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2020-10-12_GENERAL DOCUMENTS - C1981010
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2020-10-12_GENERAL DOCUMENTS - C1981010
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Last modified
10/13/2020 8:24:40 AM
Creation date
10/13/2020 7:50:41 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1981010
IBM Index Class Name
General Documents
Doc Date
10/12/2020
Doc Name Note
For PR10
Doc Name
Proposed Decision and Findings of Compliance
From
DRMS
To
Trapper Mining Inc
Permit Index Doc Type
Findings
Email Name
JLE
RAR
Media Type
D
Archive
No
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Surface Water Impacts <br /> Surface water flow and quality are monitored in the Flume System, Johnson Gulch, <br /> No Name Gulch,Ute Gulch, Pyeatt System, Oak, Gulch, Horse Gulch and Deal <br /> Gulch. Generally, Johnson,No Name East Pyeatt and Middle Flume gulches <br /> exhibit flow over the course of the year. The most noticeable change in surface <br /> water quality resulting from mining activities constitutes increased levels of total <br /> dissolved solids (TDS). TMI expects higher TDS in some surface water runoff <br /> for a few years after reclamation in an area. Increased TDS levels occur <br /> periodically when the contribution from precipitation and snowmelt is at a <br /> minimum (base flow conditions). <br /> Conductivity, TDS and major constituents tend to increase as the ground water <br /> contribution comprises a larger portion of flow. For a detailed analysis of surface <br /> water impacts,the 2019 Annual Hydrology Report, Section 2.5 of the permit <br /> presents the most current information. <br /> Leachate that may discharge from the toe of the Horse Gulch Fill probably will <br /> cause an increase in the dissolved solids content of natural stream flows in Horse <br /> Gulch. Rain or snowmelt provides most natural surface water flows in Horse <br /> Gulch. Although loading of Horse Gulch surface flows with dissolved solids from <br /> the fill would be a local impact, it does not rise to the level of material damage <br /> because use or potential use is not likely to be impaired. An exceedance of an <br /> instream standard in Horse Gulch is unlikely because leachate from the fill will <br /> probably be alkaline (like all other Trapper leachates)and is not likely to contain <br /> high concentrations of the inorganic or metals constituents for which there are <br /> numeric standards in Horse Gulch. <br /> Ground Water Impacts <br /> The 2019 Annual Hydrology Report AHR), Section 2.5 of the permit presents the <br /> most current information regarding springs and seeps at TMI. Table B-2 Appendix <br /> B presents the 2010 -2019 water quality data for springs and seeps at Trapper Mine. <br /> Flow from the springs and seeps is shown on Table B-2. The table indicates that <br /> only the East Pyeatt discharged during 2019 at a rate exceeding 5 gallons per <br /> minute,the minimum for collecting a sample. <br /> The NPDES permit#CO-0032115 issued by the Colorado Department of Public <br /> Health and Environment describes water quality monitoring requirements. Pit <br /> dewatering occurs in L,N Pits, and well dewatering in the G Pit wells. All pit water <br /> is routed to NPDES drainage systems with discharges monitored at the approved <br /> outfall. Dust suppression for the main haul road consumes all the water yielded <br /> from dewatering activities. Currently a number of the listed outfalls encompass <br /> Phase III bond released areas and therefore are no longer subject to DRMS <br /> monitoring requirements. <br /> IV. Topsoil <br /> Soil information can be found in Section 2.6,Volume II and Section 4.9,Vol. IV. <br /> 17 <br />
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