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Colowyo Coa[ Company L.P. <br />Neilson Pit <br />• Neilson Pit, into the underlying bedrock. Any water that recharges the bedrock units <br />tends to accumulate along unit contacts since these tend to be areas of least flow <br />resistance. <br />Any groundwater that has been discharged from the mine highwall has been found to <br />evaporate from the pit floor or be consumed by pit highwall. Past hydrological studies <br />also reveal the mined units tend to have low permeabilities (even the sandstones) and do <br />not allow for large water movement, even if the groundwater is present. This is also the <br />case where the groundwater is under confined or unconfined conditions (i.e. below the <br />elevation of the valley bottoms). <br />If any groundwater does percolate vertically through the discordant geologic units, it <br />encounters a tonstein bed near the base of the Williams Fork Formation. This bed is <br />approximately 150 feet above the top of the Trout Creek Sandstone and is approximately <br />400 feet below the bottom of the active pit. The tonstein bed has an approximate <br />thickness of 2.5 feet. Permeability tests of this material show it has penneabilities greater <br />than 1x10'10 centimeters per second. Thus, this bed is an effective aquiclude and prevents <br />downward movement of any groundwater to the underlying Trout Creek Sandstone. <br />All surface water runoff is contained at the base of the Neilson Pit by a ditch and small <br />containment area. The ditch runs north to south below the entire Neilson Pit and directs <br />all surface runoff to a small containment area at the north end of the disturbance area. <br />• This ditch will be maintained to catch all surface water runoff from exiting the <br />disturbance area. Furthermore, any runoff that flows down the access road to the <br />Neilson Pit is contained in a ditch on the north side of the road to contain and transfer <br />runoff to Colowyo's existing ditches and containment sumps <br />Water Quality <br />The quality of the water in the azea of the Neilson Pit has been rated as poor by the USGS <br />and designated for limited agricultural use. Since USGS testing in 1978, no water quality <br />analysis performed at monitoring points at the adjacent Colowyo Coal Mine have shown <br />any significant difference in water quality compared with what the initial USGS work. <br />The water is slightly saline, alkaline and definitely classified as `hard' water. This can be <br />seen in the water quality measurements for total dissolved solids (TDS) and electrical <br />conductivity (eC). Both TDS and eC exceed the EPA secondary drinking water <br />standards. <br />Since the water is alkaline, the pH is above 7, but rarely exceeding 8.4. Concentrations <br />of heavy metals rarely exceed health limits, as stated in the USGS report. This has also <br />been confirmed by the shallow groundwater monitoring performed since the Neilson Pit <br />began operation. <br />Conclusions <br />The Neilson Pit has no single or multiple continuous geologic units in the mine that <br />contains groundwater under unconfined or confined conditions. The only groundwater <br />encountered is the discontinuous perched pockets of groundwater. This lack of <br />5 <br />