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<br />'001261 . <br /> <br />Draft Task 7 Technical Memorandum <br /> <br />. <br /> <br />after the existing senior demands described above, but ahead of the Juniper-based instream <br />flow right and ahead of existing junior and future demands. <br /> <br />The only future demand treated as being senior in the model is the Hayden Station. The <br />power plant has a senior (pre-1954) direct flow water right for 30 cfs which is more than <br />adequate to cover existing uses at the plant as well as projected water demands beyond the <br />2040 long-term horizon. Future demand at the Hayden plant (demand 28) was, therefore, <br />represented in the model as a senior demand and allowed to divert ahead of the Juniper-based <br />instream flow right and ahead of the filling of new storage facilities. <br /> <br />Junior Demands: These demands reflect increments to bring the baseline demand <br />condition up to a future demand level, either 2015 or 2040. Future junior demands include <br />demands 25 through 27, 29 through 33 and demands 35 and 36 (Table 2). These juniors have <br />the lowest priority of all modeled demands and reservoirs and are served only after all other <br />demands and reservoirs are satisfied. <br /> <br />Reservoir Fill Administration <br /> <br />The basin model was structured to operate on a water-year basis, i.e. October through <br />September. Reservoirs in the model were allowed to fill only one time each water year up to <br />their physical capacity; carryover storage in reservoirs was not counted against the reservoirs' <br />annual fill limit. This simplification of true strict administration is not thought to introduce <br />significant error since none of the modeled reservoirs approached using their full annual fill <br />limit. However, the administration of reservoir fill may be further refined in Task 9 of this <br />Study. <br /> <br />Demands as Withdrawals versus Depletions <br /> <br />Certain diversions in the basin are fully consumptive (e.g., cooling water at power <br />plants) while others produce significant quantities of return flow (e.g., municipal uses). The <br />majority of the demands explicitly represented in the Yampa River basin model were treated as <br />depletions (fully consumptive) in the amounts estimated in Task 2 of the Study. There are <br />certain exceptions, however, where demands were modeled as withdrawals and return flows. <br /> <br />Demands which were modeled as withdrawals included municipal demands and <br />diversions of the Maybell Canal. These demands could not be represented as simple depletions <br />because to do so would underestimate their draft on reservoir storage and their call against <br />upstream junior water rights. Municipal withdrawals were assumed to generate return flows <br />within the same time step (one month) as the diversion; the percentage of municipal withdrawal <br />actually consumed was varied seasonally. The Maybell Canal was also represented as a <br />withdrawal but with lagged return flows. <br /> <br />Potential Low Flow Reaches <br /> <br />Except for. the minimum release requirements from Stagecoach Reservoir, there are no <br />instream flow requirements on the mainstem of the Yampa River above Juniper Canyon. <br />Juniper Canyon is the location of the modeled Juniper Project contemplated draft as converted <br />to an instream flow right. Although instream flows on the Yampa mainstem were not <br />explicitly targeted in the model, modeled flows in several reaches which were considered <br />susceptible to low flow conditions were reviewed in all model runs. Included in these reviews <br />were the reaches below the Hayden Station diversion and the reach immediately above the <br />confluence of the Yampa River and the Williams Fork River. While low flows predicted by <br /> <br />6 <br /> <br />'1;... <br />