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<br />. <br /> <br />I-~ <br />o <br />~ <br />CoO <br /> <br />. <br /> <br />. <br /> <br />EVALUATIONS OF EXISTING SALINITY CONDITIONS (continued) <br /> <br />Tables I to 20 with each table number corresponding to a stat ion number. <br />The concentrat ions as shown were determined on a flow-weighted basis. <br /> <br />To simplify tabulation, monthly values of flow and total dissolved- <br />sol ids loads were rounded to the nearest 1,000 acre-feet and 1,000 tons. <br />Th is resu 1 ted in some differences between the recorded and t he computed <br />monthly concentrations when the flows were low, for example, below 1,000 <br />acre-feet in the San Rafael and Duchesne Rivers. Similarly, minor differ- <br />ences from published data in monthly concentrations occur in some instances <br />for other stations. <br /> <br />The water qual ity at the Lees Ferry and the four other key stations <br />on the main stem of the Lower Colorado River has been affected by abnormal <br />condit ions during the 1959-78 period because of low runoff in 1959, 1960, <br />1961, 1963, 1964, 1966, and 1967 and the storage of water in Lake Powell <br />in 1963-78. Figure 3 shows the historical flow weighted average salinity <br />concentration fOt" these five statiuns and the combinat ion of the Green <br />River at Green River, Utah; San Rafael near Green River, Utah; Colorado <br />River near Cisco, Utah; and the San Juan River near Bluff, Utah. <br /> <br />The Grand Canyon stat ion has the longest water qual ity record on <br />the Colorado River, 1926-78. It is of interest that the average salinity <br />concentration for the period 1941-78 is only 51 ightly higher than the <br />average salinity concentration for the period 1926-40, 0.B4 to 0.81 tons <br />per acre-foot (618 to 596 mg/L), respectively. <br /> <br />Generally the salinity concentration increases at each succeeding <br />downstream station as a result of depletions by diversions; reservuir and <br />stream evaporation; consumptive use by irrigated crops and phreatophytes; <br />and by 'salt loading from natural springs) streams, solution of salt from <br />reservoir basins, and by irrigat ion return flows. The flows of the Bill <br />Williams River often dilute the flow of the Colorado River in Lake Havasu <br />which sometimes results in a decrease in the salinity concentrat ion from <br />the below Hoover Dam stat ion to the below Parker Dam stat ion. Figure 3 <br />shows the concentrat ion changes between the five lower stat ions and the <br />combined four stations above Lake Powell on the Colorado River. Note also <br />that Lake Mead has a dampening and delaying effect, about 2 years, on the <br />salinity concentrations at the downstream station~. This is especially <br />noticeable for the high salinity concentrations of 1963 at the Lees Ferry <br />and Grand Canyon stations. <br /> <br />D. Present Mod if ied Cond it ions <br /> <br />The 1941-78 period average present modified flow and quality at <br />any station, as defined in this report, is the average of the flows and <br />qual ity that would have resulted if the present (1978) level of deplet ions <br />and salt loading instead of actual depletions and loading had occurred each <br />year of the period. This average present modified flow and quality, <br />therefore, represent an average condition based on the 1941-78 water supply <br /> <br />43 <br />