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<br />.~,~..- <br />~~~, <br /> <br />Concentrations of major chemical constituents near the reservoir surface <br />at transect 7 and near the reservoir bottom at transect 2 for the summer of <br />1985 are shown in figure 17. Between July and August, concentrations of <br />calcium, magnesium, sodium, bicarbonate, chloride, and sulfate more than <br />doubled near the reservoir bottom, whereas concentrations of these constit- <br />uents changed very little near the reservoir surface at transect 7. The <br />variations in ion concentrations at transects 2 and 7 were consistent with <br />changes in specific conductance that occurred with depth and demonstrate the <br />effects of chemical stratification for specific ions. The changes in concen- <br />trations of specific ions probably result largely from variations in concen- <br />trations of the ions in the Arkansas River upstream from the reservoir. <br /> <br />Trace Elements <br /> <br />Trace elements occur in relatively small concentrations and usually are <br />expressed in micrograms per liter. Concentrations of selected trace elements <br />analyzed from water samples collected during the summer of 1985 near the <br />reservoir bottom at transect 2 and near the reservoir surface at transect 7 <br />are summarized in table 3. These data indicate that most of the trace ele- <br />ments are suspended rather than dissolved; the trace elements are sorbed to <br />the sediment particles (and organic particulates) and, therefore, are trans- <br />ported with sediment entering the reservoir. As the sediment settles to the <br />reservoir bottom, trace elements are removed from the water. Reducing condi- <br />tions commonly occur in the bottom sediments where the water filling the void <br />spaces between sediment particles contains little or no dissolved oxygen. <br />These conditions result in dissolution and mobilization of trace elements <br />which then migrate upward. As trace elements reach the surface of the reser- <br />voir sediments, the trace elements are oxidized by dissolved oxygen in the <br />reservoir water and precipitate on the upper sediment particles (Britton and <br />Wentz, 1980). If dissolved oxygen becomes depleted in the lower strata of <br />the reservoir, reducing conditions may cause large concentrations of trace <br />elements to be released quickly to the reservoir water. <br /> <br />During August and September 1985, concentrations of total recoverable <br />iron were 4,100 ~g/L and 2,800 ~g/L near the reservoir bottom at transect 2. <br />The recommended criterion for aquatic life is 1,000 ~g/L (U.S. Environmental <br />Protection Agency, 1976). Dissolved-manganese concentrations also exceeded <br />public water-supply standards near the reservoir bottom at transect 2 during <br />July and September. Concentrations of other trace elements were less than <br />established water-quality standards for Pueblo Reservoir (Colorado Department <br />of Health, 1982). <br /> <br />Biological Constituents <br /> <br />Lakes contain a large variety of organisms. During 1985, the distribu- <br />tion and abundance of phytoplankton and zooplankton were measured. Plankton <br />is the community of suspended or floating organisms that drift with water <br />currents. The plant portion of the plankton are called phytoplankton and <br />commonly are referred to as algae. Zooplankton are the animal part of the <br />plankton. <br /> <br />37 <br />