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Comparison of Two Approaces for Determining Ground-Water Discharge and Pumpage in the Lower Arkansas River Basin Colorado 1997-98
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Comparison of Two Approaces for Determining Ground-Water Discharge and Pumpage in the Lower Arkansas River Basin Colorado 1997-98
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Water Supply Protection
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Comparison of Two Approaces for Determining Ground-Water Discharge and Pumpage in the Lower Arkansas River Basin Colorado 1997-98
State
CO
Basin
Arkansas
Author
Dash, Russell; Troutman, Brent; Edelmann, Patrick
Title
Comparison of Two Approaces for Determining Ground-Water Discharge and Pumpage in the Lower Arkansas River Basin Colorado 1997-98
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terms in equation 5. Site -to -site variability accounts <br />for about 53 percent (100 x 0.001399/ 0.002639) of <br />the sum of the variance components, the date within <br />site variability accounts for about 27 percent of the <br />sum of the variance components, and the random error <br />terms accounts for the remaining 20 percent. <br />Table 4. Estimates of the variances of the site, date, and <br />error random terms in discharge measurements <br />Random terms <br />Variance <br />Site <br />0.001399 <br />Date <br />.000701 <br />Error <br />.000539 <br />Sum 0.002639 <br />The total variance of diffQ around the <br />overall mean (that is, the variance of diffQ without <br />a model) is 0.003037, which indicates that the <br />fixed effects account for about 13 percent [equals <br />100 x (0.003037 — 0.002639) / 0.003037] of the vari- <br />ance of diffQ. This is a relatively small part of the total <br />variability, but the data set is large enough to result in <br />the statistically significant differences listed in tables 1 <br />through 3. Similarly, the site, date, and error variance <br />components expressed as a percent of the total vari- <br />ance are 46 percent, 23 percent, and 18 percent, <br />respectively. Overall, the largest portion of the <br />variance of diffQ is accounted for by site -to -site <br />variability. <br />The random error variance (0.000539 in table 4) <br />measures the amount of variability among different <br />portable flowmeter measurements applied on the <br />same day at the same site. The error variance can be <br />used to determine the range in expected differences <br />between (logarithmically transformed) instantaneous <br />discharge measured using two different portable flow - <br />meters. The estimated variance of the difference will <br />be 2 x 0.000539 because the variance of the difference <br />between two independent random variables is the sum <br />of their variances. This translates into a standard devi- <br />ation of about 3.28 percent. When this measure of the <br />random component of the difference is considered in <br />conjunction with the systematic differences in table 2 <br />for different portable flowmeter methods, an estimate <br />of the total error can be determined. For example, if <br />measurements are made using P and M portable <br />flowmeters, the systematic bias (M —P) is 1.08 percent <br />with a standard deviation of 3.28 percent. If normality <br />is assumed, about 95 percent of the differences <br />between the measurements taken with the two <br />portable flowmeters will be between —5.48 percent <br />and 7.64 percent. <br />The small size of the random error variance <br />component is indicated by the precision with which <br />differences among portable flowmeters can be esti- <br />mated in table 2. The standard errors for portable flow - <br />meter differences range from 0.25 to 0.27 percent, <br />which is considerably smaller than standard errors for <br />make differences (0.88 percent) or type differences <br />(0.82 percent). A strength of the design for this data <br />collection was the application of multiple portable <br />flowmeter methods at the same well on the same date <br />during a short period of time. <br />TEMPORAL VARIATIONS IN POWER <br />CONVERSION COEFFICIENTS <br />The use of PCC's to estimate ground -water <br />pumpage from wells is most accurate when the rela- <br />tion of well discharge to power consumption remains <br />stable. However, over time, hydrologic and pump <br />operating conditions may change, thus altering the <br />PCC relation to well discharge and power consump- <br />tion. As examples, depth to ground water may increase <br />after an extended period of pumping or pump effi- <br />ciency may decrease as the irrigation pump ages. Any <br />well operation that results in significant variations in <br />the PCC over time can result in errors when using the <br />PCC approach to estimate ground -water pumpage. <br />Short -Term Variations in Power <br />Conversion Coefficients <br />Multiple PCC measurements repeated at the <br />well sites during 1997 and 1998 are used to indicate <br />the temporal variability in PCC's during one and two <br />irrigation seasons. The range in PCC's at 104 sites <br />during 1998 is shown in figure 5A. The PCC's for most <br />sites (86 percent) did not fluctuate more than <br />20 percent throughout the 1998 irrigation season; <br />however, for unknown reasons, a wide range in PCC's <br />occurred at about 14 percent of the network sites. At <br />some wells, a lower than expected PCC measurement <br />(site 5) or several lower than expected PCC measure- <br />ments (site 27) resulted in the wide range in PCC's <br />that were measured. The percent difference for the <br />TEMPORAL VARIATIONS IN POWER CONVERSION COEFFICIENTS 19 <br />
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