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Permit C-81-071 1995 Annual Hydrology Report <br />• The dissolved solids concentrations in the upstream station of Fish Creek (16) are generally <br />slightly lower than those in the downstream station (1002). There is also a slight downstream <br />trend of increasing sodium and sulfate concentrations while calcium, magnesium and <br />bicarbonate concentrations remain fairly consistent. The proportionally higher sodium <br />concentrations over calcium and magnesium leads to a slight downstream increase in SAR. <br />These major ion changes are more apparent during the low-flow period. The increase in TDS <br />could be caused to some extent by evapotransporative effects, but this would not account for <br />the major ion changes. These changes are more likely attributable to discharges of waters <br />having higher sodium and sulfate concentrations than the Fish Creek water. One source of <br />such discharge is the spoil runoff and springs associated with Mine 2. However, the very low <br />flows associated with the Mine 2 disturbed areas indicates minimal influence from this source. <br />The primary source of such water at this time is the underground mine discharge point located <br />near Mine 2. <br />Since 1987, except for a short period during 1990, the salt content of Trout Creek below Middle <br />Creek has been consistently higher than above Middle Creek. Typically, there is approximately <br />100 to 200 umhos/cm increase in field conductivity over this reach. The downstream increase <br />was apparent during the spring runoff period. The Trout Creek salt content increases during <br />the spring runoff. This is probably due to the effects of Middle Creek flows that have a higher <br />salt content than Trout Creek primarily as a result of Foidel Creek which flows into Middle <br />Creek just upgradient of the Trout Creek confluence. Foidel Creek salt loads during the Spring <br />runoff are primarily due to the impact of surface mine discharges. However, the Trout Creek <br />salt content increase has not caused material damage, nor is there any increase in trace metal <br />• levels <br />SPOIL SPRING MONITORING <br />A spoil spring monitoring program was initiated in 1986 and will be conducted annually until <br />such time as the monitoring requirement is eliminated. According to the approved plan, the <br />annual mine-wide survey is conducted during May, and springs are measured for flow and field <br />parameters. If a spring is discharging 35 gallons per minute or greater than it is monitored <br />throughout the remainder of the year in accordance with the monitoring plan. <br />Flow <br />The field data of the 1995 spoil spring monitoring program is presented on Table 47. A plot of <br />the historic flow data for Station 114 is presented on Figure 44. Due to pumping of Site 114 for <br />supply water by Twentymile Coal Company, the spoil spring did not discharge for the 1995 <br />water year. Only one significant spoil spring at Mine 2 (a composite of two springs) was <br />observed in 1995 and it had a conductivity of only 1040 umhos/cm. Seven additional springs <br />with flows greater than 35 gpm were recorded at Mine 1 and Eckman Park. The flow data <br />indicates that the spoil springs follow the same pattern as the surface runoff: very low flow <br />during most of the year and a very rapid increase in flow during the spring runoff followed by a <br />moderately rapid decrease in flow. <br /> <br />EPSTE%T DOC 03/17/97 Page 6 <br />