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9.5 <br />~ 9.0 <br />Z <br />~ 8.5 <br />Q <br />~ 8.0 <br />Z <br />H <br />(A 7.5 <br />Z <br />= 7.0 <br />Q <br />6.5 <br />1,000 <br />QZ~ <br />J Z J <br />~ ~ <br />`~a~ <br />J Z Q <br />W <br />U <br />~ Z <br />~U~ <br />1950-74 <br />1975-99 <br />Colorado water-quality standard <br />• t• s .asp s•~. <br />0~ <br />1950 <br />500 <br />~ • , <br />ffi~~~ .. <br />~'.!` . <br />. ~ t } ~ ~ ~ <br />iet~~ Sl:• <br />.~~. <br />1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 <br />DATE SAMPLED <br />Figure 18. Temporal distribution of measured pH and dissolved solids at Yampa River near Maybell, 1950-99. <br />the 1950-74 period had greater concentrations of chlo- <br />ride (fig. 19), fluoride, and silica. Alkalinity (fig. 20) <br />and concentration of potassium (fig. 19) were not <br />significantly different between the two periods. <br />The relatively large increase in median magne- <br />sium concentration (25 percent) between the two <br />periods compared to increases in median concentra- <br />tions of calcium (7.9 percent) and sodium (8.3 <br />percent) and unchanged median concentrations of <br />potassium caused significantly greater cation-equiva- <br />lent fractions of magnesium and significantly smaller <br />cation-equivalent fractions of calcium, sodium, and <br />potassium during the later period (table 2). Similarly, <br />the large increase in median sulfate concentration <br />(52.8 percent) between the two periods compared to <br />decreased median concentrations of chloride <br />(22.2 percent) and alkalinity (0.7 percent) caused a <br />significantly greater anion-equivalent fraction of <br />sulfate and significantly smaller anion-equivalent frac- <br />tions of chloride and alkalinity during the later period <br />(table 2). Judging by median equivalent percentages <br />(table 2), the water at Yampa River near Maybell, on <br />average, changed from acalcium-sodium-magnesium- <br />bicarbonate-sulfate type during 1950-74 to a calcium- <br />magnesium-sodium-bicarbonate-sulfate type during <br />1975-99, with sulfate becoming more dominant. <br />The results of statistical hypothesis testing <br />(table 2) are consistent with previous studies. Lieber- <br />mann and others (1989) determined by monotonic- <br />trend analysis that, at Yampa River near Maybell over <br />the period 1951-83, median annual dissolved-solids <br />concentration increased by 0.9 mg/L per year, a <br />21-percent increase (29 percent, 1.2 mg/L per year, <br />when flow adjusted). Dissolved-solids load increased <br />by 65 percent over the 33 years of record. In addition, <br />they determined that annual flow-adjusted concentra- <br />tions of magnesium, sodium, and sulfate were deter- <br />mined to have significant upward trends for the period <br />1951-83. For the Yampa River near Maybell for the <br />period 1951-96, Vaill and Butler (1999) determined <br />significant annual increases in annual, flow-adjusted <br />dissolved-solids concentrations (by 0.61 percent per <br />year) and loads (by 0.57 percent per year). <br />INTERPRETATION OF HISTORICAL DATA FROM YAMPA RIVER NEAR MAYBELL 27 <br />