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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 />N <br />o <br />()l <br />o <br />c <br />.0 <br />o+:; <br />- 0 <br />IL ~ <br />..- <br />o c <br />0" <br />~ 0 <br />~ C <br />" 0 <br />(flU <br /> <br /> <br />High Flow <br /> <br />Low Flow <br /> <br />Antecedent Flow Index <br /> <br />Figure 1.6. Hypothetical antecedent flow in- <br />dex (taken fro~ Lane 1975), <br /> <br />(1970) modeled average monthly salinity mass <br />flow on a major subbasin of the Upper Colo- <br />rado River. A distributed parameter hydro- <br />log!c. watershed model was coupled with a <br />salInIty uptake model. Flow separation was <br />lit il ized in the hydrologic model, and sepa- <br />rate salt loads were associated with surface <br />flow, groundwater flow, and interflow. Salt <br />concentrations in groundwater and interflow <br />wer.e assumed constant. The surface inflow <br />c oocent 1'8 t ions for ungaged S Qurces were <br />related to water flow rates by utilizing <br />exponential regression equations. To incor- <br />porate flash flows from small watersheds, the <br />average monthly salt concentrations were <br />increased. It ,was assumed initially tha-t <br />salt load increases within the valley bottoms <br />could be attributed entirely to agriculture. <br />However, on the basis of this assumption, the <br />initial simulated salinity concentrations <br />associated with subbasin outflows were low by <br />factors ranging from two to ten. To add to <br />the salt loading, a channel salt uptake <br />mechanism was assumed according to the <br />following hypothesis: <br /> <br />~ <br /> <br />.. .Much of the water which enters <br />the alluvium as influent flow in <br />the upstream portion of the basin <br />returns again to the stream channel <br />in the lower reaches, and that <br />within a particular subbasin the <br />rate of interchange between surface <br />water and, groundwater may be <br />influenced by water levels in <br />the stream channels. Hence, during <br />periods of high streamflow some <br />increase in the interchange rate <br />might he expected (Hyatt 1970, p, <br />34) . <br /> <br />The following two empirical equations <br />were used to account for this loading: <br /> <br />Kp = n (Qr>m <br /> <br />(J .15) <br /> <br />in which <br /> Kp <br /> Qr <br /> m <br /> n <br /> <br />.. <br /> <br /> <br />Percentage of surface flow inter- <br />changed or recirculated through <br />the stream alluvium or groundwater <br />Monthly surface flow rate in cfs <br />Slope of the line of Kp plotted <br />agaInst Qr on log-log paper <br />Intercept on the Kp-axis of the <br />log-log plor <br /> <br />and <br /> <br />SNS <br />r <br /> <br />. , , . ' (1,16) <br /> <br />Kp Qr Cg <br /> <br />in which <br /> <br />SNS <br />r <br /> <br />Rate of salt flow contributed from <br />natural sources within the basin <br />Average water salinity level <br />within the groundwater basin or <br />stream alluvium. This quantity <br />assumed to be constant throughout <br />the simulation period, is esti- <br />mated from either well samples or <br />the average salinity level of the <br />base flows of the streams within <br />the subbas in. <br /> <br />C <br />g <br /> <br />The water and salt budgets Hyatt derived <br />by applying this model to the Price River <br />Basin are tabulated in Table 1.2. These <br />figures suggest that irrigation is a rela- <br />tively minor salt contributor to the waters <br />of the Price River. The report concluded <br />that "... more research is needed to de- <br />lineate between natural and man induced <br />salt loading before stringent and perhaps <br />unnecessary controls are placed on human <br />activities" (Hyatt 1970, p. 9"1). <br /> <br />, Thom~s, et a1. (1971) proposed a hydro- <br />logIc-~al~nlty model that can be applied to <br />bo~h. IrrIgated and nonirrigated areas and <br />utIlIzed tQermodynamic ionic relationships <br />for estimating salt uptake concentrations. <br />The model was successfully applied to the <br />Bear River, Utah, and simulated Ca, Mg, Na, <br />804, Cl, and HC03. The model however <br />is unwieldy due to its extensiv~ data re~ <br />quirements. <br /> <br />,Hill (1973) applied a hydro1ogic- <br />salInIty model to the LIttle Bear River, <br />Utah. Natural weathering was not considered, <br />and salt uptake was assumed to be limited <br />to agricultural and groundwater sources. <br />Flow separation and average monthly salt <br />loading factors were used. <br /> <br />Narasimhan (1975) added a biochemical <br />nitrogen subroutine for agricultural per- <br />colated waters to the Thomas et al. (1971) <br />model. The expanded model was successfully <br />applied to the Twin Falls tract of the Snake <br />River Basin in I daho. However, the amount <br />and complexity of the required data are also <br />a problem in applying this model. <br /> <br />7 <br />
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