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ENVIRONMENTAL ASSESSMENT <br /> Surface Water Resources <br /> Surface water resources within the area encompassed by the King II Mine and its associated CIAA for <br /> water resources include drainages classified as ephemeral and intermittent by OSMRE (2017). Ephemeral <br /> streams flow only in response to precipitation events or snow melt and include East and West Alkali Gulch <br /> which cross the King II Mine underground workings and are tributary to Hay Gulch below Mormon <br /> Reservoir. The Gulch parallels the western boundary of the permit area and separates the King II mine <br /> workings from the Project Area to the west. The Gulch is an intermittent stream with a portion of the <br /> stream drainage below the water table, allowing for flow in a segment of the stream over part of the year <br /> derived from groundwater. <br /> Because of the lack of perennial streams in the Project Area and the CIAA, quantification of surface water <br /> is limited to storm events or flow in irrigation ditches (OSMRE 2017).The Hay Gulch Ditch is a year-round <br /> diversion from the La Plata River and showed a range in flow rates from 0.28 to 1.5 cubic feet per second <br /> (cfs) during the period from April 2016 to March 2017. The typical flow rate was on the order of 1.0 cfs <br /> (OSMRE 2017). To date,there are no water quality data on storm water runoff.The Hay Gulch Ditch water <br /> is sodium/calcium bicarbonate water with a pH of 8.2,total dissolved solids(TDS)of 100 to 700 mg/L(RHS <br /> 2017); most constituents are below drinking water standards(RHS 2017).Water in the Mormon Reservoir <br /> is calcium/magnesium sulfate water with a pH of 7.8, and a TDS ranging from 1,000 to 1,500 mg/L due to <br /> evapo-concentration (OSMRE 2017). <br /> Ground Water Resources <br /> Groundwater in the Project Area and the CIAA is found in the alluvium of Hay Gulch and in bedrock <br /> geologic units in the Cliff House Sandstone, the Menefee Formation, and the Point Lookout Sandstone <br /> members of the late Cretaceous Mesa Verde Group. <br /> Alluvial Groundwater <br /> Alluvial groundwater is present in the Hay Gulch alluvium and in some of the unconsolidated alluvial <br /> sediments that fill topographic lows in the ephemeral stream systems. Hay Gulch has groundwater that is <br /> sufficient in quantity for agricultural and stock water use during the summer months. Groundwater in the <br /> alluvial aquifers is generally unconfined (RHS 2016a). Groundwater in the La Plata River alluvium along <br /> the eastern margin of the CIAA is tapped by hundreds of domestic wells that yield up to 65 gallons per <br /> minute (gpm) (RHS 2016a). Groundwater in the Hay Gulch alluvium is found in the upper 100 ft of the <br /> alluvium and yields water on a seasonal basis for agricultural and stock water use at variable rates <br /> generally below 30 gpm. Groundwater in the alluvium of The Gulch exhibits spatially limited saturation <br /> and is highly variable depending on seasonal precipitation. Groundwater in the alluvium of Cherry Creek <br /> along the eastern margin of the CIAA yields water to domestic wells at rates up to 30 gpm (OSMRE 2017). <br /> Alluvial groundwater quality has been monitored for several years by GCCE along Hay Gulch and varies <br /> both spatially and temporally. In general, the pH of alluvial water is in the range of pH 7.0 to 8.0. TDS is <br /> highly variable and generally ranges from 400 to 800 mg/L but can be as high as 1,480 to 1,580 mg/L in <br /> the Wiltse Well (RHS 2016b; 2017). Sulfate can range from 400 to 800 mg/L. Most alluvial water samples <br /> exceed the drinking water standard of 500 mg/L for sulfate but have trace metals within drinking water <br /> standards (RHS 2017). <br /> Dunn Ranch Area Coal Lease by Application COC-78825 and Mine Plan Modification EA 3-13 <br />