Laserfiche WebLink
i <br />' records. The differences evidently are rounding and the small volumes of Wind River water in <br />the CDSS records. <br />' The available USBR and state records indicate that C -BT Project's actual in- priority <br />diversions of Big Thompson River water were less than the volumes indicated in this analysis. <br />' Consequently, this analysis probably overstates the actual in- priority diversions. Some of the <br />discrepancies could be inaccuracies in the data and imprecisions in project operation. Although <br />our analysis did not cover 1999, we note that the USBR reported that 55,000 acre -feet of in- <br />priority Big Thompson River water was stored in Carter Lake and Horsetooth Reservoir in 1999. <br />' DIVERTIBLE BIG THOMPSON RIVER WATER <br />The water that was available for diversion under the C -BT water rights during 1983 -98 <br />' was estimated through daily calculations of the native flows in the river and comparisons of <br />these native flows to the actual recorded diversions into the 15 major ditches and 1 municipal <br />' pipeline on the river. The native flows that were in excess of these diversions were considered <br />as being surplus to the other water users on the river and available for C -BT Project diversions, <br />provided that river calls were not being made by water users on the South Platte. The <br />' calculations and comparisons were made in an EXCEL spreadsheet beginning with calculations <br />for the gaging station at the canyon mouth and working downstream past all the points of <br />diversion. The native water at the gaging station at the canyon mouth was calculated by (1) <br />' adding the upstream diversions into the Olympus and Dille Tunnels to the gaged flow at the <br />canyon mouth, (2) subtracting the Adams Tunnel diversion, and (3) adjusting for changes in <br />storage in Marys Lake and Lake Estes. Thus, it can be noted that the calculated native flows are <br />essentially "virgin" or "undepleted" flows in that they are the flows that would have occurred but <br />for the upstream operation of the C -BT Project. Although changes in storage in Marys Lake and <br />Lake Estes were generally small in relation to the native flows, the adjustments for their <br />changes in storage helped to make the native flow estimates more consistent. Once the native <br />' flow was calculated, the flow passing each downstream point of diversion was calculated as the <br />flow passing the immediate upstream point of diversion plus the stream gain in the intervening <br />reach minus the diversion at the current point of diversion. The divertible flow was then <br />' calculated as the smaller of either the native flow at the canyon mouth less the required 45 cfs <br />bypass at the Dille diversion facility or the minimum flow passing any of the downstream points <br />of diversion. Thus, the native water that was available for C -BT Project diversions was limited by <br />both the native water at the Dille diversion facility exceeding the required minimum bypass and <br />the smallest amount of native water passing any of downstream points of diversion. Had the C- <br />' BT Project diverted native water at greater rates, either sanding problems would have occurred <br />at the Dille diversion facility or existing water users would not have been able to make their <br />historical diversions. Negative values occurred in the calculations for the native flow passing <br />downstream points of diversion on days when C -BT Project water was being diverted by the <br />water users since the total historical diversions, including C -BT Project water as well as river <br />' water, were used in the comparisons. Obviously, divertible native flows did not exist on days <br />when negative values occurred. <br />10 <br />