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<br />tion water, An irrigation water having a high sodium peroentage will, after a time, give
<br />
<br />rise to a soil having a large proportion of t-eplaceable sodium in the colloid. Clay which
<br />
<br />is partially sodium-saturated is highly dispersible in the absence of flocculating salts
<br />
<br />and has a tendency to migrate downward through the soil and accumulate at lower levels. As
<br />
<br />a result the surface of the soil may be relatively coarse in texture and friable. However,
<br />
<br />below,where the clay accumulates, the soil develops a dense layer of low permeability.
<br />
<br />A quality analysis, taken in 1952 by the Corps of Engineers, reveals that the amount
<br />
<br />of exohangeable sodium tends to increase when water is impounded in Jehn Martin Reservoir,
<br />
<br />and to deorease drastically when the river flows unrestricted through the Reservoir. On
<br />
<br />May 12, . with storage water in the Reservoir, a sample taken one-half mile below the dam
<br />
<br />showed 340 parts per million of sodium, or 30 percent of the total cation eXChange capad ty.
<br />
<br />The Reservoir was emptied on June 1. A sample taken at the same location on June 2 showed
<br />
<br />192 ppm of sodium, or 25 per cent of total cation exchange capacity. By July 7 the amount
<br />
<br />had fallen to 88 ppm, or 8 per Cent of the cation exchange capacity.
<br />
<br />If irrigation water contains available calcium it is exchanged fer excese sodium in
<br />
<br />the soil colloid, promotes flOCCulation and increases the friability of a saline soil. The
<br />
<br />above analysis, however, shows a decrease in calcium content during periods of impounded
<br />
<br />water and an increase when river flow passes through the Reservoir.
<br />
<br />The above discussion shows that the quality of the water deteriorates when it is
<br />
<br />impounded. This factor, plus the increase in transportation loss, the raise in ground
<br />
<br />water, level, and the reduction of erganic material carried by stilled water, is the basis
<br />
<br />upon which the relative values of silt-laden and clear waters were determined.
<br />
<br />Reservoir losses
<br />
<br />Proponents of the permanent pool mU3t realize that certain 108seE: Occur from clIer;y
<br />
<br />body of water. In the case of John Martin Reservoir it is ob\Tic!Us from the record that in
<br />
<br />several past years there has been no irrigd.ion stornge for as long as 6.months at a time.
<br />
<br />This reoord would indicate that during auch periods all losses attributed to impounded
<br />
<br />water lmuld of necessity have to be borne by the permanent :pool. Furthermore, these periods
<br />
<br />occur during tha 7 months from April to October when at least 75 per cent of the total
<br />
<br />annual loss due to evaporation is felt.
<br />
<br />The annual less chargeable to evaporation averages 65 vertical inches per year. ThiA
<br />
<br />would mean a 10A8 of 5,600 acre feet from the 10,000 acre foot pool during the summer
<br />
<br />months and a loss of nearly 7,500 acre feet for the Year.
<br />
<br />Seepage lor!l:lee arc not eo large as thOSe from evaporation, but will run at the
<br />approximate rate of 5 cubic feet per second (frcm De-vis, Handbook of AoPlied Hvdraulics),
<br />
<br />This loss will amount to 10 acre feet per day and may reach a maximum of 2,000 acre feet
<br />
<br />during a period such as discussed above. Durir..g the remainder of the year seepage lossen
<br />
<br />--.Page 4 --
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