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GENERAL32839
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GENERAL32839
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Last modified
8/24/2016 7:55:09 PM
Creation date
11/23/2007 7:26:56 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1977306
IBM Index Class Name
General Documents
Doc Date
2/8/2006
Doc Name
Response to the Jan.17 2006 Ltr.
From
GeoScience Services
To
DMG
Permit Index Doc Type
DMO
Media Type
D
Archive
No
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GeoScience Services <br />2263 %ingston Road <br />Grand Junction, CO 81503 <br />(970) 314-3356 <br />1992). This data indicates that the background water quality for perched water in the Salt <br />Wash does not meet drinking water standards. <br />Please state all other input parameters and assumptions that are implicit in the <br />model <br />All of the boundary conditions for the model are presented in the site reports. The model <br />is run under steady state conditions assuming consistent flow conditions during the <br />simulations. Representative moisture chazacteristic curves for the soil/rock types aze <br />used to describe unsaturated flow in the vadose zone. Water content values for the <br />unsaturated zone are calculated by the model based on the moisture characteristic curves <br />and the rate of recharge. <br />Finally, the revised geologic cross sections attached to this letter report do not exaggerate <br />the vertical scale as did the previous cross sections presented in the mine evaluation <br />reports. At this revised scale, it is cleaz that the predicted plume for the SM-18 mine is <br />located at a substantial distance from the hillside and does not present the potential for <br />lateral migration and subsequent discharge of potential plumes along the hillside. <br />Further, the dip of the bedrock is away from the cliff face plus recharge along the cliff <br />induces a hydraulic gradient away from the cliff face. <br />In summary, modeling predictions using several conservative assumptions indicate that <br />the waste piles from uranium mining operations at the SM-18, ID-6, JD-8, and JD-9 <br />mines pose minimal impact to the environment. This statement is based on the following <br />facts: <br />1. Model predictions show that after 1000 yeazs of transport, no species of concern <br />reach the underlying water table. <br />2. Concentrations at the leading edge of the plume are significantly lower than <br />background concentrations in the underlying aquifers. <br />3. Even using the unrealistic assumption of no sorption, the leading edge of the <br />plume as defined by a concentration of one millionth of the initial concentration <br />fails to reach the groundwater. <br />4. Under realistic conditions, the rock units underlying all of the mine waste piles <br />would exhibit significant sorption characteristic that would retard the movement <br />of species of concern. As noted in the response to comments, the Morrison <br />Formation behaves as a geochemical trap that resulted in the Uravan Mineral Belt. <br />5. Laboratory tests on the permeability of the Summerville Formation yielded a <br />hydraulic conductivity value of less than 9.7 E-10 cm/s, effectively creating an <br />aquiclude that would prevent downward migration of water to potential aquifers <br />below the Summerville. For comparison purposes, concrete has a hydraulic <br />conductivity of lE-8 cm/s. <br />
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