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Flows on Sage Creek range from intermittent to perennial, depending on location and precipitation <br /> patterns. At the Seneca IIW monitoring sites, Sage Creek can be classified as perennial during years <br /> at or above average precipitation,and intermittent in years below average. The numerous small <br /> drainages tributary to Dry Creek are ephemeral in nature. Hubberson Gulch, downstream of the <br /> mine site to its confluence with Dry Creek, is intermittent. Dry Creek, like Sage Creek, can be <br /> classified as perennial most years, and intermittent during years with below average precipitation. <br /> Both Sage Creek and Dry Creek confluence with the Yampa River near Hayden, Colorado. <br /> Water in Hubberson Gulch is a MgCa-SO4 type. Surface water total dissolved solids (TDS), <br /> averages 820 mg/l. The water is hard, and is characterized as slightly alkaline (average pH 8.1). It <br /> is suitable for livestock watering and irrigation of salt tolerant crops grown in well drained soils. <br /> Water quality in Sage Creek is a CaMg-HCO3 type. Samples from baseline monitoring points <br /> indicate the water is slightly alkaline with a pH ranging between 7.0 and 8.0. The water has a TDS <br /> level of less than 500 mg/l, and is characterized as very hard. It is suitable for livestock and <br /> irrigation; however, flow is generally inadequate for irrigation. <br /> Dry Creek water quality is categorized as brackish, since the TDS level averages greater than 1000 <br /> mg/1 (1048 mg/1) near its confluence with Hubberson Gulch. Water quality degrades further <br /> downstream. With an average pH of 8.3, the water is slightly alkaline. Hardness averages 796 <br /> mg/l, and is considered very hard. <br /> Information pertaining to water rights comprises Tab, 16 Protection of the_ydroloLic Balance, of the <br /> permit application. All water rights in the area of the operation are listed in Table 16-1, and <br /> approximate locations are mapped on Exhibit 16-1. Attachments 16-A and 16-B are water rights <br /> studies performed for Seneca Coal Company. <br /> There are three adjudicated water sources within the permit area. The Temple Pond No. 2 and the <br /> Temple well No. I were destroyed by mining. SPL executed an agreement with the water right <br /> owner(s) to replace these two sources by leaving Pond 006 as a permanent impoundment. The <br /> Frank Temple Stock Pond is an adjudicated water source also destroyed by mining of the north pit, <br /> and SP has arranged to leave Pond 005 as a permanent replacement water source. <br /> SPL has an augmentation plan approved by the Water Division 6 Water Court to replace any other <br /> sources which may be impacted, and to provide supplies when a call is placed on Dry Creek by <br /> senior water users. The plan also approved a well permit for the operation's Trout Creek Sandstone <br /> water supply well. <br /> Climate <br /> The average annual precipitation at the mine site is approximately 16 inches. The mean annual <br /> temperature is 42°F. The average maximum and minimum temperatures are 66°F and 17°F <br /> respectively. Regionally, wind directions run east to west following the Yampa River Valley. <br /> More localized wind patterns trend along the side valleys. <br /> Land Use <br /> The current and historic land uses of the area comprise grazing land for livestock and habitat for <br /> wildlife. Regional land use patterns are oriented in three relatively distinct bands. Irrigated cropland <br /> is closely associated with the floodplain of the Yampa River. To the south, non-irrigated crops are <br /> grown on the sloping upland surfaces. The area nearest the mining operation includes hilly and <br /> mountainous terrain, utilized primarily as rangeland for livestock grazing and wildlife habitat. Land <br /> use in the mine area is undeveloped rangeland, with a small area classified as industrial due to an <br /> oil well site. <br /> Page 7 of 37 <br />