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<br />001902 <br /> <br />Model Verification <br /> <br />Most digital-computer models, such as those used in this study, must be <br />cal ibrated. This calibration procedure, as discussed by Hines and others (1975a, <br />1975b), is required to adjust certain model parameters so that the model results <br />adequately represent actual conditions. As noted by Shearman (1976), the multi- <br />reservoir-flow model is an accounting model and contains no model parameters that <br />can be cal ibrated. However, the model can be verified if sufficient data are <br />available. The model was verified previously using data for 1970-73 from the <br />reservoir system in the Wi I lamette River basin in Oregon (Shearman, 1976; Jennings <br />and others, 1976). However, a similar verification of the model for conditions in <br />the Yampa River basin could not be made because most of the reservoir system is <br />not in existence. <br /> <br />:-; <br /> <br />:: <br /> <br />'::: <br /> <br />..;: <br /> <br />To provide Some means of testing the model as a predictive tool for theYampa <br />River basin, model simulations were made using historical streamflow data for <br />50 water years (1927-76). This period was chosen for two reasons: (1) The model <br />is constrained by array sizes to a 50-year period; and (2) by starting with water <br />year 1927. the model analysis included the droughts of the 1930's and the 1950's. <br />For this analysis, comparisons between simulated historical and measured mean <br />annual streamflow were made for streamflow-gaging stations at control poi'nt 39 <br />(Yampa River at Steamboat Springs, Colo.) as shown in figure 7; control point 18 <br />(Yampa River near Maybell, Colo.) as shown in figure 8; and control point 42 <br />eLi ttle Snake River near Li ly, Colo.) as shown in figure 9. Approximate locations <br />of the streamflow gages are shown in figure 6. <br /> <br />(" <br /> <br />~>: <br /> <br />!:~;. <br />:., <br />1L:~~ <br />" <br />~::.' <br />;{;~ <br />:~;; <br /> <br />;~~~ <br /> <br />2: <br /> <br />The comparison between simulated historical and measured annual-mean stream- <br />flow values indicates agreement within 5 percent,for control points 39 (Yampa <br />River at Steamboat Springs, Colo.) and for control point 42 (Little Snake River <br />near Lily, Colo.) and agreement within 20 percent for control point 18 (Yampa Riv- <br />er near Maybell. Colo.). The less accura~e comparisons at the downstream control <br />point of the Yampa River may be explained by the effects of numerous small irriga- <br />tion diversions and tributaries that were not measured and could only be approxi- <br />mated in the multi reservoir-flow model. In contrast, the Little Snake River has <br />less irrigation and fewer unmeasured tributaries than the downstream Yampa River <br />locations; the result is closer agreement between the simulated historical and <br />measured streamflow values. <br /> <br /> <br />The unmeasured inflows and outflows were approximated within the multi reser- <br />voir-simulation model by an additive "local-flow" computation procedure that in- <br />volves starting at an upstream point and adding intervening flows in a downstream <br />direction. These intervening flows, called local flows, were determined either <br />directly by using existing streamflow records or were estimated by multiplying a <br />nearby streamflow record by the ratio of the intervening drainage area and the <br />drainage area upstream from the streamflow-gaging station. This assumes a direct <br />correlation between the flows at the streamflow-gaging stations and the interven- <br />ing flows. In some instances, the streamflow-gaging stations were located in or <br />near the intervening area. Records for 22 of the 36 streamflow-gaging stations <br />indicated in figures 3 and 4 were used in the local-flow computation. <br /> <br />23 <br /> <br />