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instream flow recommendation from the SF Slater Creek upstream if the confluence with West <br />Prong South Fork Slater Creek (4.1 cfs) to recommend a 9.0 cfs instream flow during the <br />summer months, The winter flow recommendation, which meets 2 or 3 criteria and is within the <br />accuracy range of the R2Cross model is 5.25 cfs. These recommendations were derived by <br />averaging the results of the two data sets. <br />Hydrologic Data and Analysis <br />After receiving the cooperating agency's biologic recommendation, the CWCB staff conducted <br />an evaluation of the stream hydrology to determine if water was physically available for an <br />instream flow appropriation. This evaluation was done through a computation that is, in essence, <br />a "water balance ". In concept a "water balance" computation can be viewed as an accounting <br />exercise. When done in its most rigorous form, the water balance parses precipitation into all the <br />avenues water pursues after it is deposited as rain, snow, or ice. In other words, given a specified <br />amount of water deposition (input), the balance tries to account for all water depletions (losses) <br />until a selected end point is reached. Water losses include depletions due to evaporation and <br />transpiration, deliveries into ground water storage, temporary surface storage, incorporations into <br />plant and animal tissue and so forth. These losses are individually or collectively subtracted <br />from the input to reveal the net amount of stream runoff as represented by the discharge <br />measured by stream gages. Of course, the measured stream flow need not be the end point of <br />interest; indeed, when looking at issues of water use to extinction stream flow measurements <br />may only describe intermediate steps in the complex accounting process that is a water balance <br />carried out to a net value of zero. <br />In its analysis, CWCB staff has attempted to use this idea of balancing inputs and losses to <br />determine if water is available for the recommended Instream Flow Appropriation. Of course, <br />this analysis must be a practical exercise rather than a lengthy, and costly, scientific <br />investigation. As a result, staff has simplified the process by lumping together some variables <br />and employing certain rational and scientifically supportable assumptions. The process may be <br />described through the following description of the steps used to complete the evaluation for this <br />particular stream. <br />The first step required in determining water availability is a determination of the hydrologic <br />regime at the Lower Terminus (LT) of the recommended ISF reach. In the best case this means <br />looking at the data from a gage at the LT. Further, this data, in the best case, has been collected <br />for a long period of time (the longer the better) including wet and dry periods. In the case of <br />South Fork Slater Cr - Lower no such gage is available at the LT. In fact, there is no gage on <br />South Fork Slater Cr - Lower. It is thus necessary to describe the normal flow regime at <br />Chaparral Creek above the LT through a "representative" gage station. The gage station selected <br />for this purpose was NORTH FORK ELKHEAD CREEK NEAR ELKHEAD, CO (USGS <br />09245500); it has a period of record (POR) of 15 years collected between 1958 and 1973. The <br />gage is at an elevation of 7,005.00 ft above mean sea level (amsl) and has a drainage area of 21.0 <br />mil. The hydrograph (plot of discharge over time) produced from this gage includes the <br />consumptive uses of numerous diversions. However, the existence of these diversions does not <br />preclude use of the data from the gage. To make the measured data transferable to South Fork <br />Slater Cr - Lower above the LT, the consumptive portions of these diversions were added back to <br />the measured hydrograph. The resulting "adjusted" hydrograph could then be used on South <br />-4- <br />