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West Elk Mine <br />Groundwater Quality Characteristics <br />Groundwater Quality <br />MCC has selected the water quality parameters listed in Table 7 for baseline laboratory analysis to <br />chazacterize baseline and ongoing groundwater quality. These include iron and manganese, <br />because the detection of these elements (or changes in their observed concentrations) may represent <br />conditions in which metals are mobilized. Additionally, changes in conductivity and TDS can <br />indicate changes in water quality that need to be further investigated. As a result, monitoring of <br />these selected parameters provides a detection system for mining-induced changes in water quality. <br />Therefore, once full-suite analyses have been collected at a site for at least five yeazs, these indicator <br />parameters (pH, conductivity, TDS, and iron) will be collected on an annual basis. <br />Analyses aze completed as outlined in the Guidelines for Collection of Baseline Water Quality and <br />Overburden Geochemistry Data (CDMG, 1982). Results are reported in the Annual Hydrology <br />Reports (AHR). If not already provided in AHR's, baseline data will be provided to CDMG prior to <br />longwall mining under or within the angle-of--draw of a monitored water resource. <br />Reeional Groundwater Quality <br />Data collected on groundwater quality from representative wells within the permit area are <br />summarized in Table 7. As this table shows, the highest average levels of TDS are in well SOM-3B <br />and 03-11-1 as completed in the B Seam coals. This is consistent with the elevated TDS <br />• concentrations in other B Seam wells such as SOM-129-H and JMB-12. The highest average total <br />and dissolved iron concentrations occur in wells SOM-3B and SOM-3E. These wells also produce <br />the highest average manganese values as well. The water chemistry results from these two wells <br />demonstrate a striking similarity between the B and E Seams. This is consistent with the geologic <br />(depositional and lithologic) similarities noted in Section 2.04.6 (Geology Description). The <br />relatively high levels of iron in groundwater (Table 7) are consistent with the levels found in surface <br />water (Table 19) and indicate some groundwater discharge to the streams and a similazity in terms <br />of geology. <br />The only applicable water quality standards for the parameters monitored are secondary drinking <br />water standards. Compazison of these standards to groundwater quality data show numerous <br />dissolved iron exceedances and routine pH levels above 8.5 in three groundwater wells (SOM- <br />38-H-1, SOM-2, and SOM-16). However, the causes of elevated levels of these parameters are <br />natural and not due to mining activities. <br />Seasonal Variations in Groundwater Quality <br />Data from selected wells in the permit area with relatively long records covering different seasons <br />were evaluated for seasonal trends. In general, the parameters evaluated do not exhibit defined <br />seasonal changes in concentration. Levels of TDS, TSS, and pH do not vary appreciably over the <br />yeaz. This is due to the poor aquifer chazacteristics of the formations in the permit azea and lack of <br />recharge and connection to surface water sources. <br /> <br />7.04 -74 Revised Nwember7004 PR/0 <br />