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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 />feeder channela (channel orders 3 and 2, <br />respectively) are shown. The main stem of <br />r\'Coal Creek was subdivided into ten reaches of <br />~qual length, each approximately 0.82 mi long <br />o(Figure 6.2). Each reach waa aasumed to have <br />d uniform channel cross-sect ion' and salt <br />producing potential. A constant Muskinghum <br />routing coefficient was used for each reach <br />(Table 6.1). <br /> <br />Subbasin 9 <br /> <br /> <br /> <br />1 <br /> <br />Subbasin 8 <br /> <br />2 <br /> <br /> <br />Subbasin 1 <br /> <br />Headwater basef10w, channel seepage, and <br />groundwater inflow values are also liste!,! in <br />Table 6.1. Precipitation and precipitation <br />excess values obtained from the RAIN and <br />HYDRGY subroutines are given in Appendix E. <br />Table 6.2 gives routing coefficients for <br />surface runoff and for tributary channels <br />(orders 1, 2, and 3). <br /> <br />For overland flows, coefficienta for <br />predicting salt pickup as a function of <br />geologic member are given by Table 5.2. <br />Channel (orders 1, 2, 3, and 4) salt pickup <br />characteristics are listed in Table 6.3. <br /> <br />The model was run in timestepa of 20 <br />minutes, and steady state conditions were <br />achieved after 90 timesteps. An illua- <br />trative model response for 2 mm of surface <br />runoff is illustrated in Figure 6.3. The <br />salt concentration peaked at the beginning of <br />the flood hydrograph and then rapidly dropped <br />to a low value during the bulk of the flow. <br />A t the ta 11 of the flood hydrograph, the <br />concentration slowly rose again because of <br />reduced dilution. Finally, the concentration <br />dropped as inflows from lateral channels <br />ceased, and the remaining flow drained <br />from storage in the main channel. <br /> <br />In the model, the salt concentration may <br />be linearly adjusted by varying the salt <br />loading coefficients. The second salt <br />concentration rise may be varied independent- <br />ly of the first by adjusting. 1) the time of <br /> <br />3 <br /> <br />4 <br /> <br />Subbasin 7 <br /> <br />~ <br /> <br />Subbasin 2 <br />Subbasin 3 <br /> <br />5 <br /> <br />6 <br /> <br />Subbasin 6 <br /> <br />~ <br /> <br />7 <br /> <br />8 <br /> <br />9 <br /> <br />Subbasin 5 <br /> <br />~ .. <br /> <br />Subbasin 4 <br /> <br />10 <br /> <br /> <br />Figure 6,2. Model representation of Coal <br />Creek. <br /> <br />Table 6.1. Primary channel characteristics. <br />Reach Wetted Groundwater Concentration Channel Muskinghum <br />Number Perimeter Inflow Groundwater Seepage Routing <br />Coefficients Coefficients <br /> A B m3;min mg/l m3/min K(min) X(min) <br />1 2.1 0.4 0.0 2200 -0.00056 30. 0.3 <br />2 2.1 0.4 0.0 2200 -0.00056 30. 0,3 <br />3 2.1 0,4 0,0 2200 -0,00056 30. 0.3 <br />4 2.1 0,4 0.0 2200 -0,00056 30. 0.3 <br />5 2,1 0.4 0.0022 2200 -0.00056 30. 0.3 <br />6 2.1 0.4 0,0 2200 -0.00056 30, 0.3 <br />7 2.1 0.4 0.0 2200 -0.00056 30. 0,3 <br />8 2.1 0.4 0.0 2200 -0.00056 30. 0.3 <br />9 2.1 0.4 0.0 2200 -0,00056 30, 0.3 <br />10 2,1 0.4 0.0 2200 -0.00056 30. 0.3 <br />Headwater base flow = 1. 704 m3fmin. <br /> 58 <br />
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