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<br />P ART V <br /> <br />HISTORICAL AND PRESENT SALINITY CONDITIONS <br /> <br />e <br /> <br />Sedimentation in reservoirs may influence both TDS and the <br />ratio of dissolved ions. Suspended sediment which is subject to mechan- <br />ical degradation in a river environment may continue to release salts <br />and exchange ions (sodium exchanged for calcium); however, once settled <br />out in the reservoir, these salts and ion exchange capabilities may be <br />isolated. Sediment stored in reservoirs may contain salts which would <br />have been released with continued mechanical breakdown in a riverine <br />environment. <br /> <br />3. Irrigation and Increased Depletions <br /> <br />Most of the irrigation projects that deplete water and increase <br />salt pickup to the river were largely in place before 1965. Moreover, <br />like the newly inundated soils in reservoirs, newly irrigated lands are <br />subject to a leach-out period. In cases where lands with poor drainage <br />stored salt, these areas were taken out of production. In addition, <br />irrigation practices changed significantly during the 1960-80 period, <br />with canal and lateral lining, sprinkling systems, gated pipe, and <br />trickle systems being introduced. These changes should result in re- <br />duced return flows and salt pickup. Projected water depletions through <br />the 1965-80 period were largely unrealized; total depletions increased <br />by approximately 12 percent. <br /> <br />Years <br />1970-79 <br />1960-69 <br />1950-59 <br />1940-49 <br />1930-39 <br />1920-29 <br />1910-19 <br />1900-09 <br /> <br />Average annual depletions <br />(1,000 acre-feet) <br />Upper Basin <br />3,565 <br />2,538 <br />2,043 <br />1,894 <br />1,712 <br />1,998 <br />1,656 <br />1,001 <br /> <br />by basin <br /> <br />e <br /> <br />Lower Basin <br />6,136 <br />6,119 <br />4,757 <br />3,776 <br />3,676 <br />3,662 <br />3,643 <br />3,373 <br /> <br />Previous Reclamation salinity projections have been too high, <br />largely because the depletion projections were also too high. Trans- <br />basin diversions and increased reservoir evaporation account for most <br />of the increased depletions from 1960-80; however, no additional salt <br />pickup or loading occurred with these depletions. <br /> <br />The large quantities of water expected to be depleted for <br />steam power generation, coal gasification, oil shale, and mineral de- <br />velopment have not been realized in the past decade. Even where new <br />coal-fired powerplants have been constructed, some of the water has been <br />obtained from existing agricultural rights. While water uses have often <br />changed, the total depletions have increased only slightly. <br /> <br />e <br /> <br />In cases where powerplant water was obtained from existing <br />agricultural supplies, salt pickup may have been reduced since irri- <br />gated lands in areas of coal deposits are often saline soils of Mancos <br />Shale origin. <br /> <br />26 <br />