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-2s- <br />Existing surface water monitoriny data taken at the mine over the past <br />two years indicates that suspended sediment levels downstream of the mine <br />are equal or lower than the upstream monitoring site about 50% of the <br />time. This shows, in part, that the sediment control system is <br />functioning. <br />The sediment ponds themselves have the potential of affecting water <br />quantity. Ponds may impound water that otherwise would be available to <br />the receiviny stream. The total amount of water to be impounded at the <br />mine area is only 5.6 acre-feet. This amount is 0.0005% of the total <br />flow in Thompson Creek (12,100 acre-feet/year). However, the Division <br />still requires the operator to dewater the ponds within 72 hours as a <br />mitigation measure to water rights holders downstream. <br />The underyround mine workings generate water that may, in part, be <br />tributary to the North and f4iddle Thompson Creeks. Part of this water is <br />consumed by the operation and part is discharged back into the North <br />Thompson Creek. This aspect of the operation may cause several potential <br />surface water impacts. <br />Assuming all inflows in the mine are from stream flows (a conservative <br />assumption), the amount of water depleted from North and Middle Thompson <br />Creeks from Mines No. 1 and No. 3 combined is 0.3 cfs. This is, at <br />present, a worse-case approximation. Future monitoring should show the <br />depletion to be less than predicted. <br />Assuming all mine inflows come solely from North Thompson Creek and <br />assuming all water is consumed (a conservative approach), depletions <br />would amount to 217 acre-feet/year, or U.3 cfs averaye discharge (see <br />Table 4). This is only a mean annual reduction of less than 1% of flow. <br />However, the effect of this reduction is more severe during low flows. <br />The one-day low flow of record (13 years of data) on the Lower Thompson <br />Creek is 1.5 cfs (9/]/54). For this extreme, a 20% reduction of flow <br />will be experienced. Insufficient data is available to establish the <br />frequency of this event. The average daily year low flow of record is <br />2.36 cfs. For this flow, a 13% reduction would be experienced. This <br />short-lived depletion is not predicted to cause any material damage to <br />the stream. <br />The mine water being discharged at present to North Thompson Creek has <br />ionic characteristics that differ from the natural stream levels. The <br />discharge is predicted to shift the ion balance in North Thompson Creek <br />from its present calcium-bicarbonate type to acalcium-sulfate type. The <br />magnitude of this shift, however, cannot be quantified, since the <br />receiving stream will tend to dilute the effect. Assuming a mean annual <br />low flow of 2.36 cfs and a maximum discharge of 0.3 cfs from the mine <br />(13% of total flow), the dilution ratio would be 8 to 1. This shows that <br />a near or complete shift in the ion balance, even during low flows, in <br />unlikely. No standards have been set for these ionic changes. However, <br />it is known that sudden changes of high magnitude can affect fish and <br />other aquatic life. In this case, however, no significant changes are <br />anticipated. Past monitoring data at the mine shows only a slight <br />increase in sulfate levels downstream from the mine. <br />