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<br />INTRODUCTION <br /> <br />An unusually heavy snowpack in the Colorado's southern San Juan mountains <br />during the winter of 1992/1993, resulted in the second largest spring run-off in <br />the Dolores River basin since McPhee Reservoir became operational in April 1984 <br />(see Table 1). In late-November 1992 the U.U. Bureau of Reclamation -Durango <br />Projects Office (USBOR-DPO) determined the bottom outlet gates in McPhee Dam <br />needed maintenance that required removal. Moreover, use of the surface spillway <br />gates would be required to control the rate of filling of McPhee Reservoir once <br />the spring run-off began. <br /> <br />Use of the spillway gates began in mid-March and continued until late May <br />1993, when repair and reinstallation of the bottom release gates had been <br />completed. The managed spill (through the bottom outlet gates) continued into <br />the first week in July. Large blocking seines were installed in McPhee Reservoir <br />in front of the spillway gates a few weeks after the surface spill began to <br />minimize escapement of fish from the reservoir into the river below. However, <br />it was suspected that some fish from the reservoir would escape over the spillway <br />or through the bottom outlet works during the managed spill. <br /> <br />In order to assess the level of fish escapement from McPhee Reservoir into <br />the Dolores River downstream, the USBOR-DPO requested that the Colorado Division <br />of Wildlife (CDOW) cooperate in an extensive electrofishing survey of the river <br />below the dam. The primary purpose of the survey was to assess the distribution <br />and abundance of fish species in the Dolores River from McPhee Dam to the Dove <br />Creek Pump Plant, some 30 river miles downstream. This report summarizes the <br />results of that survey. <br /> <br />Table 1. Dolores River flow regime cubic feet/second (cfs) below McPhee <br />Reservoir versus acre-feet (AF) inflow/water year, 1984 to 1993. <br /> <br /> Winter flows" Spill period & range Summer flowsb <br />Water Inflow <br />year AFxlOJ Mean Range Dates Range Mean Range <br />1984 580.3 -- 4/10-7/2 700-3825 172 54-656 <br />1985 611.0 167 32-1065 4/1-6/25 187-3700 69 50-187 <br />1986 572 .3 59 49-100 4/2-6/23 600-4461 131 77 -501 <br />1987 589.2 223 71-600 4/4-6/27 600-3324 163 46-269 <br />1988 259.2 78 70-83 5/2-6/7 194-1201 79 77-81 <br />1989 263.1 79 49-81 4/6-5/14 440-1001 82 70-107 <br />1990 142.5 69 20-80 -- 0 35" 20-75 <br />1991 293.0 31 27-39 5/13-5/27 125-800 61 33-71 <br />1992 351. 9 32 .29-38 - 4/15-6/19 151-3009 75 55""'102 <br />1993 598.2d 85 30-680 3/17-7/5 126-4140 132d 90-643 <br />W~nter tlow data ~s tor October T - March .31 tor water year. <br /> <br />b Summer flow period data is for July 1 - September 30. <br />o Summer flow period for 1990 is April 1 - September 30. <br />d Estimated for 1993 water year, 10/1/92-9/30/93. <br /> <br />METHODS <br /> <br />Except for the reach of the river between Bradfield Bridge and the BLM raft <br />launching area (approximately 0.5 river miles), the entire river from the USFS <br />Metaska Day Use Area near McPhee Dam to the Dove Creek Pump Plant was surveyed <br />twice with an electrofishing raft. Electrofishing operations on the river <br />segment from the BLM raft launch site below Bradfield Bridge to the Dove Creek <br /> <br />-1- <br />