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Dissolved Solids <br />There aze no receiving stream standazds for total dissolved solids. However, the Division <br />considered the additional total salt load on North Thompson Creek. The average (1995 <br />through 2001) September (low stream flow conditions) concentrations of total dissolved <br />solids in North Thompson Creek rose from 138 mg/1 above the mine azea to 222 mg/1 <br />below the mine azea, an increase of 62%. The September 8, 2002 upstream concentration <br />was 140 mg/1 and downstream concentration was 215 mg/1. The concentration of total <br />dissolved solids in Mine No. 1 dischazge of September 8, 2002 was 1580 mg/1. The <br />concentration of total dissolved solids in Mine No. 3 dischazge of the same date was 1140 <br />mg/1. The concentration of total dissolved solids in combined portal dischazge (Outfall <br />001) was 1501 mg/l. Thus Outfall 001 likely contributed to the rise in concentration <br />between the upper and lower stream monitoring stations. Derived from average flow rates <br />and concentrations, the highest level of salt dischazge at Outfa11001 recorded from 1995 <br />through 2002 was 0.4 tons of salt per day (1997). The 2001 contribution was 0.21 ton of <br />salt per day to North Thompson Creek. During 2002, the average flow rate at Outfa11001 <br />was 22.4 gpm and the average TDS concentration was 1,388 mg/1. This equates to a salt <br />loading of 0.19 tons per day to North Thompson Creek. The CDPHE considers anything <br />less than 0.4 ton per day as a no salt dischazge. Annual salt loading at the 2002 rate would <br />be 69.4 tons. <br />Depletion of Springs and Seeps <br />Mining may cause the depletion of springs and seeps above the undermined azeas. A <br />spring and seep survey conducted by the mine has only identified two springs within the <br />five-yeaz mine plan azea. Both springs (designated on the mine subsidence map) flowed <br />less than one gallon per minute, except during the spring, when site SP-2 flows of 20-40 <br />gallons per minute were reported. Both springs flow from the Upper Sandstone and aze <br />not adjudicated. Based on the low flow and poor quality, it does not appeaz that the <br />springs were, or aze, a significant component of the surface water regime. On May 20, <br />2003, the flow of Spring 2 was estimated at 0.125 gallon per minute. Should mining have <br />diminished Spring 2 flows, they would now re-appeaz in Mine No. 1 discharges. There <br />would, thus, not be a significant impact to the surface hydrologic balance. <br />Water Balance <br />There was aone-time loss from the pre-mining hydraulic regime to impounded water of <br />the underground reservoirs from flooding of the areas of coal extraction after pumping <br />ceased. An estimated 363 acre feet in Mine No. 1 and 94 acre feet in Mine No. 3, are <br />stored. Dischazges from the Mine No. 1 portal were noticed on Apri128, 1988, and from <br />the Mine No. 3 portal on June 26, 1995. Since these times, mine inflows have been in <br />balance with mine discharges. There maybe some increase to North Thompson Creek <br />surface flows from diversion of upper groundwater to the portal dischazges at the expense <br />of underground recharge of aquifers. Although it is not likely that all of the mine <br />discharge water originates in the aquifers, even this maximum dischazge would not <br />29 <br />