Laserfiche WebLink
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 <br />