Laserfiche WebLink
<br />initiated during this time. The runoff produced from <br />precipitation in the study area shows at the Bedrock <br />station, while the dam release remains constant. If <br />these runoff events are overlooked, it can be seen that <br />for June, July, and August, the Bedrock flows tend to <br />stabilize near 60 ft3/s. This equates to an 18 ft3/s <br />loss in flow between McPhee Dam and Bedrock. For <br />the most part, the summer of 1989 was drier and <br />warmer than average which would tend to maximize <br />the low-flow losses. It should also be noted that <br />during cooler months, when evapotranspiration rates <br />and irrigation withdrawals are lower, low-flow losses <br />would not be as great. <br />During the summer of 1989, BLM made several <br />discharge measurements on the Dolores River to <br />determine how and where the 18 ft3/s loss was <br />occurring. The average discharges measured at <br />selected points within the study area are shown in <br />Figure 14. The difference in discharge between sites <br />(i.e., water loss) correlates well with channel dis- <br />tance, especially if the "in use" water rights (see <br />Table 8) between sites are taken into consideration. <br />This indicates that most of the water loss is occurring <br />from evapotranspiration along the water course and <br /> <br />200 <br /> <br />150 <br /> <br />.,!!!. <br />u:: <br />~ <br />o <br />u: <br /> <br />100 <br /> <br /> <br /> <br />from man-related water diversions. Water loss or <br />gain to or from ground water systems appears to be <br />insignificant. Also, water gains from tributary <br />inflows were minimal (e.g., Disappointment Creek, at <br />its confluence with the Dolores River, was ~ most <br />of June and July and flowing less than 0.10 ft Is in <br />August). <br />Table 9 shows how the 18 ft3/s loss would affect <br />the three bypass release flows (i.e., 78, 50, and 20 ft31 <br />s) at selected points in the study area. A worst case <br />scenario is also presented which includes diversions <br />for all valid existing water rights with appropriation <br />dates prior to 1975 (see Table 9). Presently "in-use" <br />water rights are assumed to be part of the 18 ft3/s <br />loss, while inactive water rights are factored in, <br />continuously using their full ap~ropriation. As <br />previously mentioned, the 18 ft Is loss was deter- <br />mined during a summer release of 78 ft3/s. It is <br />possible that at the lower releases of 50 and 20 ft3/s <br />losses would be greater due to higher water tempera- <br />tures. <br />Based on river resource values analyzed in this <br />report, changes in water quality resulting from <br />operation of McPhee Reservoir are negligible. <br /> <br />2 <br /> <br />-+- Bedrock <br /> <br /> <br />----- McPhee <br /> <br />:==:: Precipitation <br /> <br />1.5 <br /> <br />Data Source: (USGS, <br />USBR, BLM), 1989 <br /> <br />.." <br />iD <br />o <br />is' <br />;=;: <br />~ <br />(5" <br />:::l <br />:::l <br />o <br />:::r <br />(D <br />l/l <br /> <br />50 <br /> 0.5 <br /> '-I <br /> I I ,-, <br /> I , <br /> , , I I <br /> 1-1 I I I <br /> I I I <br /> I I I <br /> I I I <br /> , I I <br />0 I I I 0 <br />5 10 15 20 25 30 <br /> <br /> <br />July, 1989 <br />Figure 11, Dolores River low flow - McPhee vs. Bedrock, June 1989. <br /> <br />22 <br />