Laserfiche WebLink
Reservoir Operating Studies <br />reservoir and reflects sedimentation which has occurred in the existing reservoir. Of this total <br />capacity, 3,722 of are assumed to be dead storage; this is the same as the existing reservoir. <br />The enlarged Elkhead Reservoir is assumed to fill under its existing water rights plus a <br />transferred California Park first-fill water right in the amount of 36,536 af. The California <br />Park water right is a conditional storage right held by the River District for a proposed project <br />further upstream in the Elkhead Creek basin. As a result of the California Park transfer, the <br />decreed storage rights at the enlarged Elkhead Reservoir total 50,236 af. As with Stagecoach <br />Reservoir discussed earlier, the "excess" decree capacity was assumed to be administered as a <br />refill right. <br /> <br />' Two important changes were made to reservoir operating assumptions in this scenario. <br />First, it was assumed that the 9,000 of industrial water supply contract pool in Stagecoach <br /> Reservoir was moved into the enlarged Elkhead. This assumption reflects the fact that the 2040 <br /> demand projections show most increases in industrial water demands to occur in the Craig area <br /> while most increases in municipal demand will occur in the Steamboat Springs area. The <br /> transfer of the industrial contract to the enlarged Elkhead would free up that supply in <br /> Stagecoach for additional municipal use in the upper part of the basin. As a result of this <br /> assumed transfer, a total of 22,700 of of storage in the enlarged Elkhead Reservoir would be <br /> allocated to existing municipal and industrial contracts and to dead storage, leaving 22,200 of <br /> allocable to other future uses. <br /> The second important change in reservoir operating assumptions was the adoption of a <br /> flow support operation at the enlarged Elkhead Reservoir. This operation would seek to <br /> enhance Yampa River mainstem flows in critical low flow periods by making releases from the <br /> 22,200 of unallocated pool in the enlarged reservoir. These releases would improve late season <br /> low flow conditions in reaches designated as critical habitat for the endangered Colorado <br /> squawfish and Humpback chub. <br /> The timing and amount of such releases were assumed to be keyed to flow conditions at <br /> Maybell; if flows at Maybell are less than a monthly target value and there is water available in <br /> the 22,200 of unallocated pool, a release is made to bring flows at Maybell up to the target <br /> level. Several target levels were investigated, including the preliminary flow recommendations <br /> at Maybell. However, it was determined that releases to meet monthly targets equal to the flow <br />' recommendations would not provide as much flow enhancement supply in the late fall (the <br /> water would be used up trying to meet the July target in most years) and would seriously <br /> jeopardize the summer recreation potential at the enlarged reservoir. To some degree this <br /> conclusion is an artifact of using a monthly model; nevertheless, a more modest set of monthly <br /> targets intended to "feather" releases out over a longer period, was adopted. These targets are <br /> displayed in Table 2-8. In actual operation these releases would probably be determined on a <br /> daily basis. <br />Results <br />Water Deliveries <br />Shortages occur in 38 years of the 53 year study period. The average annual total <br />shortage is 1,588 of and the maximum annual total shortage is 15,721 af. These values are <br />basically the same as modeled demand shortages observed under future "without project" <br />2-19