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<br />Colorado Water Conservation Board <br />J alluary 7, 2008 <br />Page 4 <br /> <br />No diversions will be made when flows at the gage are less than or equal to 15 cfs. <br /> <br />Under the foregoing schedule, the flow-through diversions into the ChalUlels, for recreation) <br />piscatorial, alld fish and wildlife habitat purposes, will never exceed 3.8% of the flow in Trout <br />Creek. In addition, no diversions will occur when flows are less than 15 c.f.s., a rate at which <br />two out of the three CWCB hydraulic criteria for instrealll flows are exceeded, as fin1her <br />described in subparagraph ILB, below. <br /> <br />In addition to the foregoing direct flow diversions from Trout Creek, the ChalUlels will be <br />excavated st11lctmes and may also intercept ground water 1ributal'y to Trout Creek. Such ground <br />water will provide a neceSSal.y source of water for fish habitat during the winter (October 16 to <br />April 30). Depletions associated with evaporation alId secondary evapotranspiration from the <br />'Challl1els are estimated to total between 2.6 alld 4.1 acre-feet alU1Ually. Under the injury with <br />mitigation plan, such depletions will be deemed to occur as the result of surface water diversions <br />from Trout Creek, given the sU1mneIiime diversions of surface water from the Creek and the <br />negligible lag in groundwater depletions to the Creek in the winter. <br /> <br />B. Benefits of mitigation. The benefits to the natural environment from Mr. <br />Neal.burg's stream restoration alId habitat improvement projects on Trout Creek are detailed in <br />the May 2007 repoIi from Black Creek Hydrology, and Feb11lal'y 2000 reports from Wright <br />Water Engineers (both previously provided to CWCB staff), alld will be more fully described at <br />the presentation during the BOal'd's Janual.y 22/23,2008 meeting. As stated in the Black Creek <br />Hydrology rep0l1, Mr. Neal'burg's work on Trout Creek has had a "remarkable effect on the local <br />strealll system," trallsforming the "severely degraded, eroded and braided conditions on <br />[approximately 1.5 miles of] Trout Creek') into a "single thread challl1el alId deep pool habitat" <br />that now provides an "excellent fishery," holds all abU1ldance of fish and provides cool summer <br />water and deep pool habitat for winter. <br /> <br />In 1999 alId 2000, Wright Water Engineers conducted a bioassessment of Trout Creek, <br />including a hydraulic allalysis to evaluate the tiuee principal criteria (average depth, average <br />velocity, alId percent wetted perimeter) used by the CWCB to develop biologic instrealll flow <br />recommendations. Excerpts of this analysis are enclosed (alld tile complete repoIis were <br />previously provided to the CWCB staff). This allalysis measured and modeled flows in Trout <br />Creek at three different stations (see enclosed map), and used methods similal. to the CWCB's <br />R2CROSS methodology. The upper-most location (Station I) was chosen because it is located <br />on an un-restored portion of Trout Creek, while the lower stations al'e located in the improved <br />sections of tile stream on Mr. Nearbmg's propeliy. <br /> <br />Wright Water concluded that, at Station 1 (tile un-restored stTeam location), only one of <br />the CWCB hydraulic criteria was satisfied at flow rates of both 35 c.f.s. (the decreed <br />summel1ime instrealll flow rate) and 15 c.f.s. At the lower stations, however, all tlu.ee criteria <br />were satisfied at a flow rate of25 c.f.s., and two out of three criteria were satisfied at a flow rate <br />of 15 c.f.s. These findings are significant because, under the current injury with mitigation <br />proposal, diversions of 1 c.f.s. into the ChalUle1s will occur only when the gaged flow in Trout <br />