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West Elk Mine <br />snowmelt or rainfall-runoff periods (when there is no "call" for water in the river). Furthermore, <br />as discussed in Section 2.05.6 (3)(b)(iii & viii), Streams, surface flow losses will be small. A <br />conservative projection of the average annual streamflow "lost" to crack infiltration in the North <br />Fork drainage is less than one acre-foot. The losses that do occur (as a consequence of <br />infiltration into surface cracks) will eventually be dischazged to the North Fork as either <br />springs/seeps or shallow groundwater return flow. MCC recognizes that this may affect the <br />"timing" of dischazges into the North Fork, but the key point is that water will be returned to the <br />river. Also, as described later in this section, given the lazge fault inflows in 1996 and eazly <br />1997, MCC has been a net exporter of water to the river. <br />2. Springs -As discussed at length in Section 2.05.6 (3) (b) (iii & viii) Springs/Seeps, there are no <br />springs in the Apache Rocks and Box Canyon permit revision azeas which are within the <br />fracture zone above the B Seam or the combined caved/fractured zone above the B and E <br />Seams. As such, no spring flow is expected to be lost to the mine workings. Surface cracks <br />could disrupt some of the colluvial springs, but this would ultimately result in the downgradient <br />displacement of the flows, and there would be no loss to the river. <br />Groundwater -There is extensive discussion in Section 2.05.6(3)(b)(iii & viii), Groundwater <br />Quantity Effects, on groundwater impacts including fault system inflows and underground <br />storage of water. There aze no "aquifers" in the current permit azea. Most of the groundwater <br />resulting from primary porosity occurs in small, discontinuous "lenses." Fractures and faults <br />within the stratigraphic column have provided secondary porosity, which contributes the <br />majority of the groundwater into the mine. <br />Most of the groundwater intercepted in the mine is collected, pumped to the surface, treated, if <br />necessary, and released to the North Fork. Until 1996, this treated and released groundwater <br />represented approximately 20 acre-feet of "new" water in the North Fork. This is based on the <br />observation that most of the B Seam dips under the North Fork in a downgradient direction from <br />West Elk Mine. Therefore, dischazges to the North Fork of this "developed water" constitute <br />new water in the North Fork system. In 1996 and 1997, MCC encountered inflows up to 2,500 <br />gpm and 8,000 gpm, respectively, which exceeded the hydraulic capacity of their treatment <br />facilities. This necessitated the subsurface storage of water in previously mined azeas or sealed <br />sumps (see discussion in Section 2.05.6(3)(b)(iii & viii), Groundwater Quantity Effects). <br />Isotope analysis of tritium and cazbon-14 (Mayo 1998) has been used to determine the <br />groundwater "age" (or mean residence time) of the fault water to be at least 50 yeazs (per 3H <br />analysis) and between 5,000 and 20,000 years (per ~QC analysis). This fact, coupled with no <br />known claim of reliance or water rights on these fault inflows, suggests that this water has not <br />been appropriated. MCC has appropriated the fault water and storage rights to these inflows. <br />Water Ri htg s Aspects of North Fork Diversions. Fault Inflows and Sealed Panels Sumps <br />In light of the lazge fault inflows experienced by MCC in 1996 and 1997, in conjunction with <br />MCC's utilization of sealed panels sumps, the following text has been prepazed to summarize the <br />resulting water rights implications. In addition, MCC's historic and recent pattern of diversions and <br />return flows to the North Fork aze described. <br />1.05-178 Revised June 1005 PRIG <br />