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2012-10-01_REVISION - M1977311 (12)
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2012-10-01_REVISION - M1977311 (12)
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Last modified
6/15/2021 2:26:51 PM
Creation date
10/19/2012 12:55:54 PM
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Template:
DRMS Permit Index
Permit No
M1977311
IBM Index Class Name
REVISION
Doc Date
10/1/2012
Doc Name
AM-01 EEP SUBMITTAL
From
COTTER
To
DRMS
Type & Sequence
AM1
Email Name
GRM
Media Type
D
Archive
No
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8.6 Mobilization of Uranium Related Constituents <br />With an understanding of the site geology, hydrology, and geochemistry, a scenario of <br />possible mobilization and transport of uranium and related constituents needs to be <br />developed to design an effective monitoring strategy. Mining would disturb the uranium <br />deposits by introducing oxygen into reduced mineralized zones. It is possible that <br />changes in redox conditions could mobilize uranium - related constituents but the <br />geochemistry indicates that only limited amounts could be mobilized due to the low <br />solubility of these uranium minerals. The lack of groundwater in the area further <br />prevents a viable pathway for the transport of these constituents. If groundwater was <br />encountered in sufficient quantities to transport the uranium and related constituents (all <br />hydrologic data suggests this is not the case), then groundwater in the upper Salt Wash <br />sandstone would migrate down dip toward the syncline between the Paradox and <br />Uncompahgre uplifts. <br />Kearl (2005) conducted transport modeling studies to estimate the transport of mineral <br />constituents associated with uranium ore deposits near the town of Uravan (Appendix I). <br />These studies assumed that the Entrada Sandstone was the upper most aquifer in the area <br />- applicable at SR -13A mine site based on the area well data. A conservative approach <br />consistent with the Nuclear Regulatory Commission requirements for high -level nuclear <br />waste sites was used to develop a worst -case scenario - not necessarily the most likely <br />scenario. Even under the worst case conditions, the modeling predicted that after 1000 <br />years, uranium - related constituents migrated approximately 200 feet vertically at a <br />concentration of 10 -6 (1 /1,000,000 of the source concentration) of the initial concentration <br />in the pore water of the waste rock. The uranium plume is contained in the Salt Wash <br />Member of the Morrison Formation. The plume does not enter the Entrada Sandstone. <br />The Summerville Formation provides an additional buffer zone restricting potential <br />contamination from entering the groundwater. <br />The results of this analysis indicate that conditions are not conducive to the transport of <br />uranium - related constituents to the environment. Geochemistry suggests that <br />mobilization of these constituents is unlikely. There is no indication of a continuous <br />groundwater system that could provide a pathway for these constituents to migrate from <br />the mine into the environment. Transport modeling has shown that vertical migration <br />from the upper Salt Wash sandstone to the upper -most aquifer in the area (Entrada <br />Formation) is highly unlikely due to the lack of water, low permeability of the strata and <br />the sorption of uranium - related constituents. <br />8.7 Proposed Groundwater Monitoring Plan <br />If water is encountered during mining, then the water will be sampled and a chemical <br />analysis performed. If levels of uranium related constituents are above established <br />regulatory guidelines, then a well will be placed down gradient of the mining area that <br />contains groundwater and monitored according to DRMS regulations. This approach will <br />provide a better chance of encountering groundwater in a monitoring well rather than <br />drilling a hole at a random location down gradient of the mine workings. The data <br />gathered by Cotter Corporation supports this plan. <br />O'Connor Design Group Inc. T - 16 <br />
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