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INTERPRETATION OF HISTORICAL DATA
<br />FROM YAMPA RIVER NEAR MAYBELL
<br />This section describes the results of statistical
<br />hypothesis tests that were used to examine historical
<br />trends in onsite measurements, concentrations of
<br />dissolved solids and major ions, and selected thermo-
<br />dynamic characteristics of water-quality samples
<br />collected from the Yampa River near Maybell (site 8 in
<br />fig. 1). For this site, from November 29, 1950, through
<br />August 16, 1999, the USGS National Water Informa-
<br />tion System (NWIS) data base has 657 water-quality
<br />analyses that have sufficient data to allow thermody-
<br />namic calculations using PHREEQC. At a minimum,
<br />such calculations require pH measurement and
<br />concentrations of all major ions (except potassium,
<br />which can be neglected because of small concentra-
<br />tions). River discharge was not measured for one of
<br />these analyses, allowing 656 flow-adjusted analyses
<br />for statistical calculations. Through September 1,
<br />1969, sampling times (for 413 analyses) and tempera-
<br />tures (for 406 analyses) were not recorded; most of
<br />these analyses were for composited samples. Missing
<br />temperatures were estimated to be the median water
<br />temperature for the month of the sampling date. Alka-
<br />linity was measured on unfiltered sample water before
<br />October 15, 1986, and on filtered water thereafter; for
<br />PHREEQC calculations, unfiltered measurements
<br />were used when filtered measurements were not avail-
<br />able. For the periods October 9, 1980, through
<br />December 20, 1984 (25 samples), and May 15, 1991,
<br />through March 5, 1999 (61 samples), neither measure-
<br />ment generally was done, so alkalinity was calculated
<br />as the amount required to charge balance the solution
<br />with other ions, including potassium. For the sample
<br />collected on July 12, 1956, the concentration of the
<br />sulfate ion was calculated in a similar manner
<br />(neglecting potassium).
<br />The Wilcoxon-Mann-Whitney rank-sum test, a
<br />nonparametric t-test on the joint ranks of two sample
<br />sets (Iman and Conover, 1983), was used to compare
<br />onsite measurements (including pH), constituent
<br />concentrations, and thermodynamic properties of
<br />water samples collected from Yampa River near
<br />Maybell during 1950-74 with those parameters during
<br />1975-99. These periods of time were chosen to repre-
<br />sent the general periods of time before and after onsite
<br />measurements of pH were begun and to separate the
<br />earlier period of minor coal-mining development from
<br />the period beginning in the late 1970's, when coal-
<br />mining development grew rapidly. These statistical
<br />tests were done to indicate possible water-quality
<br />trends associated with the apparent historical increase
<br />in measured pH at Yampa River near Maybell and to
<br />suggest hypotheses that can be examined as possible
<br />causes of that increase.
<br />Because concentrations of dissolved water-
<br />quality constituents usually vary inversely with
<br />discharge, if the data are not flow adjusted for hypoth-
<br />esis tests, unequal distributions of flow discharge
<br />between two sampling periods can cause apparent
<br />significant differences in physical measurements,
<br />concentrations of water-quality constituents, and ther-
<br />modynamic properties. To adjust for the effects of
<br />flow, logarithmic values of these variables (except pH,
<br />calcite saturation index, and pH at atmospheric PCOZ)
<br />were fitted by linear regression (Iman and Conover,
<br />1983) to logarithmic values of discharge for the entire
<br />period of record, and residuals (differences between
<br />predicted and measured values) were used to conduct
<br />statistical hypothesis tests. Because pH is a loga-
<br />rithmic function of H+ concentration, measured pH
<br />and pH at atmospheric PCp2 were not converted to
<br />logarithms for regression. Because some calcite satu-
<br />ration indices are negative and cannot be converted to
<br />logarithms and because saturation indices are loga-
<br />rithmic quotients, calcite saturation indices were not
<br />converted to logarithms for regression.
<br />Tests were set up by defining a null hypothesis
<br />(Hp) stating that the distribution of flow-regression
<br />residuals for measurements, concentrations, and prop-
<br />erties was not significantly different for the two
<br />periods and an alternative hypothesis (Hl) stating that
<br />a significant difference did exist. A test resulting in a
<br />two-tailed significance less than or equal to 0.05 indi-
<br />cates that the alternative hypothesis was accepted,
<br />whereas a significance greater than 0.05 indicates that
<br />the null hypothesis was accepted. Accepting the null
<br />hypothesis does not necessarily indicate a lack of
<br />difference in sample distributions; it merely indicates
<br />that the chance of erroneously rejecting a true null
<br />hypothesis exceeds 5 percent, given the variability in
<br />the data. When the alternative hypothesis was accepted
<br />for a variable, the mean ranks of the residuals for the
<br />two periods were inspected to determine which period
<br />had significantly greater values with respect to that
<br />variable. Results of flow-adjusted Wilcoxon-Mann-
<br />Whitney rank-sum tests are listed in table 2.
<br />INTERPRETATION OF HISTORICAL DATA FROM YAMPA RIVER NEAR MAYBELL 25
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