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WSP12246
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Last modified
1/26/2010 4:14:22 PM
Creation date
10/12/2006 5:28:34 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8210.310
Description
Colorado River Basin Organizations and Entities - Colorado River Water Conservation District
State
CO
Basin
Western Slope
Date
1/1/1996
Author
David L Butler
Title
Trend Analysis of Selected Water-Quality Data Associate With Salinity-Control Projects in the Grand Valley in the Lower Gunnison River Basin and at Meeker Dome Western Colorado
Water Supply Pro - Doc Type
Report/Study
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<br />2401 <br /> <br />A nonparametric test called the seasonal Kendall <br />test is used in ESTREND. The null hypothesis for the <br />test is that there is no trend. Nonparametric methods <br />often are used for trend tests on water-quality data <br />because the data often do not meet assumptions <br />required for parametric methods. To appropriately use <br />parametric methods for multiple station tests with sev- <br />eral variables, every data set for every station would <br />need to be tested for violation of the assumptions of the <br />test. Compared to parametric tests, non parametric pro- <br />cedures had small disadvantages where the data were <br />normally distributed, but can have major advantages <br />where data distributions depart from normality (Hirsch <br />and others, 1991). Further discussion about paramelric <br />and nonparamelric statistical methods are in Iman and <br />Conover (1983), Hirsch and others (1991), and Helsel <br />and Hirsch (1992). <br />Differences in water-quality data between <br />seasons of the year can be a source of variability that <br />can prevent or complicate trend detection (Schertz and <br />others, 1991; Helsel and Hirsch, 1992). Dissolved- <br />solids and major-ion data for the Colorado, Gunnison, <br />and White Rivers indicate distinct seasonal variations, <br />primarily because of dilution by snowmelt runoff dur- <br />ing May and June. Often, most of the seasonal varia- <br />tion in water quality is related to seasonal variation in <br />streamflow; however, seasonality often remains after <br />the effect of streamflow has been removed (Helsel <br />and Hirsch, 1992). In the study area, there could be <br />seasonal effects on dissolved-solids and major-ion con- <br />centrations and loads that could be related to agricul- <br />tural return flows that would not necessarily be related <br />to streamflow. <br />The seasonal Kendall test accounts for seasonal- <br />ity by only comparing water-quality data collected <br />during the same season of each year. For example, for <br />data collected monthly, only data collected in January <br />of each year are compared; only data collected in <br />February are compared, and so on. The seasonal <br />Kendall test statistic for the overall monotonic trend <br />is the sum of all Mann-Kendall test statistics for each <br />season (Hirsch and others, 1982). ]n ESTREND, one <br />value of the constituent being tested is used for each <br />season for each year. For seasons with more than one <br />value, the most central observation with respect to time <br />for that season is used (Schertz and others, 1991). <br />Users of ESTREND can define the number of <br />seasons per year and the length of each season. If the <br />data frequency is uniform, the number of seasons can <br />be equal to the sampling frequency. For monthly data, <br /> <br />such as monthly dissolved-solids loads, the number of <br />seasons is 12. Where sampling frequency has changed, <br />the number of seasons per year is based on the years of <br />least frequent sampling. The goal is to provide uniform <br />coverage of the entire period being tested without bias- <br />ing the results toward years of denser data collection <br />and yet define the seasons so that there will be data in <br />most seasons in most of the years. The seasonal defini- <br />tions should reflect the actual seasonal cycles in <br />streamflow or water quality in the watershed being <br />studied. Although there are general guidelines for <br />selecting seasonal definitions, some element of subjec- <br />tivity can enter into the selection. <br />Dissolved-solids and major-ion concentrations <br />often are highly correlated with streamflow. In the <br />Upper Colorado River Basin, increasing streamflow <br />often causes decreasing concentrations because of <br />dilution, especially during snowmelt runoff. Because <br />streamflow is used to compute dissolved-solids loads, <br />dissolved-solids loads also will be correlated with <br />streamflow. The purpose of the monotonic trend tests <br />on salinity data collected at the gaging stations on <br />the Colorado and Gunnison Rivers is to determine <br />if the salinity-control projects have affected salinity <br />in the Colorado River. The variability of concentra- <br />tions and loads caused by streamflow might overwhelm <br />any human-induced changes; therefore, removal of <br />the variance due to streamflow is desirable. If the <br />streamflow-induced variability in salinity data is <br />decreased, then the chance of detecting a trend that <br />resulted from some effect other than streamflow is <br />enhanced. Generally, monotonic trends on flow- <br />adjusted water-quality data should not be done during <br />a period when major changes to the stream-discharge <br />regime occurred, such as reservoir construction or <br />major changes in water diversions or water use. <br />The procedure in ESTREND to decrease <br />streamflow-related variability in the data set is done <br />in three steps. First, a relation is determined for con- <br />centration (or load) to streamflow through a linear- <br />regression fit or a nonlinear smoothing method. Then <br />the residuals (the observed value minus the predicted <br />value from the regression) are computed for every data <br />pair. The residuals are referred to as the flow-adjusted <br />concentrations (Liebermann and others, 1988; Schertz <br />and others, ]991). The flow-adjusted concentrations <br />then are tested for trends with the seasonal Kendalltesl. <br />There are ]2 possible regression models available for <br />flow adjustment in ESTREND. Models I through II <br />are functions that have various linear, logarithmic, <br /> <br />, <br /> <br />METHODS DF TREND ANALYSIS 11 <br />
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