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• TABLE 7 Comparison of GP - t Baseline and 1989 Sampling Results, Gunnison No. 1 Mine <br /> Sampling pH Conduct. TDS Temp. Fe Mn <br /> Date Turbidity (units) (µmhos) (mg/L) (°C) (mg/L) (mg/L) <br /> 08/08/85 048 7.5 990 566.0 10.1 <0.02 0.21 <br /> 08/08/85 <br /> (Dup) 048 7.5 990 526.0 10.0 <0.02 0.21 <br /> 10/10/85 054 693 870.0 7.5 <0.02 0.05 <br /> 05/01/89 006 7.0 922 558 8.7 <0.02 <0.01 <br /> 06/05/89 025 7.6 980 554 10.5 <0.02 <0.01 <br /> 09/06/89 029 6.5 957 546 8.8 3.60 0.09 <br /> casing was apparently damaged by • The shallow subsidence monitoring <br /> subsidence as described earlier in wells, SW-I through SW-6,were gen- <br /> this section. erally the same as in previous years. <br /> • Barren Member well 38-H-3 provided Lower Refuse Pile <br /> • no useful well data in 1989. Moisture <br /> problems with the casing and later During 1989, mine development waste from the <br /> communication with the mine work- underground mining operations was placed in the <br /> ings, probably caused by subsidence, lower refuse pile. The lower refuse pile was per- <br /> precluded the determination of water milled for permanent disposal of some 1.7 million <br /> levels. cubic yards of mine development waste, coal <br /> processing waste, and sediment pond cleanoui <br /> • Barren Member well B-32 exhibited material. In 1989 approximately 46,922 tons <br /> virtually no response to seasonal in- (42,000 cu. yd.) were placed in the lower refuse <br /> fluences which indicates no apparent pile in the phase III and IV areas. <br /> connection to surface recharges. <br /> Table 7 shows the 1989 sampling results from <br /> monitoring well GP-1 as well as baseline data from <br /> • "F'-seam wells SOM-2, and SOM-16 the well. The sample results indicate the lower <br /> show no seasonal or annual fluctua- refuse pile is not impacting the groundwater zone <br /> lion and have little or no surface near Sylvester Creek. Due to the low permeability <br /> water connection. of the colluvial soil and the lack of a groundwater <br /> table near the surface in the colluvium (except <br /> • Barren Member wells SOM-13 and along the margin of Sylvester Creek),no significant <br /> SOM-80 have shown seasonal varia- future impacts to the groundwater regime arc <br /> tions in previous years. During 1987, anticipated. <br /> SOM-80 showed very little or no <br /> response to seasonal fluctuation while Conductivity and TDS from samples of monitoring <br /> SOM-13 was similar to previous years. well GP-1 were closely monitored because conduc- <br /> In 1988 and 1989,neither well showed tivity was slightly higher than the baseline samples <br /> response to seasonal fluctuation. in some instances during 1986. However, this does <br /> • <br /> 11 <br />