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<br /> * . <br />. * I * 8 <br />@ * <br />0 * <br />0 <br /> @ <br />SPRING SUMMER FALL <br /> <br />\)826 <br /> <br />40 <br /> <br />o <br />z <br />o 30 <br />() <br />Ul <br />Ul <br />II: <br />~ 20 <br /> <br />~~ <br />"-0 <br />U...J 10 <br />in <br />::;) <br />() <br />~ <br />00 -0 <br />Ul <br />o <br />..JZ <br /><1:- <br />o C; .10 <br />z <br />;;: <br />(!) <br /> <br />~ .20 <br /> <br />~ <br /><I: .30 <br />Iii <br /> <br />D DAILY ANALYSIS <br />. STREAMFLOW.EVENT <br />o ANALYSIS <br /> <br />* <br /> <br />* <br /> <br />* <br /> <br />. <br /> <br /> <br />* <br /> <br />; <br /> <br />NOTE: NOT ALL OUTLIERS ARE SHOWN <br /> <br />.40 <br /> <br />WINTER <br /> <br />* <br />* <br /> <br /> <br />~ <br /> <br />8 <br />I <br /> <br /> <br /> <br /> <br />SEASON <br /> <br />Figure 10. Boxplots showing daily mean streamflow gains and losses and daily mean streamflow-event gains and losses <br />for reach 2 of. the study area, 1984-92. <br /> <br />The statistical summary of daily estimates for <br />reach 3 (table 3) indicated that median streamflow <br />gain was at least 2 ft3ts during all four seasons. <br />During winter, gain-and-loss computations were made <br />for 812 days, resulting in a daily median gain of <br />2 ft3ts; during spring, gain-and-loss computations <br />made for 828 days had a daily median gain of 8.7 ft3ts; <br />during summer, gain-and-loss computations made for <br />828 days had a daily median gain of 16 ft3ts; and <br />during fall, gain-and-loss computations made for <br />819 days had a daily median gain of 12 ft3ts (table 3). <br />Statistical analysis, using a one-tailed t-test (Iman and <br />Conover, 1983), was used to assess if daily streamflow <br />gains were significantly greater than zero during some <br />seasons. A one-tailed hypothesis test assumes that the <br />difference is greater than zero. Results of the test <br />using the 1984-92 estimated gain-and-loss data <br />indicated that during all four seasons, the daily gains <br />of streamflow in reach 3 were significantly different <br />from zero at the 95-percent confidence level. <br />In addition to the more than 3,200 daily <br />computations of streamflow gains and losses in <br />reach 3, boxplots are shown in figure 11 that <br />summarize streamflow gain-and-loss calculations <br /> <br />for 88 selected streamflow events between 1984 <br />and 1992. Gain-and-loss computations for 3 winter <br />streamflow events that were analyzed had a daily <br />median gain of 2 ft3ts; for 19 spring streamflow <br />events, a daily median gain of 7 ft3ts; for 57 summer <br />streamflow events, a daily median gain of 15 ft3ts; and <br />for 9 fall streamflow events, a daily median gain of <br />4 ft3ts (table 3). The streamflow-event estimates in <br />reach 3 ranged from a daily gain of 275 ft3ts to a daily <br />loss of 224 ft3ts (table 3). <br />The daily occurrence of streamflow gains in <br />reach 3 could be because of ground-water inflows and <br />. other ungaged streamflows that might occur in an <br />irrigated river reach; the sources likely are from field <br />; tailwater, canal operations, and other ungaged surface- <br />. water sources. No records of tributary inflow were <br />available for reach 3. Ungaged tributary inflow into <br />reach 3 was assumed to be small. During those days <br />; when side-channel inflows from ungaged tributary <br />streams were large, gain-and-Ioss computations <br />indicated a large daily gain; these large reported <br />streamflow gains were outlier values in the gain-and- <br />loss boxplots (fig. 11). <br /> <br />20 Evaluation of Straamflow Travaltlme and Streamflow Galne a~d Losaea along the Lower Purgatoire River, <br />Southeastern Colorado, 1984-92 <br />