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<br />4'~ <br />2. u;.; <br /> <br />hyperbolic, or inverse forms. Model 12 is a multiple <br />regression of the logarithm of concentration to the log- <br />arithm of streamflow and the square of the logarithm of <br />streamflow. The regression model for a particular vari- <br /> <br />able was selected after rcviev.' of regression statistics, <br /> <br />such as the coefficient of detem,i nation and predicted <br />error sum of squares (PRESS statistic) and review of <br />plots of regression residuals. For dissolved-solids and <br />major-ion concentrations, model 12 was used for flow <br />adjustment. Hyperbolic functions were used for flow <br />adjustment of monthly loads. <br />The output from ESTREND lists summary <br />statistics, regression statistics for the various regression <br />flow-adjustment models, and the results of the mono- <br />tonic tests for the original data (not flow adjusted) and <br />the flow-adjusted data (Schertz and others, ] 991). <br />The trend slope is reported in original units per year <br />and is computed by the method in Sen (1968). The <br />trend slope equals the median slope of all pairwise <br />comparisons (the difference between two observed <br />values divided by the number of years between obser- <br />vations). The trend slopes also are reported as a per- <br />centage of the mean value (the slope divided by the <br />mean times 100). For logarithm-transformed data <br />(model 12), the slope in original units is computed <br />from the expression (eb minus I) times the mean con- <br />centration, where b is the seasonal Kendall slope in nat- <br />ural logarithm (base e) units. The corresponding <br />percent change for logarithm units is computed from <br />the expression (eb minus I) times 100. The trend <br />slopes for flow-adjusted data also are reported in origi- <br />nal units by ESTREND. The percent rate of change is <br />extracted from the slope of the residuals trend and then <br />is used to estimate the slope in original units from the <br />median concentration of the original data. <br />Along with computing the trend slopes and <br />percent rate of change, ESTREND also computes the <br />p value for each test (on the original data and the flow- <br />adjusted data). The p value is the attained significance <br />level of the test. The p value is a measure of the evi- <br />dence to accept or reject the null hypothesis (Helsel <br />and Hirsch, 1992). As the p value gets smaller, the <br />probability of rejecting the null hypothesis (no trend) <br />increases, or in other words, the probability increases <br />that there is in fact a trend in the data. <br />The trend slopes derived by ESTREND repre- <br />sent a median rate of change of concentration or load <br />and are measures of monotonic trends during the <br />selected time period. The slope is an approximation of <br /> <br />the time variation for the entire period, and it might <br />mask short-term changes in the data. Monotonic trend <br />slopes are not specific about when changes occurred; <br />however, more specific information was needed for this <br /> <br />study because the objective was to relate salinity- <br /> <br />control projects to salinity trends, if any were present. <br />To aid in interpretation of the monotonic trend results, <br />graphical examination of the data also was done using <br />a smoothing technique called LOWESS, or LOcally <br />WEighted Scatterplot Smoothing (Cleveland, 1979). <br />The LOWESS technique fits a smooth curve to a data <br />set by use of weighting functions with weighted least <br />squares. The LOWESS smooth is robust, which means <br />that the effect of outliers is minimized, and might be <br />highly nonlinear. The curve-smoothing technique was <br />used with the ESTREND results to determine in what <br />part of the record a trend had occurred in instances <br />where a significant monotonic trend was reported. <br /> <br />Monotonic Trend Analysis Using Linear <br />Regression <br /> <br />Linear-regression analysis for trends is a para- <br />metric method that involves a regression of the variable <br />of interest to time. Parametric methods are more pow- <br />erful than nonparametric methods for trend analysis <br />if the residuals are normally distributed (Hirsch and <br />others, 1991). Also, parametric methods might be <br />more effective for data sets that have small departures <br />from normality and for small sample sizes. Trends in <br />annual and seasonal dissolved-solids loads were ana- <br />lyzed using the linear-regression method. Data sets <br />consisting of annual or seasonal loads have only one <br />value per year and have much smaller sample sizes <br />than data sets derived from periodic data, and the <br />potential seasonality problem associated with periodic <br />data is removed for data sets consisting of annual <br />values. <br /> <br />The simple linear regression of annual (or sea- <br />sonal) dissolved-solids loads to time is of the forrn: <br /> <br />L = a + bT <br /> <br />(3) <br /> <br />where <br />L = annual or seasonal dissolved-solids load, <br />in tons; <br />a and b = regression coefficients; and <br />T = time (year or water year in the case of <br />annual data). <br /> <br />12 Trend Analysis of Selected Water-Qualily Data Associated With Sallnlly-Controt ProJect. In the Grand Valley, <br />In the Lower Gunnison River Basin, and at Meeker Dome, Western Colorado <br />