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WSP07478
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Last modified
1/26/2010 2:27:31 PM
Creation date
10/12/2006 2:25:27 AM
Metadata
Fields
Template:
Water Supply Protection
File Number
8272.600.60
Description
Colorado River Basin Salinity Control Program - Basin Member State Info - Utah
Basin
Colorado Mainstem
Water Division
5
Date
3/1/1982
Title
Salt Uptake in Natural Channels Traversing Mancos Shales in the Price River Basin - Utah
Water Supply Pro - Doc Type
Report/Study
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<br /> <br />significsnt differences smong shsles and a <br />continuing significsnt difference between <br />rv treatments on the seventh day. <br /> <br />c:> The differences were probed once more by <br />~testing dissolution amounts during the second <br />Q040-day treatment period. The results in <br />Table 4.8 cover the entire 85-day period <br />and thus, according to the results reported <br />in Table 4,6, would be significant if s <br />constant dissolution were added during the <br />second 40-day period. Therefore, Hicks' <br />(1973) model was used to test for significant <br />differences among shales, between treatments, <br />and in interaction between the two. Again, <br />all three differences were found significant. <br /> <br />The results of these tests have impor- <br />tant implications. Dissolution rates vary <br />significantly among shales and with the <br />history of wetting and drying as the material <br />moves downstream. The many shale sources and <br />histories will make it very difficult to <br />estimate dissolution rates in a -given stream. <br />Also, the tendency of wetting and drying <br />cycles to increase dissolution would cause <br />more of the salts in the bed material of <br />ephemeral channels to be leached out before <br />the bed material reaches a larger stream. <br />Msterial directly entering a perennial stream <br />may move through the system with much more of <br />its salt content'in tact. These materials <br />may continue as an important salt aource <br />downstream on the Colorado River for years. <br /> <br />Time rates of dissolution <br /> <br />Whitmore (1976) found that when salt <br />dissolution rates are plotted against the <br /> <br />square root of time a broken curve of <br />the sort illustrated by Figure 4.16 results. <br />Accordingly, an attempt was made to fit the <br />dissolution data with a square root model of <br />the form: <br /> <br />C a K1 TO.5. . . . . . , . . . . . (4.3) <br /> <br />in which <br /> <br />C The specific conductance in <br />~mhos, at time T <br />T Time in minutes <br />Kl A dissolution <br /> <br />1 n order to determine the effect of <br />grain size on dissolution rates, accumulated <br />conductivities were also measured in the <br />laboratory for shale samples separated by <br />grain size with the results shown in Table <br />D.4. Equation 4.3 fit the data with a single <br />cons tant K1 rather than wi th the breakpoint <br />shown in Figure 4.16. Eighty percent of the <br />72-hour conductivity was obtained after a <br />mean of 9.4 hours, with a standard deviation <br />of 7.1 hours, as compared to the few minutes <br />found by Whitmore (1976) for Mancos soil. <br />The advanced weathering state of the channel <br />material used by Whitmore probably accounts <br />for the rapid dissolution that he observed. <br /> <br />The results of the student t-test <br />analysis for differences by grain size <br />of the 3D-second and 72-hour conductivity <br />va lues are presented in Table 4.9. The <br />significant increase in 3D-second dissolution <br />for smaller grain sizes is evidence that the <br />initial rate of salt dissolution increases <br />with partial surface area. <br /> <br /> <br />~ 2000 I <br />u <br />. K2 <br />LO j <br />t\J 0 . \ <br />@ 0. , <br />1500 .' <br />Ul <br />0 <br />.c <br />E <br />:t. 1000 <br />~ <br />>- <br />.... <br />:> 500 <br />~ <br />::::> <br />0 <br />z 0 <br />0 0 100 200 300 <br />u <br /> SQUARE ROOT OF TIME (mino.l5) <br /> <br /> <br />Figure 4,16, Accumulated conductivity from laboratory salt dissolution. <br /> <br />36 <br />
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