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HYDRO29526
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Last modified
8/24/2016 8:48:28 PM
Creation date
11/20/2007 11:03:47 PM
Metadata
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Template:
DRMS Permit Index
Permit No
M1988112
IBM Index Class Name
Hydrology
Doc Date
8/25/1999
Doc Name
TECHNICAL SUPPORT DOCUMENT FOR THE CDPS PERMIT APPLICATION
Media Type
D
Archive
No
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and compared the antidegradation-based limits for each baseline loading 4as is summarized in Appendix C for the <br />250 gpm discharge flow, along with a comparison with the calculated water quality standard-based limitationsl. <br />Based upon this evaluation, the Division has concluded that the baseline loading will still be based upon Station RS- <br />5, which overall results in more stringent and protective limitations in the permit. <br />Aluminum: Based upon the concentrations of aluminum that have been detected in the pit backfill monitoring <br />wastewater source, the Division finds that there is a reasonable potential for aluminum to occur in the untreated <br />ground water source. Thus, limitations and monitoring have been added for potentially dissolved aluminum for the <br />001 outfalls. Since there should be no discharge from the West Pit to 002, there are no limits or routine monitoring <br />for aluminum at this location. However, if seeps should be identified within the historically defined area as shown <br />in figure 2 of the permit, parameters such as potentially dissolved aluminum, dissolved iron, and dissolved <br />manganese must be analyzed in samples collected. <br />Radioactive Constituents: With respect to the radioactive constituents that are associated with Gross Alpha <br />Activity, discharge permits in Colorado have specifically identified that this is primarily associated with radium <br />(226+228) and uranium. Where radioactive constituents are limited for other mining discharge permits, limits and <br />monitoring are specified for these two constituents, and these limits are based upon the statewide standards for all <br />surface waters. The BMRI discharge permit explicitly sets limits on the concentrations of uranium and radium <br />discharged from the water treatment facility. <br />Time Periods: In the original public noticed draft permit, there was reference to an initial time period that included a <br />higher discharge flow rate (400 gpml, with a later time period when discharge flows would be expected to <br />decrease. Thus, tiered limitations in the permit were developed and these limits along with discharge flow rate <br />limits are based upon discharge flow values of 400, 250, and 100 gallons per minute Igpml• With the revisions <br />and updates made for this facility's permit, there is no longer any defined periods for initial and later discharge <br />flows. Thus, previous comments related to flows are no longer applicable. The tiered-discharge approach for <br />Discharge Point 001 provides the flexibility necessary to reasonably represent the probable range of ilows that are <br />expected to occur during the extraction of groundwater from the West Pit. For the purposes of the CDPS permit, <br />BMRI will pump the backfilled West Pit as necessary, up to a maximum flow rate of 400 gpm 130 day averagel, to <br />maintain a reversed hydraulic gradient from the Rito Seco alluvial aquifer to the West Pit. <br />Comments: Issues related to outfall 002: <br />- Better definitions for the location and requirements for outfall 002 <br />- Utilizing monitoring wells to define outfall 002 <br />- Addressing specific flow and other limitations and monitoring requirements for outfall 002 <br />- Identifying seepage contributions as part of the mass balance water quality standard-based calculations <br />- Not referencing the CDMG requirements for TR-26 and TR-28 in association with the requirements for outfall <br />002 in the CDPS discharge permit <br />- Concerns related to short-term West Pit groundwater discharge issues and long-term water groundwater <br />discharge issues (defining a window far identification of ground water flowing through a restricted zone as <br />points of compliance; utilization of additional ground water monitoring wells; installation of a slurry wall) <br />- Concerns regarding the Best Management Practices requirements described far outfall 002 <br />Response: <br />There were a number of comments related to outfall 002. In response to these comments, several major revisions <br />were made relating to outfall 002. Descriptive language, as well as figure 2 of the permit, have been revised to <br />define the window and boundary for 002. Also, a limitation that is associated with this outfall has been•added in <br />the permit which defines 002 with respect to maintaining a required water level depth in the West Pit that is below <br />the water level of the Rito Seco to ensure that the hydraulic gradient is reversed resulting in permanent elimination <br />of flow from the West Pit to the seeps on the bank oT the Rito Seco. A compliance schedule has also been <br />incorporated and the Best Management Practices requirements for this outfall have been revised in the permit to <br />further address the existing situation. The compliance schedule will address requirements to follow in case any <br />seeps should occur in the window /boundary of the 002 outfall. (See permit languagel. <br />With regard to the installation of a slurry wall, BMRI, WOCD, and CDMG have reviewed the potential merits of the <br />slurry wall and all parties have concluded that the long-term consequences of the slurry wall outweigh the short- <br />term benefits as perceived by the reviewers. The flushing action provided by the inflow of groundwater from the <br />Rito Seco alluvial aquifer is a fundamental component of the water management plan because the inflow of <br />groundwater with lower concentrations of constituents more effectively flushes the secondary sulfate salts <br />associated with the backfill material. When the water management program is completed, the water quality in the <br />West Pit is expected to no longer contain elevated concentrations of constituents. Thus, the issue of "keeping <br />clean water clean" will have been addressed. Additionally, the installation of a slurry wall would further disturb the <br />hydrologic system beyond the changes induced as a result of the historical mining activity with no corresponding <br />benefits. <br />
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