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2013-10-02_PERMIT FILE - C1981019A (3)
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2013-10-02_PERMIT FILE - C1981019A (3)
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Last modified
8/24/2016 5:31:59 PM
Creation date
10/18/2013 8:51:20 AM
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Template:
DRMS Permit Index
Permit No
C1981019A
IBM Index Class Name
Permit File
Doc Date
10/2/2013
Section_Exhibit Name
Rule 2 Permits -ST
Media Type
D
Archive
Yes
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RULE 2 PERMITS <br />Groundwater from the reclaimed South Taylor pit will eventually discharge into Good Spring Creek at the <br />drainage that is above the Sturgeon Flume (the unnamed tributary to West Fork Good Spring Creek in <br />Section 21). This would result in a pit spoil spring and/or dischazge through colluvial and shallow <br />bedrock groundwater infiltration. This water would likely have the same characteristics as the water in <br />the Streeter Fill well or the Streeter pond or in similar spoil springs (Williams and Clark, 1994). <br />Analytical data for these sampling points aze summazized on Table 2.04.7-31. <br />If all of the water that infiltrates into the pit dischazges into Good Spring Creek, then 150 acre-feet per <br />year or 92 gallons per minute (0.21 cfs) of pit spoil water will enter the Good Spring Creek drainage. <br />This is more flow than originates from the potentially-impacted springs, which have an average annual <br />flow of 77 gpm. <br />The alluvial aquifer associated with Good Spring Creek has a high transmissivity and is unconfined. <br />Possible impacts to this aquifer would be associated with the infiltration of water from the pit and water <br />quality deviations caused by infiltration of runoff water. <br />The preferential flowpath of bedrock groundwater from the reclaimed pits would tend to be down-dip <br />through and between the different strata of the Williams Fork Formation. The dischazge would be to <br />springs and, thus, some groundwater could eventually rechazge the alluvial material of Good Spring <br />Creek. <br />Transmissivity of the Williams Fork Formation is presented in Section 2.04.7. Measured and published <br />transmissivities of the upper Williams Fork Formation average about 50 square feet per day (ftZ/d). The <br />average hydraulic conductivity of the formation is about 1 foot per day (ft/d). The values utilized to <br />calculate these averages are presented in Table 2.04.7-26 and aze from published data (Robson and <br />Stewart, 1990; tables 5 and 6; upper member Williams Fork Formation). <br />A rectangulaz infiltration azea in the undisturbed pit highwall of 133 feet long by 133 feet high could <br />transmit all of the estimated 92 gpm (approximately 150 acre-feet) of annual rechazge from the reclaimed <br />pit. This is calculated as follows: <br />Annual seepage from the pit = <br />(133 ft high)(133 ft long)(1 fr/d) = 17,710 ft3/d = 150 ac-ft/yr. <br />With approximately 400,000 squaze feet of buried highwall, all of the meteoric water infiltrating into the <br />reclaimed pit that contacts the pit wall is expected to enter the strata of the Williams Fork Formation. <br />Most of this water is expected to eventually contribute to seeps and springs tributary to Good Spring <br />Creek. This suggests that it is possible that a reclaimed pit aquifer (if it develops) will flow entirely into <br />the undisturbed strata, and that there will be no or limited discharge into the su~cial alluvium/colluvium <br />from the reclaimed pit. Whether the pit aquifer dischazges into the bedrock of the Williams Fork <br />Formation or into surface colluvium, it will eventually contribute to the alluvial aquifer and springs <br />tributary to Good Spring Creek. <br />u <br />South Taylor/Lower Wilsou - Aule 2, Pale 116 Revision Date: 3/30/07 <br />Revision No.: PR-02 <br />
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