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<br />002858 <br /> <br />Table 1.--Maximum likely ambient aonaentrations of ahemiaal aonstituents <br />in streams in the Yampa River basin--Continued <br /> <br />- <br /> <br />Constituent <br /> <br />Number <br />of an- x + 2s <br />alyses <br />73 15 <br />72 33 <br />40 7.0 <br />40 14 <br />40 51 <br />40 19 <br />40 15,000 <br />40 260 <br />40 .073 <br />40 17 <br /> <br />( <br /> <br />Dissolved zinc, ~g/L--------------------------------------- <br />Total zinc, ~g/L------------------------------------------- <br />Bottom antimony, ~g/g (micrograms per gram)---------------- <br />Bottom arsenic, ~g/g--------------------------------------- <br />Bottom chromium, ~g/g-------------------------------------- <br /> <br />Bottom copper, ~g/g---------------------------------------- <br />Bottom iron, ~g/g------------------------------------------ <br />Bottom lead, ~g/g------------------------------------------ <br />Bottom mercury, ~g/g--------------------------------------- <br />Bottom nickel, ~g/g---------------------------------------- <br /> <br />lAII values were <10 ~g/L. <br />2AIl values were <100 ~g/L. <br />3Total vanadium is not analyzed by the U.S. Geological Survey. <br /> <br />, <br /> <br />consumption. Environmental impacts for each alternative combination of the <br />above uses will differ considerably. Aided by the application of plant-proc- <br />ess and environmental models (Steele and others, 1976b; I. C. James II and <br />others, written commun., 1976), ramifications of these direct environmental <br />impacts are being ~va1uated. As part of this evaluation, residuals-management <br />alternatives of coal-mining and coal-conversion processes will be analyzed in <br />the context of amounts and nature of discharged residuals and water-use re- <br />quirements. Secondary impacts of increased population and related economic <br />growth are being studied (Udis and Hess, 1976) through the use of regional <br />economic input-output analyses. Projections to the year 1990 will relate <br />economic growth with empirically derived coefficients to determine residuals <br />loadings (Udis and others, 1973). <br /> <br />For the most part, the surface waters of the Yampa River basin currently <br />are unregulated. Only four reservoirs have active storage capacities exceed- <br />ing 5,000 acre-feet (6,200,000 m3); and the total content of the 31 existing <br />reservoirs having individual capacities greater than 100 acre-feet (120,000 m3) <br />is less than 57,000 acre-feet (73,000,000 m3) (Colorado State Engineer, writ- <br />ten commun., 1975). However, a number of major reservoirs have been proposed <br />in the basin. The aggregate storage capacities of these reservoirs total <br />nearly 2.3 million acre-feet (2.9 billion m3), or about 1~ times the long-term <br />mean annual streamflow discharged from the entire basin. The implications of <br />construction of selected major proposed reservoirs are being studied with con- <br />sideration of possible changes in seasonal streamflow patterns and downstream <br />water-quality changes, as well as in regard to storage characteristics and <br />proposed operating rules. Modeling techniques used for these studies will be <br />comparable to those described by Adams (1975) and Ribbens (1975). <br /> <br />. <br /> <br />24 <br /> <br />., <br /> <br />.~~ <br />