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2025-05-02_REVISION - C1981010 (2)
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2025-05-02_REVISION - C1981010 (2)
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Last modified
5/6/2025 11:15:36 AM
Creation date
5/6/2025 10:46:18 AM
Metadata
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Template:
DRMS Permit Index
Permit No
C1981010
IBM Index Class Name
Revision
Doc Date
5/2/2025
Doc Name
Proposed Decision and Findings of Compliance
From
DRMS
To
Trapper Mining, Inc.
Type & Sequence
PR12
Email Name
RAR
JLE
Media Type
D
Archive
No
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Gulch. Generally, Johnson,No Name East Pyeatt and Middle Flume gulches exhibit <br /> flow over the course of the year. The most noticeable change in surface water quality <br /> resulting from mining activities constitutes increased levels of total dissolved solids <br /> (TDS). TMI expects higher TDS in some surface water runoff for a few years after <br /> reclamation in an area. Increased TDS levels occur periodically when the contribution <br /> from precipitation and snowmelt is at a 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 2021 Annual Hydrology Report, Section 2.5 of the permit presents <br /> the most current information. <br /> Leachate that may discharge from the toe of the Horse Gulch Fill probably will cause <br /> an increase in the dissolved solids content of natural stream flows in Horse Gulch. <br /> Rain or snowmelt provides most natural surface water flows in Horse Gulch. <br /> Although loading of Horse Gulch surface flows with dissolved solids from the fill <br /> would be a local impact, it does not rise to the level of material damage because use or <br /> potential use is not likely to be impaired. An exceedance of an instream standard in <br /> Horse Gulch is unlikely because leachate from the fill will probably be alkaline (like <br /> all other Trapper leachates)and is not likely to contain high concentrations of the <br /> inorganic or metals constituents for which there are numeric standards in Horse Gulch. <br /> Ground Water Impacts <br /> The 2023 Annual Hydrology Report (AHR), Section 2.5 of the permit presents the <br /> most current information regarding springs and seps at TMI. Appendix B presents <br /> ground water quality data from 2012 through 2022. Flow from the springs and seeps <br /> is shown on Table B-2. A CD submitted with the AHR provides all historical data. <br /> The NPDES permit#CO-0032115 issued by the Colorado Department of Public Health <br /> and Environment describes water quality monitoring requirements. Pit dewatering <br /> occurs in L,N Pits, and well dewatering in the G Pit wells. All pit water is routed to <br /> NPDES drainage systems with discharges monitored at the approved outfall. Dust <br /> suppression for the main haul road consumes most of the water yielded from <br /> dewatering activities. Currently a number of the listed outfalls encompass Phase III <br /> bond released areas and therefore are no longer subject to DRMS monitoring <br /> requirements. <br /> IV. Topsoil <br /> Soil information can be found in Section 2.6,Volume II and Section 4.9,Vol. IV. <br /> The Division previously granted a variance from topsoil removal in accordance with Rule 4. <br /> 06.2(2)(a). Specific areas which the operator will not strip topsoil are limited to rocky areas which <br /> occur over limited areas throughout the mine area. Each area approved is handled separately as a <br /> minor revision to the permit and no general variance is currently approved. <br /> V. Sealing of Drilled Holes and Underground Openings <br /> Sealing of wells,holes, and other openings is discussed in permit Section 3. 3,Vol. III. <br /> 15 <br />
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