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level measurements. Time series plots of selected parameters (pH, nitrate, and sulfate) <br />for GRMW -1A, GRMW -2A, and GRMW -3A are provided in Figure 5 -6. <br />5.3.4.3 Discussion <br />Ground water levels in GRMW -1A, GRMW -2A, and GRMW -3A are shown on Figure 5- <br />6. The ground water levels in GRMW -1A, GRMW -2A, and GRMW -3A vary from 144 <br />to 149.34 feet bmp, 54.1 to 76.98 feet bmp, and 139.21 to 158.78 feet bmp, respectively. <br />The hand measured data for GRMW -2A show 0 -2 water level peaks per year. The timing <br />and magnitude of the peaks for the shallow monitor well is likely related to the melting <br />and infiltration of the snow in the spring months and the precipitation events in the <br />summer and fall months. The hand level measurements for the deeper monitor wells <br />GRMW -1A and GRMW -3A show relatively stable water level conditions. A <br />comprehensive analysis of the horizontal and vertical ground water flow and ground <br />water gradients in the Diatreme and the adjacent granites for the Cresson Project area, <br />and specifically Grassy Valley is presented in "Cresson Project Hydrogeochemical <br />Evaluation" dated February 2012 and prepared by ABC. <br />Field and water quality conditions for GRMW -1A, GRMW -2A, and GRMW -3A are <br />provided in Tables 5 -9, 5 -10, and 5 -11. Time series plots for pH, nitrate, and sulfate are <br />provided in Figure 5 -7. Shallow bedrock and deeper bedrock ground waters in Gold Run <br />drainage at GRMW -1A and GRMW -2A are characterized as calcium- sulfate waters. <br />Deeper bedrock ground water at GRMW -3A is characterized as calcium- bicarbonate <br />waters. Data in Tables 5 -9, 5 -10, and 5 -11 show median pH values of 6.84 SU, 7.01 SU, <br />and 7.41 SU for GRMW -1A, GRMW -2A, and GRMW -3A, respectively. Median nitrate <br />values were <0.05 mg/L as N for all three monitor wells. Median sulfate values were 691 <br />mg/L, 1726 mg/L, and 184 mg/L for GRMW -1A, GRMW -2A, and GRMW -3A, <br />respectively. Figure 5 -7 shows relatively stable conditions for all three parameters. <br />Compiled data and statistics for aluminum, manganese, and zinc, which are common <br />geochemical indicators in the Diatreme, are provided in Tables 5 -9, 5 -10, and 5 -11. The <br />water quality data indicate relatively stable and low concentrations for aluminum, <br />manganese, and zinc at GRMW -1A and GRMW -3A from 1998 -2001 and in 2011. The <br />water quality data indicate relatively stable and low concentrations for aluminum and <br />zinc and stable and elevated concentrations of manganese at GRMW -2A from 1998 -2004 <br />and in 2011. Other trace metals are analyzed as part of the monitoring program. Median <br />values for arsenic (except GRMW -1A), cadmium, chromium, copper, lead, mercury, <br />'Cripple Creek & Victor Gold Mining Company <br />Cresson Project Hydrologic Evaluation for Mine Life Extension 2 <br />22 <br />