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Surface water 27 <br />Surface water below the confluence of the east and west forks of Jubb Creek (CJC) is <br />characterized as a magnesium - sulfate water (Figure 4.3). Compared to other stream <br />waters, this water has a higher percentage of sodium. The pH ranged from 8.29 to 8.61, <br />except when the creek was frozen (pH = 7.19). The TDS ranged from 1,590 to <br />1,800 mg /I. Concentrations of Total Suspended Solids (TSS), were below the detection <br />limit of 5 mg /I in all samples. Samples collected by KEC in 1996 and 1997 are very <br />similar to the samples collected during the pre - feasibility study (Appendix 4.C). One <br />interesting time trend observed in the data is the abrupt change in concentrations during <br />the spring runoff, which occurred in May and June in 1997. During this event, <br />concentrations of all ions decreased, although the overall inorganic signature of the <br />water remained the same. Historic data from the upstream East and West Jubb Creek <br />sampling locations (EFJC and WFJC) indicate that the water is very similar to samples <br />from CJC, except for a lower sodium percentage. Between 1997 and the 2004/2005 <br />sampling event, a dam was constructed between sampling locations WFJC and CJC. <br />The water quality in Collom Gulch varied with location and time. At the upstream <br />sampling location (UCG) the water is a calcium /magnesium- bicarbonate (Figure 4.3). <br />Only two samples were evaluated, as the stream was dry during the first two sampling <br />rounds. The inorganic chemistry of the water was very similar in both samples, with a <br />slightly alkaline pH of 8.37 to 8.51. TDS ranged from of 380 to 490 mg /I, with the lower <br />value originating from the sample collected during the March spring runoff. TSS ranged <br />from 200 to 380 mg /l. The chemistry at the downstream sampling location (LCG) is <br />characterized as a calcium /magnesium- bicarbonate (Figure 4.3). The pHs of the <br />samples ranged from 8.21 to 8.35, with the exception of the December 2004 sample, <br />which had a pH of 7.19 and was collected from below 4 inches of ice. TDS ranged from <br />820 to 870 mg /I, with the lower values occurring during the spring runoff in March. TSS <br />ranged from 21 mg /I during the winter to a high of 452 mg /I during the runoff. <br />The water quality in Straight Gulch at both locations (USG and LSG) is a magnesium — <br />sulfate /bicarbonate (Figure 4.3). The inorganic chemistry of the water was very similar <br />for all samples, with a slightly alkaline pH of 8.06 to 8.54. TDS ranged from 830 to <br />1,430 mg /I. TSS ranged from 18 mg /I to 816 mg /I, with the highest concentrations <br />occurring during the runoff. <br />4.5 Springs and seep <br />Springs and seeps were inventoried and sampled in December 2004. As discussed <br />above, the focus was springs and seeps within and downgradient of the proposed mine. <br />Areas in the Collom study area were evaluated where enhanced vegetation and grasses <br />indicated the potential for seeps. Ten spring locations were identified and inventoried. <br />Most of the springs and seeps located by WMC staff had been previously identified <br />during the JBR study conducted for the Collom study area (JBR, 1998). <br />• <br />2572 -R2 <br />Colowyo Coal Company <br />Water Management Consultants <br />