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Permit Amendment (AM-06) - Climax Mine <br />CM0000085 <br />Creek systems will generally remain as previously described. • <br />In the Upper Eagle River watershed, however, Robinson Lake is expected to be reclaimed to a fresh water <br />facility, and it, together with Chalk Mountain Reservoir, may no longer be needed by Climax. Therefore, the <br />Chalk Mountain Interceptor could potentially be rerouted to empty directly into Chalk Mountain Reservoir, <br />which overflows directly into Robinson Lake. <br />As shown on Figure AM-06-G-03, it is anticipated that interceptor systems will be constructed around the pit <br />area to reduce the volume of runoff into the pit. <br />G-5.5 Impacted Water Sources <br />The primary sources of impacted water upon closure will not change dramatically from the mineral extraction <br />and production scenario. The amount of fresh water that inadvertently mixes with the impacted waters, <br />however, is expected to be significantly reduced by reclamation thereby reducing the overall volume of water <br />requiring treatment. The primary sources of impacted water will include pit water, water that has infiltrated the <br />underground mine workings, seepage and certain surface runoff from the Storke and camp areas, seepage <br />from the OSFs, 1 Dam, Robinson Dam, 4 Dam, and 5 Dam. Reclamation efforts will attemptto isolate surface <br />runoff from these areas to reduce treatment volumes. The quality of the water seeping from the Storke area, <br />4 Dam, and Robinson Dam is expected to improve so that they may no longer require treatment prior to <br />discharge into the natural stream systems. <br />G-5.6 Water Treatment Systems <br />Upon closure, the SDP will continue to be used to provide first-stage treatment for some impacted waters. <br />Effluent sludge from the SDP will be pumped into new high-density sludge (HDS) holding cells that are <br />proposed to be constructed on Mayflower TSF between the dam crest and normal water pool. New HDS <br />pipelines and pumping facilities will be required for this task. The treated effluent from the SDP and all other <br />impacted waters will be directed to Mayflower Pond. From there, water will be delivered at a controlled rate to <br />the PDWTP for final treatment and discharge to Tenmile Creek. Depending on the pH of the impacted water <br />stored in Mayflower Pond, pH adjustment may be needed to condition these waters as pretreatment prior to <br />delivery to the PDWTP. <br />The flow capacity of the PDWTP will limit the total discharge capacity of the process water system. This rate <br />is directly related to the storage capacity available in Mayflower Pond. Accurately regulated, the flow rate <br />discharged from Mayflower Pond will promote efficient water treatment within the design capacity of the <br />PDWTP. Sludge generated at the PDWTP will be pumped into the HDS cells located on Mayflower TSF just <br />above the expected normal operating pool of Mayflower Pond. <br />G-5.7 Domestic Water Systems <br />Significant changes to the domestic water systems are expected forthe closure scenario. A certain amount of <br />domestic water will likely be required by the SDP and PDWTP and therefore the system cannot be abandoned <br />entirely. The domestic water demands upon closure are certain to be less than those during mineral <br />production. It is currently envisaged that the Arkansas Well, McNulty Well, and Buffehrs Lake will provide <br />sufficient domestic water upon closure. As a result, these systems will be maintained. Chalk Mountain <br />Reservoir and its appurtenant pump station and pipeline may be removed from the domestic water system. <br />G-6 Groundwater <br />Groundwater in the vicinity of the Climax mine site is generally present within a thin veneer of alluvium and <br />glacial till overlaying the bedrock, and ranges from near ground surface to a few tens of feet below ground <br />surface. Groundwater occurrence within the bedrock is limited to the upper fractured portion of the bedrock <br />units. A hydrogeologic study of the underground workings conducted in 1994 indicated that the bulk <br />permeability of the bedrock is relatively low and that the bedrock is not capable of transporting significant <br />quantities of groundwater. Additionally, it was shown that the presence of the Mosquito Fault provides a <br />hydraulic barrier to lateral flow of groundwater flow in the bedrock. <br />• <br />Exhibit G G-12 May 2010