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<br />. . <br /> <br />. . <br /> <br />. <br /> <br />. <br /> <br />. <br /> <br />INTRODUCTION <br /> <br />Because of ~he detrimental effects of mineral salts on agricultural, munici- <br />l\) pal', and' in:dustrial water use in the Colorado River Basin, the U.S. EPA <br />~ (En'vi ronmen!ta 1 Protecti on Agency), i n1972, mandated the estab 1 i shment of <br />~ salinity st~ndards for various gaging stations along the river. <br />(0 <br />On December 18, 1974, the Colorado River Basin States, through amendments to <br />40 CFR, Part 120, Colorado River Water System, adopted the 1972 levels of <br />salinity a~ three lower main stem stations (Hoover Dam, Parker Dam, and <br />Imperial Dam) as the salinity standards; in essence, a no degradation stand- <br />ard. In ortler to meet these standards, the USBR (Bureau of Reclamation) <br />is implemen~ing the Colorado River Salinity Control Program to reduce the <br />rate of sallt; loading to river, The USBR has 'al so developed mathematical <br />models for ~stimating the effects of past water development projects on the <br />salinity an~ streamflow of rivers in the Colorado River Basin and for pre- <br />dicting the! effects of future developments. <br /> <br />Since 1972, salinity levels at Imperial Dam have fallen steadily, from <br />879 mg/L in, 1972 to 810 mg/L in 1981, in contrast to USBR, EPA, and CRSCF <br />(Colorado River Salinity Control Forum) projections, Unpublished USBR and <br />CRSCF studih have indicated that starting in the mid-1960's, the salt <br />load from s~me areas in the Upper Basin began to decrease. Projections of <br />future salipity are based upon historical salt-flow relationships, under the <br />assumption that these relationships are relatively constant over the period <br />of record. ;If, however, the declining salt loads result from a physical <br />~hange to t~e system, rather than a short-term aberation, prediction of <br />future salinity will be inaccurate. A systematic change may manifest itself <br />in a shift in the individual solute concentration-streamflow relationships <br />or in the values of solute loads or mass fractions. <br /> <br />In order tO'evaluate the possibility of such a systematic change, this study <br />will addresS the following questions: <br /> <br />1. What'is the most accurate model for describing the relationship <br />between $olute concentrations and streamflow? What are the estimated <br />values of parameters for individual ions? <br /> <br />2. ,Do significant long-term trends exist in the recorded values of <br />streamflQw, solute loads or concentrations, or relative composition of <br />total di$solved solids, or in the estimated parameter values of the <br />concentr4tion-streamflow relationship? <br /> <br />3. What are the causes of any identified trends? <br /> <br />In addition, this study will develop a data base containing monthly values <br />from as early as 1926 for streamflow and concentrations of 7 ions at 16 major <br />locations. .Documentation for updating the data base will be provided for use <br />in future statistical analyses. <br /> <br />'-:~~-.-:-71""';--:r ':;~ ,-:,":"'-::":::--"'-':'''-.' ."..--:---'-~:' ~-- :T""-,.-..~ - "'~'-'--'--":::---::-."'--'-:-:.,.,'-:'::~ " <br /> <br />" -~ _ < :t-, <br /> <br />~; ..il.... <br /> <br />i("'- <br /> <br />, . ".~ ~~ ..._ it. <br /> <br /> <br /> <br />J <br /> <br />,~ <br />1 <br />! <br />:1 <br />!~I <br />',!', f <br />f;.:_ " <br />iil,j; " <br />.-~"- ~ ;,~~ --~ ,~ <br />