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<br /> <br />" <br /> <br />FL Ogden ef Dt.1 JOllmo/ of Hydrolog)' 22E (2()()()) 82-]00 <br />300 <br /> <br />'" 200 <br />"E <br />. <br />" <br />. <br />. <br />~ <br />c5 100 <br /> <br />U""'''~'.Mi <br />DiochargeMeUUfS""'nl I \ <br />alSlallOnUl \ <br />1\ <br />I \ <br />I \ <br />{ \ <br />{ \ <br />I t"c <br />{ <br />{ <br />{ <br />I <br />I <br />I <br />{' <br />{ <br />/ <br /> <br />o <br />18:00:00 <br /> <br />--- SIationU1 <br />Station U2 <br />- Slalion U3 <br /> <br /> <br />21 :00:00 00:00:00 03:00:00 <br />Time, July 28/29,1997 (MOT) <br /> <br />Fig. 5. Reference simulalionrcsuhs. <br /> <br />affected this flood is the large detention basin behind <br />the 6 ill high railroad embankment (see Fig. I). The <br />Importance of other lakes and detention basins was <br />secondary but they were also included in model A <br />large lake formed upstream from the railroad emba~k- <br />mem as the three 2.1 ill (7 ft)diameterculverts did not <br />have the capaen}' to pass the inflow to the detention <br />~asln. Dunng the morning storm on 28 July, simula- <br />lIOns show the lake behind lhe main detention basin <br />grew to an area of about 0.02 km2 and then shrank to a <br />ffil.n.Jm,um area of 0.009 km2 before starting to expand <br />agam as the major storm stalled in the early evening <br />of ~8 July 1997. The lake ultimately expanded 10 an <br /> <br />area of more than 0.6 km2 inundating two kilometers of <br />channel reach and overtopping the railroad embank- <br />menl Shortly aftelWards, at about 22:55 MDT the box <br />culvert started to unplug. The unplugging of the culvert <br />~as assumed to take 18 min and the area of the opening <br />IS assu~ed to grow exponentially before expanding to <br />the full area of the c~lve~ cross-section. The timing of <br />the culvert unplugglOg IS estimated from records of <br />emergency telephone calls in the immediate area <br />downstream from the railroad embankment. <br />Referen.ce simulation results ploned Fig. 5 show <br />~hat the discharge at the watershed outlet is greatly <br />lllfluenced by the detention basin and by the culvert <br /> <br /> <br />Fig. 6. Polanm"lrlC SlOmHOlal rad.ar esti I d . f Jl <br />ma e ram a accumulalions (mmI17:JO-23:30 MDT. 28 July 1997. <br /> <br />I-- 3 km---l <br /> <br />300 <br /> <br />FL 08d~n ~r ,,1.1 j""ffl,,1 ,,{Hydrology 228 (2000) 82-)00 <br /> <br />93 <br /> <br />ft!!!. 200 <br />E <br />. <br />o <br />. <br />~ <br />o 100 <br /> <br />{ <br />I <br />I <br />I <br />I <br />I <br />, <br />/ <br /> <br />o <br />18:00:00 <br /> <br />... AdJUSt. WSR-68D <br />_ _ - Unadj. WSR-88D <br />_ Rete/ence Run <br /> <br />", <br />\ <br />\ <br />\ <br />\ <br />, , <br />"- <br /> <br />21 :00:00 00:00:00 03:00:00 <br />Time. July 28129, 1997 (MDT) <br /> <br />Fig. 7. Simulalion resuhs at slalion VI using unadjusted and adjuSled WSR.88D precipitation estimates. <br /> <br />unplugging. Notice the very sharp rise in outflow at <br />station U2 (see Fig. 1) due to culvert unplugging. <br />Given the uncertainty regarding the timing and rate of <br />culvert unplugging, the discharge at station U 1 is the <br />moSI useful in evaluating the effects of input uncertainty <br />on model performance. Furthermore, most of the runoff <br />originates upstream from slation U 1. <br />Fig. 6 shows polarimetric radar-estimated storm total <br />rainfall accumulations in rom between 17:30 and 23:00 <br />MDT over the Spring Creek watershed. The gradient in <br />stonn-total rainfall over the eastern half of the watershed <br />is very steep, up to 40 mm/km. The land-use map is <br />shown in the background in Fig. 6 to illustrated the <br />fact that large portions of the watershed are urbanized <br />where the most intense rainfall occurred. <br />The simulated peak discharge in the reference run <br />at station U I was 17.5% higher than the USGS indir- <br />ect measurement but still within the uncertainty range <br />of ::!:25%. The model estimated the peak discharge at <br />the outlet of the catchment to be 172 m3Js (3.5% <br />higher than the indirect estimate) which was well <br />within the uncertainlY range of :!:15%. Reference <br />run simulation results are listed in Table 3. <br /> <br />12. Simulations witb WSR-88D radar-rainfall <br />estimates <br /> <br />The uncalibrated single-polarization WSR-88D <br /> <br />observations significantly underestimated the rainfall <br />from the stann. The WSR-88D estimated rainfall <br />volume on the watershed area was 42% less than the <br />reference rainfall volume. The runoff volume calcu- <br />lated using unadjusted WSR-88D rainfall estimates <br />was 52% less than the reference run value indicating <br />the rainfall estimation error is amplified as it propa~ <br />gates through the runoff model. <br />The WSR.88D estimates were adjusted by multi. <br />plying by a constant bias-adjustment factor (Smith et <br />at, 1996) equal to 1.72 so that the slOrm total rainfall <br />volume is equal to the reference rainfall volume. Fig. <br />7 compares simulated hydro graphs at station U I for <br />the reference run, unadjusted and adjusted WSR-88D <br />rainfall inputs. Although the peak discharge at station <br />VI is 7% higher using the adjusted WSR-88D rainfall, <br />the total runoff volume is 1.2% lower than the refer- <br />ence value. This finding indicates that the bias-adjust- <br />ment faclOr is nol constant over the life of the storm. <br />Notice that the simulated hydrograph produced using <br />storm-Iotal bias adjusted WSR-88D rainfaU estimates <br />changes the temporal distribution of runoff, as evident <br />by differences between the reference and adjusted <br />WSR-88D hydrographs on Fig. 7. Differences in <br />runoff volume and hydrograph timing between simu- <br />lations have a large effect on the simulated conditions <br />in the detention basin making it meaningless to <br />compare the simula'ted hydrographs at the watershed <br />outlet for these simulations. The volume of infiltration <br />