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WSP04876
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Last modified
1/26/2010 2:16:01 PM
Creation date
10/12/2006 12:42:31 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8270.100
Description
Colorado River Basin Water Quality/Salinity -- Misc Water Quality
Basin
Colorado Mainstem
Water Division
5
Date
1/1/1983
Author
USDOI
Title
Quality of Water - Colorado River Basin - Progress Report No. 11 - January 1983
Water Supply Pro - Doc Type
Report/Study
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<br />. <br /> <br />PART V <br /> <br />COLORADO RIVER WATER QUALITY ASSESSMENT <br /> <br />~ <br /> <br />The Colorado River area contiguous to California serves a large <br />influx of recreationists almost year round. but many of these people <br />camp indiscriminately on public lands along the river' 5 edge. Sanitary <br />facilities, though previously limited, are n01,1 improving, an important <br />factor for the protection of public health. <br /> <br />,.. <br />.... <br />,.... <br /> <br />The Colorado River is highly regulated and its waters are <br />intensively used and reused. Water in the California reach of the <br />Colorado River is sodium-calcium sulfate in character and is very <br />hard. The threshold value of chlorides, reported by the University of <br />California Agriculture Extension Service in Guidelines for the Inter- <br />pretation of ~'ater Quality for Agriculture, February 8, 1974,18] is 142 <br />mg/L. Prior to 1971, the average chloride concentration at Topock <br />was about 90 mg/L, and just north of the International Boundary it was <br />240 mg/L. This increasing downstream salinity can be attributed pri- <br />marily to irrigation return flows coupled with the reduced flow in the <br />Colorado River resulting from diversions bet\o'een Parker and Imperial <br />Dams. <br /> <br />_." <br /> <br />. <br /> <br />Although chlorides are a definite water quality problem, the <br />specific conductance data for the past decade have shown a minor but <br />steady improvement. During water year 1980, a slight improvement in <br />electrical conductivity was rpcorded at both stations. While conduc- <br />tivity increased again in water ypar 1981, the mean values are gf'nerally <br />below those of the laRt decade. Turbidity at the International Boundary <br />station increased markedly in March 1980 but declined later in the year. <br />Minimum dissolved oxygen values at this station violated the minimum <br />standard (6.0 mg/L) in slJIlmer 1980, and equalled the standard in 1981. <br />In \,later year 1980, DOT was detected at 0.02 ug/L (micrograms per <br />liter), violating the EPA standard of 0.001 mg/L. <br /> <br />found at <br />standard <br /> <br />During water year 1980, <br />a concentration of 0.05 <br />of 0.001 mg/L. <br /> <br />PCB's (polychlorinated byphenyls) ~re <br />mg/L, a value in excess of the EPA <br /> <br />(J 10-) 75 <br />In 1981 <br />amounts <br /> <br />Fish tissue analyses have disclosed repeated moderate levels <br />ppb) of DOT in fish from the Colorado River frem 1978 to 1980. <br />the DOT level dropped to 22 ppb (parts per billion). Trace <br />of Dacthal were detected in 1979. <br /> <br />The IDS concentration of the Salton Sea is currently about <br />38,000 mg/L and is rising at a rate of about 400 mg/L per year. When the <br />salinity reaches 40,000 mg/L, it is expected that this concentration will <br />be unsuitable for the important sport fisher~' as ~ll as water-oriented <br />recreation and wildlife habitation. <br /> <br />. <br /> <br />There has been a lack of suitable sites within the basin for <br />disposal of large volumes of waste materials generated by geothermal and <br />agricultural pesticide operations. Because the geothermal industry in <br />the Imperial Valley is developing rapidly, disposal of the brim' wastes <br />is creating growing problems; however, a major disposal site 'oo'aS opened <br />in 1981 in the Imperial Valley. <br /> <br />19 <br />
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