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water levels et Yells 6A7 to 6A3 are higher than they would normally be in May through <br />• July of the pest six years due to recently introduced (Nay, 7989) irrigation in that eras. <br />Wells 6A2, 6A3, 6A4, 7A1, and 7A2 all experienced their deepest fell water levels on <br />record (since 7980) due to dry conditions. One alluvial well, 79A, is situated <br />approximately one-half mile downstream of the MPDES 006 pond on a tributary to Mubbe rson <br />Gulch. It also exhibits eeaeonal variations typical of previously mentioned monitoring <br />wells. Monitoring of the two Yatering Trough Gulch alluvial wells (l1A and 9A) has been <br />discontinued as a result of Technical Revision 27, approved February 17, 1994. <br />Eight additional alluvial wells were added to the monitoring program in October, 7997. <br />Yell 20A is situated immediately above the MPDES 005 Pond and has been dry since <br />monitoring began. Yell 27A is situated next to the lower Sage Creek flume site <br />(SY-S2Y-FG4). Yells 22A and 23A are situated on tributaries to Sage Creek (MPDES 009 end <br />South Tributary drainages, respectively). Yells USGS A1, A3, A8 and A12 are old United <br />States Geological Survey alluvial wells situated along upper Sage Creek and are also e <br />part of gCC's proposed Toast Mine monitoring network. Mater level measurements for all <br />eight wells are required twice a year (most Yells et Seneca II-V ere measured five times a <br />year). Yells 21A, 22A, 23A, and USGS At, A8 and A72 all exhibit typical seasonal <br />• variations. Seasonal variation at Yell USGS A3 is masked by local recharge from ponded <br />water in Sage Creek created by adjacent beaver dams. <br />Wadge Overburden. Most Yedge overburden wells (unless noted) exhibit seasonal variations <br />typical of the overburden aquifer (i.e., shallow in the spring or summer, deepening in the <br />fall). Yell 160V exhibits very little seasonal or annual veri etions. Yell 770V exhibited <br />deepening water levels throughout 7994. Since hydraulic communication is suspected <br />between this well and Pond 006, deepening well water levels may be the result of lower <br />water levels in Pond 006 as a result of dry condi[ions. <br />Wedge Coal. Madge coal wells exhibit the same typical seasonal variations (unleea <br />otherwise specified) noted as the previous aquifers discussed. Due to low aquifer <br />transmissivi ties (range 0.07 to 0.36 ft2/day), water semplinB may mask normal water level <br />fluctuations. Mater levels in ell walla in 199< were within their historic rengea. <br />Yolf Creek Coal. Yell 77VC exhibited the •eme aeaeonel variability es noted previously. <br />Neither well exhibitcd water levels outside the rengea previously observed, nor do they <br />• exhibit any long-term discernible trend. Melt 3YC did not exhibit any recharge in 1994, <br />moat likely ss s result of dry eond(tions. <br />3 <br />