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<br />GQOO'71 <br /> <br />only. In general, higher unit costs are being encountered for those units <br />farther out on the planning horizon. <br /> <br />PROGRAM OVERVIEW <br /> <br />- <br /> <br />figure 6 displays the 1995 Projection Windows of TDS at Imperial Dam based on <br />the 1981 forum Review. The upper window shows conditions without any salinity <br />controls or augmentation programs in place. Under this condition, future TDS <br />could fall anywhere in the area bounded by high and low depletion rates and <br />high and low yields for the river system. The lower window shows projected <br />TDS with only Reclamation WQIP salinity control units in place (no snowpack <br />enhancement) under the same boundary conditions. Under optimal conditions of <br />high runoff (yield) and low depletions or development, the 1995 projected TDS <br />conditions could meet the TDS numeric criteria.at Imperial Dam. However, <br />according to the relative window area shown above the TDS numeric criteria, <br />projected TDS will exceed the numeric criteria under most other runoff and <br />depletion conditions, even with salinity control. <br /> <br />figure 7 is a graphical display of CRSS salinity projections at Imperial Dam. <br />These projections are based on current state-of-the-art computer modeling of <br />the Colorado River Basin and have been released to the pUblic in Progress <br />Report No. 11. <br /> <br />Projected TDS is shown only for the years 1995 and 2010 to provide a direct <br />comparison of TDS with and without USBR and USDA salinity controls or <br />snowpack enhancement projects. Hydrological variations of runoff (yield) are <br />shown as a range on the bar graph. The low salinity range represents high <br />flows and the high salinity range represents low flows. In addition, the <br />average 15 million acre-feet yield used by CRSS (fig. 7) corresponds to the <br />hi9h runoff/yield considered by the forum (fig. 6). In contrast to the forum <br />projections (fig. 6), the CRSS projections were derived based on only one <br />rate of depletion or development scenario. This rate is compared to the <br />depletion rates projected by the forum in figure 8. For the 1995 projection, <br />there appears to be a possibility of satisfying the TDS numeric criteria <br />without any salinity controls under conditions of the most favorable hydrology. <br />By 2010, however, projected TDS conditions without salinity control will <br />exceed the TDS numeric criteria standard for all hydrological variations. <br />For both the 1995 and 2010 conditions with salinity controls, and without <br />snowpack enhancement, it is apparent that there 1S about a 50 percent chance <br />for meeting the TDS numeric criteria standards for the full range of future <br />hydrology variations in the basin. <br /> <br />CRSS Simulation <br /> <br />A second set of simulations were run using CRSS to evaluate cumulative <br />effects of the full water quality improvement program and a snowpack enhance- <br />ment program. The simulations each involved 15 traces for a 58-year period, <br />from 1983 to 2040, the year in which Upper Basin depletions peak at 5.8 million <br />acre-feet per year. The scenarios consisted of the following: <br /> <br />1. BASE case. - Projected depletion schedule with no salinity control <br />projects or snowpack enhancement. <br /> <br />13 <br />