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Chapter 3 <br />3.3 WATER RESOURCES <br />3.3.1 Regulatory Framework <br />If the Dry Fork LBA tract is issued, the lessee or <br />operator would be required to submit a permit <br />application package (PAP) to the USDI-OSM and <br />the CDMG before any mining could occur. The <br />Forest Service has a concurrence role at the mine <br />permitting stage, if NFS lands are involved. The <br />SMCRA and the Colorado Surface Coal Mining <br />Reclamation Act contain provisions for protection <br />of water resources from effects of underground coal <br />mining. Parts of these acts and enabling regulations <br />provide for no disruption of the hydrologic balance <br />(i.e. impart no material damage to these resources). <br />As part of the PAP, an applicant must also prepare a <br />probable hydrologic consequences document. This <br />document is reviewed by the agencies and a <br />cumulative hydrologic impacts analysis (CHIA) <br />prepared by the CDMG. A CHIA for the North <br />Fork of the Gunnison River was conducted by <br />CDMG as a means of assessing hydrologic impacts <br />to surface water resources and regulating discharge <br />from the West Elk Mine (CDMG 1997). It is <br />assumed that information in the existing CHIA will <br />also apply to the Dry Fork tract. A new CHIA will <br />be prepared during the permitting process by the <br />CDMG. <br />Under the state coal regulations, various state <br />agencies have permitting authority for the activities <br />associated with mining. For example, the Colorado <br />Department of Public Health and Enviroimrent <br />(CDHPE) regulates water quality discharges from <br />West Elk Mine through a National Pollutant <br />Discharge Elimination System {NPDES) permit. <br />The water rights held by the MCC on the North <br />Fork of the Gunnison River and in other locations <br />are administered by the Colorado State Engineer <br />under the Division of Water Resources. <br />The Dry Fork LBA tract lies to the southeast and <br />east of the West Elk Mine's existing mining permit <br />area (MCC Permit C-80-007). The mining permit <br />details monitoring of performance standards and <br />permit requirements, including water resources <br />monitoring. Results of annual monitoring must be <br />reported annually in an annual hydrologic report. <br />Affected Environment and Environmental Consequences <br />The Forest Service District Office in Paonia, <br />Colorado and MCC agreed to informal monitoring <br />of the Forest's water resources. Results of this <br />monitoring are included in MCC's Annual <br />Hydrologic Report (sec Chapter 6). <br />MCC has aState-approved water replacement plan <br />included as part of their approved mine permit. The <br />Mountain Coal Company Water Augmentation Plan <br />was adjudicated in February 1987, in Division 4, <br />State of Colorado Water Court. A copy of the <br />Adjudicated Water Augmentation Plan is included <br />in MCC State-approved mine permit. The water <br />augmentation plan covers mitigation of potential <br />impacts from mining in the Minnesota Creek Basin. <br />The water augmentation plan is based on worst case <br />conditions where mining in the basin depletes the <br />Dry Fork of Minnesota Creek and requires <br />augmentation by Mountain Coal Company water <br />rights up to 10.96 cubic feet per second (4919 <br />gallons per minute) maximum headgate diversion. <br />3.3.2 Analysis Methods and Area <br />The project impact area for water resources is the <br />Dry Fork LBA tract area and the Upper Dry Fork of <br />Minnesota Creek, Deep Creek, and Upper Lick <br />Creek drainages. The cumulative impact area is the <br />azea encompassed by the West Elk Mine existing <br />leases and permit area. <br />The existing environment for water resources <br />includes stream segments that drain the project area, <br />groundwater in alluvium/colluvium, overburden, <br />and coal bearing zones, discharge water quality, and <br />the water balance. <br />Springs, seeps, and stream segments that drain the <br />project area were assessed by: <br />• Changes in channel morphology due to <br />subsidence, <br />• Changes in surface water flow, and <br />• Changes in sediment and constituent load. <br />Groundwater impacts from mining-related <br />subsidence were assessed by: <br />• Changes in groundwater levels in monitored <br />wells, and <br />Dry Fork Lease-By Application FE1S 3-15 <br />