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The Minnesota Creek drainage extends approximately <br /> 53.5 square miles (Figure 2) . The West Elk life-of-mine <br /> area is drained by five tributaries to Minnesota Creek_ <br /> These tributaries include East Fork, Horse Creek, South <br /> Prong, Lick Creek, and Dry Fork. Characteristics of the <br /> drainages are given in Table 3 . Lick Creek and Dry Fork <br /> average slopes are generally steeper and the watersheds are <br /> at higher elevations than those tributary to the North <br /> Fork. Based upon streamflows measured in water year 1978, <br /> the water yields from these drainages are nearly an order <br /> of magnitude greater than that from Sylvester Gulch. <br /> The evaluation of flow within the Minnesota Creek drainage <br /> can only be considered an approximation due to infiltration <br /> and seepage losses, seasonal variations in precipitation <br /> and potential evaporation and sampling difficulties. <br /> Nevertheless, approximately 1,000 acre-feet is annually <br /> transferred from the Little Gunnison Creek to the Dry Fork <br /> of Minnesota Creek, and the average annual flow of the East <br /> Fork of Minnesota Creek is approximately 19,921) acre-feet. <br /> Irrigation ditches annually remove about 20,001) acre-feet <br /> from Minnesota Creek. <br /> Two reservoirs are located within the Minnesota Creek <br /> drainage. Minnesota Reservoir is located on the Dry Fork. <br /> It has a decreed capacity of 1,285 acre-feet, but the <br /> actual capacity may be closer to 500 acre- feet_. Beaver <br /> Reservoir is located on the East Fork of Minnesota Creek <br /> and has an absolute decreed capacity of 1,620 acre-feet and <br /> a conditional decree of 522 acre- feet. Both reservoirs <br /> store water for irrigation purposes and are filled during <br /> spring :-=off. They are usually drained by late August or <br /> early September. <br /> Water quality data have been collected at several sites <br /> throughout the Minnesota Creek drainage. The data indicate <br /> that these waters are of a calcium bicarbonate type with <br /> relatively low total dissolved solids concentration. <br /> Minnesota Reservoir appears to have an effect on the water <br /> quality characteristics of Dry Fork. Detention of Dry Fork <br /> flows in the Minnesota Reservoir results in a decrease in <br /> total suspended solids (TSS) or turbidity, a slight <br /> increase in temperature, dissolved oxygen (DO) , and total <br /> dissolved solids (TDS) . The increase in TDS is most likely <br /> a result of evaporation losses. There is a slight increase <br /> in alkalinity and, as a result, a slight increase in pH. <br /> In all :Likelihood, these changes are also a result of <br /> evaporation losses. All of the changes in water quality <br /> observed are what would be expected as a result of <br /> impounding water in a shallow reservoir in a semi-arid <br /> climate. <br /> There are over a hundred (100) springs located throughout <br /> the Wes- Elk study area. Measurements indicate that spring <br /> flows generally decrease from a high in the early summer to <br /> a low in the fall. A number of the springs are ephemeral, <br /> indicating that their sources are small localized aquifers <br /> (i .e. landslide deposits, colluvium, lenticular sandstones, <br /> etc. ) . There are a total of nineteen (19) decreed spring <br /> water rights on or near the West Elk permit area. <br /> 2 . Probable Hydrologic Consequences of the west Elk Mine <br /> A determination of the probable hydrologic consequences of the <br /> proposed mining and reclamation activities at the West Elk Mine <br /> 24 <br />