Laserfiche WebLink
The applicant has also addressed the changes in ground water quality due to <br />the proposed mining operations. When water passes through spoil piles the <br />potential exists for changes in the water's quality. Studies on the Williams <br />Fork and Fort Union formations have shown that effluent water will contain <br />dissolved solids concentrations ranging from 1 to 2 times that of saturated <br />overburden extracts. The applicant prepared saturated extracts from composite <br />grab samples taken from 3 cores in the Laramie formation, The results of the <br />saturation extracts revealed an acreage TDS concentration of 450 my/1. From <br />that we would predict the spoil water quality to be 1-2 times this, or 4500 = <br />9000 my/l. Baseline water quality data for the overburden aquifer revealed a <br />TDS concentration of 7,000 my/1. Actual spoils water quality data collected <br />in Decerr~er of 1985 revealed a TDS concentration of 6900 nU'/l. This indicates <br />that the spoil water TDS concentration is similar to baseline and about 1.5 <br />times the concentration predicated by the saturation extract. THis°shows that <br />spoil water will not degrade Ennis draw above baseline levels. <br />The final impact considered by the applicant was the potential for changes in <br />the recharge capacity of the Laramie overburden. The baseline investigation <br />of recharge capacity revealed that very little recharge to the Laramie occurs <br />at the mine site. This can be attributed to the water holding capacity of the <br />thick layer of overlying blow sands. Although the hydraulic properties of the <br />spoil are difficult to predict, the high clay content of the Laramie formation <br />suggests that the hydraulic conductivity of the spoils will be close to <br />baseline conditions. The effect of replacing only 4 feet of sand over the <br />reclaimed areas may suggest that an increase in recharge will occur. However, <br />the soil studies in Appendix L display field studies that show a 1'.9 inch <br />rainfall event only penetrated 28 inches into the sand. Based on the above <br />facts and predictions, the Division finds that the recharge rate will not be <br />significantly changed by the operation. Any potential increase in the <br />recharge rate should not significantly affect the hydrologic balance provided <br />the water quality predictions are sound. The ground water monitoring program <br />is designed to verify the hydrologic projections and identify any unforeseen <br />impacts to the hydrologic balance. <br />Monitoring: <br />The Coors Keenesburg Mine has collected extensive baseline water quality and <br />water quantity data since 1978. These baseline data are used to compare with <br />present day impact assessment monitoring. The overburden, coal, Laramie-Fox <br />Hi11s, Aeolian and Ennis Draw aquifers are monitored on a regular basis, <br />Currently 9 wells are monitored in these aquifers. With the exception of one <br />well, all are monitored for field and full suite parameters at regular <br />intervals. Water monitoring and analysis procedures are discussed on pages 56 <br />and 57 bb of the permit application. <br />Sampling proceaures at this mine have been observed to be of high quality. <br />Water level measurements are accurately taken. Wells are evacuated at least <br />one volume with a submersible pump before a sample is taken and samples are <br />refrigerated and transported to a lab within 2 days. <br />The original permit approval contained a stipulation which required the <br />submittal of an annual hydrologic report. The Division believes that analysis <br />of the collected monitoring data is necessary to determine the extent of <br />impacts of mining on the hydrologic balance. <br />_12_ <br />