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Last modified
7/14/2009 5:02:37 PM
Creation date
5/20/2009 10:12:53 AM
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UCREFRP
UCREFRP Catalog Number
9626
Author
Butler, D. L.
Title
Effects of Piping Irrigation Laterals on Selenium and Salt Loads, Montrose Arroyo Basin, Western Colorado.
USFW Year
2001.
USFW - Doc Type
Denver, CO.
Copyright Material
NO
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Table 2. Mean selenium and salinity concentrations <br />in irrigation water from the AM lateral and Loutzenhizer <br />Canal, 1999-2000 <br />[<,less than] <br />Selenium Salinity <br />Site (micrograms (milligrams <br />(fig. 2) per liter) per liter) <br />1999 2000 1999 2000 <br />AM1 2.2 1.5 209 188 <br />AM3 3.6 2.4 262 246 <br />LZC <1 0.9 261 250 <br />the selenium and salinity concentrations (table 2) in <br />monthly samples collected from April to October in <br />1999-2000 from two sites on the AM lateral and one <br />site on the Loutzenhizer Canal (fig. 2). The ground- <br />water concentrations (Cgw) were the mean concentra- <br />tions of the samples collected in November through <br />March at each site (table 1) and were assumed to <br />approximate selenium and salinity concentrations in <br />the ground-water component during the irrigation <br />season. The Qsw and Qgw variables are unknowns. <br />Equation (1) was solved for Qsw; Qsw = Qi - Qgw, <br />and after substituting that expression for Qsw into <br />equation (2), there was only one unknown, Qgw, <br />remaining in equation (2). Once Qgw was calculated, <br />Qsw was computed as Qi - Qgw. After computing <br />Qsw and Qgw, the mean selenium and salt loads in the <br />surface-water and ground-water components for the <br />irrigation season were computed. Load equals flow <br />times concentration times a conversion factor <br />(0.00539 for selenium; 0.0027 for salinity). For <br />example, the mean selenium load in surface water <br />equals Qsw times Csw times 0.00539. This process <br />was done for the pre-project and post-project periods <br />for all sites except MA4, the control site. The mean <br />loads derived by this method for the irrigation season <br />(sum of mean surface-water load and mean ground- <br />water load) and the nonirrigation season are listed in <br />table 3. The mean loads for site MA4 were computed <br />using the periodic samples collected at that site for <br />each season. Readers are advised not to use the data in <br />table 1 to compute the mean loads shown in table 3. A <br />mean load computed using the mean streamflow and <br />concentration data from table 1 may or may not equal <br />the loads in table 3 because computing mean loads by <br />that method is not equivalent to the method used to <br />compute the mean loads listed in table 3. <br />Once the irrigation-season analyses were done, <br />the mean surface-water and ground-water loads were <br />converted to annual loads. The means of the surface- <br />water and ground-water loads for the irrigation season <br />(April through October) were extrapolated to loads for <br />Table 3. Mean selenium and salt loads for irrigation-season <br />(April through October) and nonirrigation-season (November <br />through March) samples at the five monitoring sites <br />[Pre, pre-project period; Post, post-project period] <br />Site <br />(fig <br />2) Selenium load <br />(pounds per day) Salt load <br />(tons per day) <br />. Pre Post Pre Post <br /> Irrigation season <br />MA4 0.09 0.07 7.3 8.3 <br />D2MA .38 .21 9.4 7.8 <br />MA3 .57 .38 21.2 18.7 <br />D1MA .60 .43 16.1 14.3 <br />MA2 2.30 1.65 62.1 52.8 <br /> Nonirrigation season <br />MA4 .19 .19 8.0 7.9 <br />D2MA .41 .12 9.2 4.2 <br />MA3 .55 .32 16.5 12.2 <br />D1MA .23 .22 7.7 7.3 <br />MA2 1.31 .95 32.6 26.9 <br />INTRODUCTION 7
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