Laserfiche WebLink
3.5 <br />3.0 <br />a <br />2.5 <br />w <br />CL <br />O <br />Z) 2.0 <br />0 <br />CL <br />z <br />0 1.5 <br />U 1.0 <br />0.5 <br />PRE-PROJECT PERIOD I POST-PROJECT <br />O O I PERIOD <br />O O I <br />qI <br />0 000 O 1 <br />O 00 O 1 <br />I <br />0 0 0 ®0 1 00 0 0 <br />0 ° b <br />I ? <br />00 O 0 <br />O I? O <br />O <br />O O 1 0 O®O <br />O O 001 <br />S o <br />0 0 BOO 0 0 <br />O 00 <br />O 0 I Q?,.p <br />O? <br />I <br />I <br />I <br />1993 1994 1995 1996 1997 1998 1999 2000 <br />Figure 4. Selenium loads in Montrose Arroyo at Niagara Street (MA2), 1993-2000. <br />nonirrigation-season data sets (table 3) for the statis- <br />tical test. The selenium loads for the post-project <br />samples were significantly less than the pre-project <br />loads for both seasons (p values 0.001 for both <br />seasons). Mean selenium concentrations and loads in <br />the nonirrigation-season samples at site MA2 (tables 1 <br />and 3) were significantly less in the post-project period <br />than in the pre-project period (p values 0.005 and <br />0.010). <br />Salt loads also decreased at all sites except at the <br />control site (table 5; fig. 5). However, the relative <br />percentage of change in total salt loads was consider- <br />ably less than the percentage of change in total sele- <br />nium loads. The maximum percentage of change in <br />salt load was the 32-percent decrease in drainage ditch <br />D2MA. A greater percentage of the decrease in salt <br />load was caused by reduced lateral waste discharges <br />(the change in the surface-water component) <br />compared to selenium load decreases; and at the <br />outflow site (MA2), about 37 percent of the salt-load <br />decrease (1,070 divided by 2,900) was in the surface- <br />water component (table 5). By comparison, only 8 <br />percent of the decrease in selenium load at site MA2 <br />was in the surface-water component (16 divided by <br />194, table 4). Based on the loading analysis in tables 4 <br />and 5, a greater percentage of the total salt load is in <br />the surface-water component compared to the total <br />selenium loads. For example, for the pre-project <br />period at site MA2, the surface-water component is 5 <br />percent of the total selenium load but 14 percent of the <br />total salt load. Therefore, the elimination of the waste- <br />water flows from the laterals that were piped had a <br />proportionately greater effect on the salt loads than on <br />selenium loads. <br />Statistical tests indicate that the post-project salt <br />loads are significantly less than pre-project loads, <br />especially during the irrigation season. The mean irri- <br />gation-season salt load decreased from 62.1 tons/d to <br />52.8 tons/d (p value 0.001). Although irrigation- <br />season salt loads were significantly less in the post- <br />project period, salt concentrations in the irrigation <br />season (table 1) were significantly higher in the post- <br />project period than in the pre-project period (p value <br />0.001). The increase in salt concentrations in the irri- <br />gation season was caused by the elimination of waste- <br />water flows from the laterals that were piped, which <br />results in less dilution of the much higher salt concen- <br />trations (about 4,800-4,900 mg/L based on nonirriga- <br />tion salinity concentrations for site MA2, table 1) in <br />ground-water inflow into Montrose Arroyo upstream <br />from site MA2. <br />10 Effects of Piping Irrigation Laterals on Selenium and Salt Loads, Montrose Arroyo Basin, Western Colorado