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<br />. <br /> <br />12 <br /> <br />anyone year on the the mainstem of the Colorado River to get a <br />reliable estimate of water use or sa1tt1oading from irrigation in <br />a reach of the river. Refer to Figure ES5 for a display of <br />monthly and annual variation in salinity concentration. A three <br />percent reduction in the salinity contributed due to the USDA <br />program would be hard to monitor when the monthly and annual <br />variation is so great. Most of the time the irrigation component <br />is less than the error of measurement of flow or salinity. <br />Therefore, it is imperative that water and salt budgets be <br />prepared for the irrigation component based on data collected on <br />acreage, diversions, estimated water use, monitored irrigation <br />management, and other irrigation parameters. There is fairly <br />good agreement between the 40 year average of gaged data and <br />computations of annual salt loading using irrigation budgets. <br /> <br />Diversion records from irrigation companies in the valley were <br />compiled and evaluated by the Colorado Water Conservation Board. <br />Crop consumptive use using acreage and standard <br />evapotranspiration methods gave a fairly reliable estimate of <br />water use. Field irrigation evaluations done over the entire <br />season in the area provide a good estimate of onfarm efficiency <br />and an estimation of deep percolation. In Grand Valley, <br />irrigation information was gathered by SCS on each farm and field <br />and validated by contacting over 900 farmers. Onfarm <br />application efficiency was estimated to average about 25 percent. <br />Diversions to the farm averaged more than eight acre feet per <br />acre or four times the water consumed by the crop. It does not <br />require sophisticated evaluations to make reliable determinations <br />at these low irrigation efficiencies. Therefore, the current SCS <br />monitoring is not of unimproved systems but of the management of <br />recently installed irrigation systems. <br /> <br />ARS collected several years of data on irrigation water <br />management and salinity. ARS evaluated salinity impacts, <br />irrigation water management, and drainage options. ARS\SCS data <br />dating back to 1954 is available. Salinity data published for <br />1917, 1928, 1954, 1973, and 1988 indicates that salinity <br />concentration of subsurface return flow, the ground water <br />aquifer, and other characteristics have remained constant over <br />the years. <br /> <br />ARS conducted a special research study in 1975 to negate the <br />notion that salts can be flushed off the surface of an irrigated <br />field. It once again substantiated that an increase in salinity <br />of surface return flow is not measurable and leaching through the <br />soil profile is required to remove salts. Conclusion; "Note that <br />there is no statistical difference in Electrical conductivity, <br />chloride concentration, or nitrate concentration between the <br />delivered irrigation water and tailwater runoff." Ions involved <br />are quite soluble and are readily moved beneath the soil surface <br />by the advancing irrigation front and are not removed by the <br />surface runoff water. ARS did collect data on the amount of <br />sediment leaving the fields, 3 tons/acre. They also found a 9 <br />fold increase in phosphorous in the surface runoff. <br />