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2011-09-27_REVISION - M1990057 (10)
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2011-09-27_REVISION - M1990057 (10)
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Last modified
6/16/2021 6:12:53 PM
Creation date
9/29/2011 11:33:52 AM
Metadata
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Template:
DRMS Permit Index
Permit No
M1990057
IBM Index Class Name
REVISION
Doc Date
9/27/2011
Doc Name
Revised TR-03, with Adequacy Responses Incorporated.
From
The Union Milling Company
To
DRMS
Type & Sequence
TR3
Email Name
MAC
Media Type
D
Archive
No
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Geologic Setting <br />UMC concurs with CTL that the TSF is in an area of a temporary perched water condition, <br />prevalent during spring melts and wet years. As discussed in CTL Thompson's April 1990 <br />Report, Permeability Study Tailing Pond Area Leadville Mining and Milling Corporation Mill <br />near Leadville, Colorado, the tailings disposal area soils are colluvial. There appear to be two <br />colluvial types, clays with lower permeabilities and gravel lenses with higher permeabilities. <br />Most of the tailings disposal area is over the lower permeability clays (k =2ft/yr to 7ftlyr). The <br />northern TSF area appears to be over a 1.5ft thick gravel lens with a permeable of 5000ft/yr at 8 <br />feet of depth. Other gravel lenses have permeabilities of 230ft/yr. <br />A monitoring well and several permeability test holes from 20yrs ago still exist within the <br />existing TSF area. UMC samples /observes the monitoring well quarterly. Additionally, UMC <br />has sporadically observed permeability test wells over the last several years. All but one of the <br />permeability test wells will become part of the TSF impoundment. <br />Monitoring well <br />MW -1 (OH -1 in CTL Thompson reports) shows minor water levels in the spring, and <br />then is dry, or at best damp following precipitation events. MW -1 is completed to a <br />depth of 9685 (9ft below the bottom of the impoundment) and is completed in a layer <br />described as "sand, dense, very clayey, gravelly, moist, red -brown (SC) ". UMC monitors <br />this well quarterly and reports the results in the annual report. All but one sample period <br />has reported no water. <br />Permeability test holes <br />PT -2, located just south of the existing TSF disturbance and in the northern portion of the <br />proposed TSF disturbance, has shown water levels during spring melts with the water <br />dissipating over time. PT -2 is completed to a depth of 9693 feet (lft below the bottom of <br />the impoundment) and is completed in a layer described as "gravel, dense, very clayey, <br />very sandy, moist, red -brown (GC) ". PT -2 averages a permeability of 2ftlyr. Based on <br />random observations over 3 years, UMC's concludes water infiltrates this hole in the <br />spring and dries out in the summer. <br />PT -3, located east of MW -1 and to the southeast of the proposed TSF disturbance, has <br />not shown water levels during spring melts. PT -3 is completed to a depth of 9701 feet <br />(7ft above the bottom of the impoundment) and is completed in a layer described as <br />"gravel, dense, very clayey, very sandy, moist, red -brown (GC) ". PT -3 averages a <br />permeability of 7ft/yr. <br />Recently drilled TH -2, located on the existing TSF disturbance embankment, ended in <br />water during the spring melt. TH -2 is drilled to a depth of 30 feet from the top of the <br />existing embankment (12ft below the bottom of the impoundment) and ends in a layer <br />described as "sandy clay overlaying clayey sand and gravel ". TH -2 permeability tests <br />were not conducted. TH -2 encountered water at 25 feet, and subsequent measurements <br />have shown water at 28 feet of depth. <br />UMC believes the above test holes all confirm colluvium/alluvium within the TSF area, yielding <br />unsorted sediment of varying particle sizes ranging from boulders to clay and areas of high and <br />low permeability. Snowmelt and storm runoff water saturates the hillside and colluvium in wet <br />periods and migrates through the colluvium/alluvium, creating the observed temporary perched <br />M1990 -057 September 27, 2011 <br />
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