited by adverse environmental <br />conditions (aerobic versus anaerobic) or by an inadequate supply of nutrients (organic carbon). <br />Ba!!!e Maun(ain Resources, /nc. <br />p:1l002671reportslmarchrptlvl6wlrmngfmarch.doc 42 March 22, 1999 <br />
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