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1 <br />to return flows from both indoor and outdoor uses of water. This has not et become a significant <br />Y <br />issue in Water Division 5 (Colorado River), but will likely be similar to precedents set in Water <br />Divisions 1 and 2. In-house consumptive use has typically been accepted to be at a rate of 5 percent <br />of in-house total use, with the remainder returning to the system via the wastewater collection and <br />treatment system. Returns from outdoor use, primarily lawn irrigation, have been recognized at rates <br />ranging from 10 percent to 38 percent. For this analysis, a reasonably conservative value of <br />15 percent has been selected, which includes 2 percent as immediate surface runoff and 13 percent <br />as deep percolation. <br />Using these return flow factors, surface and groundwater returns for indoor and outdoor use were <br />calculated. Wastewater from indoor water use associated with septic systems will also eventually <br />return to the streams, but both the volume and timing of such returns is dependent on the location, <br />type and configuration of the septic systems, characteristics of the intervening alluvium between the <br />septic systems and the receiving stream, and consumption via evapotranspiration from area <br />vegetation. For this analysis, it was assumed that the lagged return flows of total indoor use <br />associated with septic systems and returned to area streams is 13 percent. . <br />Under the baseline ear demand return flows are ex ected to avera e a relative) low 46.6 ercent <br />Y ~ P g Y P <br />of total usage (see Table 3.5), because 50 percent of the users are estimated to be on septic systems <br />where return flows do not accrue at the same level as from wastewater system users. Depletions to <br />the river basin are therefore reduced by 3,236 ac-ft/yr in return flows under baseline conditions. <br />Future.return flows would be expected to increase to 71.8 percent of demand (see Table 3.6), due <br />to the increased returns from additional users incorporated into the wastewater collection system. <br />Depletions under future conditions are therefore offset by the 20,527 ac-ft/yr in municipal returns <br />under future conditions. <br />Another factor that affects the municipal return flow calculation is the issue of replacement reservoir <br />return flow credits. It is the position of the USFWS that return flows from within Ute Water's <br />system associated with replacement reservoir releases must be credited to the replacement reservoir <br />rather than the project proponent under Section 7 consultation. As a result, the replacement reservoir <br />releases must be subtracted from Ute Water's use prior to calculation of return flows for both <br />baseline and future conditions. Therefore, return flow volumes are reduced to 2,910 ac-ft/yr and <br />18,236 ac-ft/yr of municipal returns for the baseline and future condition, respectively (see Tables <br />r 3.1 and 3.2). <br />Ute Water does not agree with the USFWS position on return flow credits from replacement <br />reservoirs and believes that this position is contrary to Colorado water law. However, Ute Water <br />accepts the USFWS position in this case because it affects only the project depletion for calculation. <br />3.2.8 Depletion Summary <br />Each of the above factors was evaluated and incorporated into the depletions analysis for the District, <br />as summarized in Tables 3.1 and 3.2. Total Colorado River Basin depletions under baseline <br />conditions average 4,628 ac-ftlyr. This number is expected to increase to 7,823 ac-ft/yr. Though <br />demand will increase significantly, this increase will be offset to a large degree by future municipal <br />CDM Camp Dresser & McKee B-8 <br />0:18047-1101DOC W PAEND-8. DOC <br />