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2011-10-14_REVISION - M1977300
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2011-10-14_REVISION - M1977300
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Last modified
8/24/2016 4:44:02 PM
Creation date
10/17/2011 12:02:05 PM
Metadata
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Template:
DRMS Permit Index
Permit No
M1977300
IBM Index Class Name
REVISION
Doc Date
10/14/2011
Doc Name
Additional Information for TR12 and TR15.
From
Cotter
To
DRMS
Email Name
DB2
TAK
AJW
Media Type
D
Archive
No
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John Hamrick and Randy Whicker <br />Cotter Corporation (N.S.L) <br />October 10, 2011 <br />Page 3 <br />pool, although the radium -226 activity in Sump No. 10 (0.60 pCi /L) is similar to radium -226 <br />levels at several other downgradient locations (Sump No.4, Sump No.5, MW -6). Relative to <br />mine pool water, the concentrations of molybdenum and radium -226 in Sump No. 10 and <br />downgradient alluvial groundwater are much reduced compared to uranium (Figures 6 and 7). <br />Mine pool water is reducing (low Eh) and contains elevated uranium, molybdenum, radium -226, <br />iron, and manganese (Table 1). However, the chemistry of mine pool water can be modified as <br />it migrates through faults and bedrock fractures and transitions into near - surface alluvium. <br />Under pH- neutral conditions in the presence of carbonate, uranium is expected to remain <br />largely mobile (Langmuir, 1997). Molybdenum and radium -226, however, can be attenuated to a <br />much greater extent compared to uranium and major ions (e.g., magnesium, sulfate). Although <br />the maximum potential for molybdenum adsorption is greatest under low pH (pH = 4 to 5), some <br />adsorption does occur at higher pH values (Goldberg et al., 1996). In the presence of calcium, <br />molybdenum can also precipitate as solid calcium molybdate (CaMoO (Lindsay, 1979). <br />Radium concentrations in solution can be reduced through cation exchange onto clay minerals <br />or coprecipitation with gypsum (Langmuir, 1979). If oxidizing conditions (high Eh) are <br />encountered in the near - surface alluvium, iron and manganese will precipitate from solution as <br />oxide minerals, providing additional adsorption sites for attenuation of radium -226 (Schott and <br />Wiegand, 2003; Zwahlen, et al. 2007). <br />3.0 CONCLUSIONS <br />ame0 <br />Evaluation of the recent geochemical data supplied by Cotter for the Schwartzwalder Mine <br />indicate that elevated uranium concentrations in Sump No. 10 result from a mixture of <br />upgradient alluvial groundwater and geochemically- modified mine pool water. The major ion and <br />uranium concentrations of water in Sump No. 10 are consistent with conservative mixing, while <br />modification by geochemical attenuation has reduced the concentrations of molybdenum and <br />radium -226 to a greater extent. This conclusion is based on: <br />• The presence of elevated concentrations of major ions, TDS, and uranium in Sump No. <br />10 which are intermediate between those of mine pool water and both upgradient and <br />downgradient alluvial groundwater; <br />• Demonstration of conservative mixing between alluvial groundwater and mine pool water <br />with distance downgradient across the site; <br />
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