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Discharge.-- <br />PLATTE RIVER BASIN <br />06696000 SOUTH PLATTE RIVER NEAR LAKE GEORGE <br />Location.-- <br />Drainage and Period of Record.-- <br />Lat. 38°54'19",Long. 105°28'22". in SW¼ sec. 20, T.13 S., R.72 W., Park County, Hydrologic Unit 10190001, on left bank 700 <br />ft downstream from Elevenmile Canyon Reservoir and 8.2 mi southwest of town of Lake George. <br />963 mi². October 1929 to current year. Monthly data only for some periods. <br />Graphic water-stage recorder and Sutron SatLink 2 satellite monitoring Data Collection Platform (DCP) with Sutron shaft <br />encoder (SE) in a concrete shelter at a 15-foot concrete Parshall flume. Primary reference is an inside tape gage, and there <br />is an enameled staff gage on the right side of the flume at the Ha location. The gage has power and the shelter is heated <br />during cold weather. The gage is owned and maintained by the Denver Water Department. A 10-foot rectangular bypass <br />channel is located beside the upper right wing wall of the 15-foot Parshall flume. The channel is normally kept closed by log <br />stop (boards). At a gage height of 3.40 ft. in the Parshall flume, water reaches the floor of the bypass channel. A Sutron <br />Stage-discharge recorder (SDR) was installed July 8, 2010. <br />Equipment.-- <br />Hydrologic Conditions.-- <br />Gage-Height Record.-- <br />Datum Corrections.-- <br />Rating.-- <br />Discharge.-- <br />Special Computations.-- <br />Remarks.-- <br />Recommendations.-- <br />Natural flow of stream affected by storage variations in Eleven Mile Reservoir (capacity 97,780 acre feet), Spinney <br />Mountain Reservoir releases (capacity 53,651 acre feet), and transmountain diversions from the Homestake pipeline into <br />Spinney Reservoir, Antero Reservoir releases (capacity 22,300 acre feet) and diversions for irrigation and return flow from <br />irrigated areas. Abrupt gage height fluctuations are experienced at this gage when the reservoir is spilling. Prevailing <br />winds cause waves of water to wash over the spillway. The gage is close to the spillway channel and experiences the <br />waves as rises and dips of unpredictable magnitude. <br />The primary record is hourly averages of 15 minute satellite data with chart and SDR back up. The primary record agrees <br />with the chart to within 0.02 ft. The record is complete and reliable without missing values. Instrument calibration was <br />verified by twenty visits made to the gage. One SE adjustment of +0.01 ft was made on May 25, 2010 and was prorated to <br />the last visit. <br />Levels were run on August 8, 2010 using RM4 as a base. The RP was found to be 0.004 ft low (the gage was found to read <br />0.005 high) which is within the allowable limits of 0.02 ft., no correction to the RP was necessary. <br />The control is a standard 15-foot Parshall flume. Shifting is caused by moss and high approach velocities as weir pool is <br />constricted by width and depth. Rating No. 4, dated October 1, 1971, is a standard Parshall flume table, the expanded <br />version was used for the record. The by-pass was not used this year. A rating for the bypass was developed in 1995 and is <br />included in the record. All flow in water year 2010 passed through the 15 foot Parshall flume. Sixteen measurements (Nos. <br />1088 - 1103) were made, ranging in discharge from 52.6 to 290 cfs. Using the USBR Water Measurement Manual, Third <br />Edition, Figure 8-9, Page 8-44, the range of accurate (within +/-5%) discharge measurement for a 15 ft Parshall Flume is 8 <br />to 600 cfs. Anything above or below this range is outside the +/- 5% accuracy range. The 15 ft rating for this flume has <br />been further verified by measurements from 3.97 to 837 cfs. All flows during the 2010 water year were within this accuracy <br />range. The peak discharge of 417 cfs occurred at 1630 on August 10, 2010 at a gage height of 3.41 ft. with a shift of +0.03 <br />ft. It exceeded measurement No. 1099, made on June 18, by 0.69 ft. in stage. <br />Shifting control method was used for the entire year. Measured shifts ranged from -0.03 to +0.03 feet. Shifts were applied <br />as defined by measurements and were distributed mainly by time with some consideration to change in stage. Shifts were <br />applied by as follows. October 1, 2009 to April 22, 2010: time distribution with all measurements given full weight. April 22 <br />to May 5, 2010: time distribution with consideration to stage by applying measurement No. 1095 (May 5) back to peak flow <br />event on April 24, 2010. Measurement 1095 was adjusted 3% to smooth distribution. May 5 to June 18, 2010: time <br />distribution with consideration to stage by applying measurement No. 1099 (June 18) back to a peak flow event on June 15, <br />2010. Measurements 1095 and 1097 made during high wind were adjusted 3% and 1% to smooth time distribution. <br />(Measurement 1097 was a check measurement.) Other measurements were given full weight. June 18 to August 17, <br />2010: time distribution with consideration to stage by applying measurement No. 1102 (August 17) back to a peak flow <br />event on August 4, 2010. All measurements given full weight. August 17 to September 30, 2010: time distribution with all <br />measurements given full weight. When clean, the flume will often show positive shifting, possibly due to approach <br />velocities. Moss growth causes negative shifting. <br />None. <br />The record is considered good. Station maintained and record developed by Mike Wild. <br />Approach conditions to the flume cause velocities greater than 0.5 ft/s in weir pool. Weir pool needs work to slow velocities. <br />2010Water Year