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North Poudre Sediment Study Final Report
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North Poudre Sediment Study Final Report
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Last modified
10/28/2011 10:22:55 AM
Creation date
9/30/2006 9:03:54 PM
Metadata
Fields
Template:
Water Conservation
Project Type
Ag/Muni Grant
Contract/PO #
C153779
Applicant
North Poudre Irrigation Company
Project Name
North Fork Poudre Sedimentation Study
Title
North Fork Cache la Poudre River Sedimentation Study Final Report
Date
1/1/1999
County
Larimer
Water Conservation - Doc Type
Final Report
Document Relationships
North Poudre Sediment Study Contract
(Attachment)
Path:
\Water Conservation\Backfile
North Poudre Sediment Study Prog Report
(Attachment)
Path:
\Water Conservation\Backfile
North Poudre Sediment Study Work Plan
(Attachment)
Path:
\Water Conservation\Backfile
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<br />HEC-6 Robust Simulation <br /> <br /> <br />If the entire suite of field data are utilized, such that the thickness of sediment <br /> <br />from the release within the pools and riffles is input to the model, and deposition and <br /> <br /> <br />erosion are allowed to occur, the model predicts 75-80% of the actual bed change that <br /> <br /> <br />occurred (Figure 7, Simulation 4 of Table 3a). Such a high percentage with a small <br /> <br /> <br />spread implies greater than or equal to 75% modeling accuracy for most of the pool. <br /> <br /> <br />None of the simulations, however, detected the deposition that occurred on the exit slope <br /> <br /> <br />of the Tick Pool at Cross Section 14. One other shortcoming of the robust simulations <br /> <br /> <br />was that while scouring of the pool thalweg occurred and was modeled, repeat surveys <br /> <br /> <br />indicated simultaneous deposition on the pool margins, though not simulated by HEC-6. <br /> <br /> <br />Because it is a purely one-dimensional model, HEC-6 only predicts uniform bed changes. <br /> <br /> <br />These limitations supported the use of a quasi-two-dimensional model to strengthen the <br /> <br /> <br />results. <br /> <br />CST4RS 2.0 Simulations <br /> <br /> <br />Default simulations were not possible within GSTARS 2,0. The model settings <br /> <br /> <br />listed in Table 2 refer to nonequilibrium conditions which are typically used for <br /> <br /> <br />sedimentation in quiescent water, and account for the lag time between when sediment is <br /> <br /> <br />entrained by the flow and when the transport capacity is fulfilled, Initially, Yang's 1983 <br /> <br /> <br />(Yang et al. 1998) sediment transport equation was used to maintain consistency between <br /> <br /> <br />the two models. GST ARS 2.0 simulated between 13-90% of the actual bed change along <br /> <br /> <br />the North Fork (Table 3b), a wide spread indicating large variability between surveyed <br /> <br /> <br />cross sections and model predictions at each cross section, <br /> <br /> <br />Subsequent simulations in GST ARS 2,0 indicaled that the model was sensitive to <br /> <br /> <br />different sediment transport equations. For example, using the Meyer-Peter Mueller <br /> <br /> <br />formulation. and keeping all other settings constant. the model predicted 0% of the actual <br /> <br /> <br />bed change. <br /> <br />II <br />
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