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<br />• <br />u <br />HYDROLOGIC MONITORING ACTIVITIES <br /> <br />The hydrologic monitoring program at the <br />Mt. Gunnison No. 1 Mine was initiated in 1974 <br />with the completion of several groundwater <br />observation wells. This preliminary monitoring <br />network was expanded considerably and in 1981, <br />with the approval of the Mt. Gunnison No. 1 <br />Mine, Mining and Reclamation plan (M and <br />R Plan), became the "approved" hydrology moni- <br />toring program. fn 1984, the hydrology monitoring <br />program was revised, with the approval of the <br />Colorado Mined Land Reclamation Division <br />(CMLRD), to more efficiently monitor possible <br />effects from mining and provide data for future <br />permitting. <br />In 1987, the hydrology monitoring program <br />was revised again, based on anticipated annual <br />coal production figures that have been down- <br />wardly revised. Under the revised program, base- <br />line monitoring in areas that would not be mined <br />for at least several years has been reduced. Con- <br />sequently, the program focuses more closely on <br />coordinating hydrology monitoring with areas <br />being mined to look for possible mining impacts. <br />Sampling periods and parameters were also <br />revised. Beginning with the 1988 water year <br />(1 October 1987 through 30 September 1988), <br />sampling is conducted three times per year instead <br />of quarterly. These three sample periods cor- <br />respond to the start of spring runoff, the peak of <br />spring runoff, and the fall low flow. Sample <br />parameters include pH, conductivity, temperature, <br />total iron, total manganese, total dissolved solids, <br />and total suspended solids. Because this revised <br />monitoring plan was approved by the CMLRD <br />during the 3rd quarter of 1987, the 1988 water <br />year was the first year affected by the revision. <br />This report reflects those changes. <br />The 198$ Annual Hydrology Report contains the <br />following: <br />Data from continuous flow monitor- <br />ing at five stream gauging stations; <br />Data from continuous flow monitor- <br />ing, in cooperation with the U. S. <br />Geological Survey (USGS), at the <br />reconstructed Minnesota Creek Gaug- <br />ing Station site and at the USGS <br />gauge on the North Fork of the <br />Gunnison River near Somerset.; <br />Data from seasonal water quality <br />sampling at two surface water quality <br />monitoring stations: The North Fork <br />Gunnison Rivcr above Sylvester <br />Gulch and the North Fork Gunnison <br />River below the mine; <br />Data from seasonal measurements of <br />pH, temperature, dissolved oxygen, <br />turbidity, and conductivity at the six <br />stream gauging stations in the Min- <br />nesota Creek Basin and Sylvester <br />Gulch; <br />• Data from seasonal measurements of <br />discharge and water quality sampling <br />on seven springs issuing from of <br />below the "F'-seam wal; <br />• Data from seasonal water level and <br />water quality measurements on 19 <br />wells; and <br />Data from measurements of mine <br />water discharges, and mapping of <br />inflow locations. <br />SURFACE WATER <br />MOI~IITORING <br />WECC's surface water monitoring program <br />includes nine monitoring locations (Table 1). The <br />locations of these monitoring stations are shown <br />on Exhibit I. Under the revised monitoring pro- <br />gram, flumes located on Horse Creek, South ~ <br />Prong, and East Fork of Minnesota Creek below S~ <br />Beaver Reservoir have been removed and will no <br />longer be monitored until they are reestablished <br />the summer before mining impacts can be ex- <br />pected in those drainages. Daily flow estimates <br />(including mean, maximum, and minimum flows) <br />for the five WECC gauges are summarized in <br />Appendix A <br />