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Last modified
1/25/2010 6:46:20 PM
Creation date
10/5/2006 12:41:44 AM
Metadata
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Template:
Floodplain Documents
County
Larimer
Community
Fort Collins
Basin
South Platte
Title
Hydrologic Analysis of the Fort Collins Flash Flood 1997
Date
12/15/1999
Prepared For
Journal of Hydrology
Prepared By
Elsevier Science Publishers
Floodplain - Doc Type
Flood Documentation Report
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<br /> <br />94 <br /> <br />300 <br /> <br />FL. Ogdtn el al. / }OUffl(J/ 0/ Hydrology 228 (1000) 82-100 <br /> <br />. 200 <br />"E <br />. <br />~ <br />. <br />~ <br />6 <br /> <br /> <br />100 <br /> <br />o <br />18:00:00 <br /> <br />~ - ~ Gages (Thiessen) <br />Gagas(IDS} <br />-f:lelerenceRun <br /> <br />, <br />\ <br />\ <br />\ <br />\ <br />\ <br />\\ <br />"~I <br />\\ <br />\\ <br />\\ <br />\\ <br />\'\,,: <br /> <br />21 :00:00 00:00:00 03:00:00 <br />Time, July 28/29, 1997 (MDT) <br /> <br />Fig. 8. Simulation resuhs III ~(alion UI using nUn gage input and two rainfall spalial irllerpolalion methods. <br /> <br />from the bias-adjusted WSR-88D simulation is 4.5% <br />higher than the reference simulation, further indicat- <br />ing that there are differences between the two rainfall <br />fields although the storm total volume ofrainfall is the <br />same. <br />Calibration of the WSR-88D rainfall pgains! rain <br />gages rather than the polarimetric radar estimates <br />indicated Ih<ll the WSR-88D underestimated the <br />storm tolal rainfall by 50% (Landel et at, 1999). A <br />simulation with a bias adjustment factor of 2.0 <br />resulted in a 16% increase in slOrm total rainfall <br />compared wilh the polarimetric radar estimates. The <br />peak discharge for this simulation was overestimated <br />by 18.5% al station VI. <br /> <br />13, Simulations with rain gage input <br /> <br />The spatial description of the rainfall field is poor <br />when Thiessen Polygons are used 10 estimate the <br />spatial distribution of precipitation due to the fact <br />that the entire watershed is essentially covered by <br />only two rain gages, This is equivalent, in a sense, <br />to picking two of the 70 hexagonal radar pixels thaI <br />cover the walershed and assuming that these two <br />pixels represent the entire rainfall field. As expected, <br />the poor gag.e coverage results in differences in the <br />lotal storm rainfit]] and simulated discharge. Simu- <br />lated hydrogr.1phs based on rain gage input are <br /> <br />compared with the reference simulation at station <br />VI in Fig. 8. The simulation using rain gage data <br />and Thiessen polygon interpolation overestimates <br />the storm tOlal rainfall volume by 6.5% and the runoff <br />volume by 6.8%. The peak discharge at slation VI <br />was underestimated by 12.5%. This indicates that <br />the existing rain gage network did not adequately <br />capture Ihe space-time structure of the precipitation. <br />Further proof of the inadequacy of the rain gage <br />spatial resolution is the large difference in simulation <br />results when the Inverse Distance Squared (IDS) <br />interpolation method was applied. IDS weighing is <br />often used as an alternative to Kriging when there <br />are insufficient data to compute the rainfall covariance <br />funclion. The storm tOlal rainfall on the watershed is <br />underestimated by 13% using IDS interpolation rela- <br />tive to the reference simulation and 18.5% compared <br />with Thiessen Polygon interpolation. The simulation <br />with IDS weighting underestimates the runoff volume <br />by 17% and the peak discharge by 34.5% at station <br />VI. In the IDS simulation, the hydrologic model <br />predicts railroad embankment overtopping 30 min <br />later than in the reference simulation. <br /> <br />14, Watershed characteristics uncertainty <br /> <br />Unlike the Horsetooth watershed, the Spring Creek <br />drainage basin is highly urbanized, as shown on Fig. 6. <br /> <br />300 <br /> <br />F.L Ogdtt" <II ",/./ JOllmtll of Hydrology 128 (2000) 82-100 <br /> <br />95 <br /> <br />200 <br />R~ <br />. <br />~ <br />~ <br />is <br /> <br />, - <br />//- <br />/1 <br />// <br />,'I <br />// <br />/- .; <br />,/,' /? <br />,'./ <br />.,-/ <br />,// <br />,1(/ <br />'1 <br />, <br /> <br /> <br />100 <br /> <br />Test #1 <br />-- -- Test #2 <br />--- Test 113 <br />--- Tesl#4 <br />-ReterenceRun <br /> <br />o <br />21:00:00 <br /> <br />22:30:00 <br />Time,July26129,1997(MDT) <br /> <br />00:00:00 <br /> <br />Fig. 9. Simulatiou J:esulls at slation UI using different levels oftand-sulface detait. <br /> <br />This portion of the analysis seeks to identify the effect <br />of watershed characteristics uncertainty on the hydro- <br />logic model results. Given thaI there is uncertainty <br />regarding the actual magnitude of land-suriace para- <br />meters, a series of tests are periormed to determine the <br />model sensitivity to watershed characteristics input <br />magnitude and level of detail for this extreme event. <br />The impact of land-use and land cover can be quan- <br />tified by running the model with different levels of <br />detail of land-use information. Four lests with differ- <br />ent land surface descriptions were chosen for compar- <br />ison to the reference simulation, which includes all <br />available land surface details. The literature indicates <br />that land-surface details are less imponant for extreme <br />events (e.g. Saghafian et aI., 1995; Winchel et aI., <br />1998). These simulations were conducted to evaluate <br />this premise using real data from an extreme event in <br />an urbanized watershed. All four tests used polari- <br />metric radar.rainfall as input. <br />In the first and second tests, impervious areas were <br />omined. Soil hydraulic parameters from the Horse- <br />tooth calibration were used. Soil parameters, overland <br />flow roughness coefficient and retention depth were <br />varied in space as in the reference run using the values <br />listed in Tables I and 2. In the second lest, spatially- <br />uniform retention depth is assumed, calculated as the <br />arithmetic mean of the spatially-varied retention used <br />in test I. Results shown in Fig. 9 indicate that differ- <br />ences between these two simulations are minor. The <br /> <br />use of spatially-averaged relention has an effect only <br />early in the stonn. Given the extreme quantity of rain- <br />fall during this storm, rt;;tention is quickly over- <br />whelmed. Comparing tests I and 2 with the <br />reference simulation (Fig. 9) reveals that omission <br />of impervious area reduces the peak dis~harge by <br />9% relative to the reference simulation. Numerical <br />values for the peak discharge, runoff and infiltration <br />volumes, and runoff efficiencies at station V 1 are <br />given in Table 3. Note that the rainfall volume is <br />identical in each simulation. <br />In the thud and fourth tests, impervious areas are <br />included, but soil hydraulic propenies were taken as <br />the arithmetic mean of the calibrated values and <br />applied unifonnly over the watershed. Spatially <br />varied overland flow roughness was input for both <br />tests 3 and 4. Spatially unifonn overland flow reten- <br />tion was applied in test 3, while retention storage was <br />omitted in test 4. The hyrlrographs shown on Fig. 9 <br />indicate that assuming spatially uniform soil hydraulic <br />characteristics has a significant impact on the <br />predicted hydrograph. The peak discharge in lests 3 <br />and 4 are both approximately 12% lower than the <br />reference simulation. Retention plays a minor role <br />compared to the effect of spatially uniform soil <br />hydraulic characteristics. The omission of retention <br />does not compensate for the errors caused by applying <br />spatially uniform soil properties. <br />The influence of errors in K, on runoff predictions <br />
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