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Mr. Eric Scott <br />Climax Mine - Response to DRMS Adequacy Review Comments <br />• Permit M-1977-493; Amendment AM-06 <br />March 1, 2011 <br />Page 11 of 16 <br />Exhibit U/Section (6) Comment: Please justify the proposal of the "wet cap" reclamation of the <br />remaining TSF areas, as opposed to the more standard practice of reclamation of TSFs using a <br />low permeability cap with positive drainage. It would seem that using the "wet cap" reclamation <br />would create a setting where surface runoff is actually captured on top of the TSF, rather than <br />shed, resulting in a greater volume of impacted water requiring treatment in perpetuity prior to <br />discharge. As it is generally understood that this facility will require post-mining water treatment in <br />perpetuity to prevent adverse impact to surface water, we believe that every attempt should be <br />made to minimize the amount of impacted water that will require future treatment. <br />Response: As described in Exhibit E - Reclamation Plan, both Tenmile and Mayflower TSFs will <br />be reclaimed with a combination of dry and wet covers. Due to concerns regarding water <br />treatment, flood control, constructability, and dam safety, a wet cap is needed for the Climax Mine <br />site. The flow rate of impacted water requiring treatment at CIVIC currently ranges from about <br />3,000 gpm during the winter to about 40,000 gpm during the peak of the snowmelt period. CIVIC <br />manages water to reduce the volume and flow rate of water requiring treatment. This <br />management includes the use of interceptor canals, diversion ditches, surface treatments, and <br />reclamation of formerly impacted land. The seepage from TSF dams and water pumped from the <br />open pit or underground mine workings, however, will continue to require treatment well into the <br />• future. These future sources of impacted water are expected to follow a similar pattern of <br />significant seasonal variability. The use of a wet cap reclamation scenario provides detention <br />storage capacity that allows for seasonal attenuation during the peak flow periods and promotes a <br />more constant flow rate for water treatment. This detention storage dampens the peaks of the <br />impacted water hydrographs and reduces the required capacity of the treatment system. In <br />addition, an active reservoir to store impacted water provides flexibility in the timing and rate of <br />water treatment and therefore reduces the risk of releasing impacted water during an upset <br />scenario in the water treatment system or under unusual hydrologic conditions. <br />Hydrologic flood studies indicate that peak flow rates onto the TSFs are generally in the thousands <br />of cfs during a PMP event. If there is no detention storage capacity within the TSF to attenuate <br />these flows, which would be the case in a dry cover scenario, then very large and heavily armored <br />channels would be required to convey the flood flows safely beyond the site. The detention <br />storage capacity provided by the wet cover configuration allows for much lower capacity flood <br />conveyance facilities. The detention concept is less sensitive to peak flood flow estimation and <br />results in lower risk from erosion, channel failure, and potential dam breach. <br />The wet cap configuration also is consistent with that presented to DRMS and approved in <br />Technical Revision TR-13. The wet cover already established on the Robinson TSF is currently <br />developing into a sustainable mosaic of mesic, wet meadow, and emergent marsh habitats which <br />support a variety of wildlife and waterfowl species. In addition, previously constructed <br />infrastructure at the Robinson TSF, including the existing East Side Channel and 2 Dam Spillway <br />will allow the established pond on the Robinson TSF to be utilized for detention storage capacity at <br />closure.