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<br /> <br /> FL Ogdell el al./ JowrMl of Hydrology 228 (2000) 82-]00 87 <br /> 120 <br /> 0 <br /> 100 <br />E <br />S 80 , <br />.. " <br />'E 0 <br />'. <br />a: 80 <br />~ 0 <br />- <br />, 0 <br />0 <br />J: <br />" 40 <br />~ <br />. <br />a: <br /> 20 <br /> + + <br /> + + <br /> 0 100 120 <br /> 0 20 40 80 80 <br /> Gage Hourly Rainfall (mm) <br /> <br />86 <br /> <br />FL Ogdell el a/./ JOWrMl of Hydrology 228 (2000) 82-100 <br /> <br />Bras (1995); BJoschl et al (1995), and Seyfried and <br />Wilcox (1995). <br />Horsetooth Reservoir, shown in Fig. 2. provides <br />irrigation storage and serves as the water supply for <br />the City of Fort Collins. II is a permanent water <br />storage facility that receives most of its supply from <br />trans-basins transfers from the upper Colorado river <br />via the Colorado-Big Thompson (CSn diversion <br />project. Horsetooth lake is formed by four dams on <br />a ridge in the foothills of the Rocky Mountains. The <br />sUIface area of the lake on 28 July 1997 was 7.4lcm2, <br />with a contributing area of 37.4 km~. This mountai- <br />nous watershed contains six different soil types, five <br />of which are common to the Spring Creek watershed. <br />As shown in Fig. 2. the Horsetooth watershed is adja- <br />cent to the Spring Cre~k and was affected by the same <br />stonns as Spring Creek on 27-28 July 1997, Interest- <br />ingly, when the Horsetooth Reservoir was constructed <br />in the early 19505, the Spring Creek watershed was <br />hydraulically cut in half. <br />Soil texture maps for both Spring Creek and Horse- <br />tooth watersheds were obtained and digitized. Flood <br />plain maps at I :100 scale. developed by others as pan <br />of the Spring Creek master drainage plan, were used <br />to develop channel cross-sections and 10 obtain details <br />of the major detention basins. Land-use data reveal <br />that 23% of the Spring Creek watershed area is <br />covered by impervious surfaces. The location of the <br />only stage-recording station on the main channel of <br />the Spring Creek was considered the watershed outlet. <br />UnfoI1unately, this slage recorder was damaged by <br />floodwaters, and no data were collected after 22:30 <br />MDT on 28 July 1997. <br /> <br />7, Radar-rainfaU <br /> <br />The spatial and temporal resolution of rainfall dala <br />has a great impacl on the accuracy of physics-based <br />distributed hydrologic models as verified by many <br />researchers. Woolhiser (1996) adeptly stated that <br />expecting a physically based hydrologic model to <br />correctly predict storm runoff using erroneous rainfall <br />data is akin to expecting a beam flexure equation to <br />predict the correct beam displacement under an erro- <br />neous loading. The magnitude of runoff prediction <br />errors resulting from rainfall spatial and temporal <br />resolution errors depends on various factors due to <br /> <br />the complexity of the flood producing system, i.e. <br />the interaction of the watershed topography and <br />geomorphology, the runoff production mechanism, <br />the ratio of the rainfall rate to the saturated hydraulic <br />conductivity of the soil (Saghafian et al., 1995) and <br />the spatial_and temporal variability of the rainfall <br />field. This wide range of factors might be the reason <br />for varied conclusions among researchers who sfudjed <br />the impacts of spatial and temporal variability on <br />runoff. Although some researchers have downplayed <br />lhe importance of averaging in certain situations, <br />many researchers have shown the opposite in other <br />studies. Ogden and Julien (1994) identified twO <br />diSlinct causes of error due to precipitation spatial <br />aggregation, "storm smearing" and "watershed smear- <br />ing". Stann smearing occurs because spatial aggrega- <br />tion tends to reduce areal-average rainfall rates. <br />Watershed smearing causes uncertainty in the location <br />of precipitation over the catchment due to aggrega- <br />tion. Winchel et al. (1998) showed that spatial and <br />temporal averaging of rainfall affects modeling results <br />more for Hortonian runoff production than for satura- <br />tion excess runoff production. Radars and rain gages <br />have very different sampling characteristics in both <br />space and time. As an example, it is possible that <br />instantaneous radar measurements taken every <br />30 min can produce more erroneous results than lhe <br />use of hourly integrated averages of rainfall rates <br />(Sharif and Ogden, 1998). <br />Only four recording rain gages cover lhe Spring <br />Creek watershed area when using Thiessen poly- <br />gons to determine the area of influence of each <br />rain gage, Two of lhese four gages cover 90% <br />of the watershed. Furthermore, extremely high <br />rainfall intensity gradients were observed on 28 <br />July 1997. Given the likely inadequacy of the <br />rain gage network, investigation of the accuracy of <br />radar-rainfall estimates was necessary for this study <br />(Pessoa et al.. 1993). Both available single- and dual- <br />polarization rainfall rate estimates were verified using <br />rain gage measurements. <br /> <br /> <br /> <br />Fi;. 3. Radar-raiofall estimates vs. rain galle observations for uncalibJaled polarimetric and WSR-88D radu.rainfall algorithms. <br /> <br />radar located near Cheyenne, WY, which is 85 km <br />north-northeast of Fort Collins. The WSR-88D is a <br />single-polarization radar which observes the reflec- <br />tivity factor, Z, which is theoretically given by: <br /> <br />Z= V-I iD~ <br />1'=1 <br /> <br />where V is the volume of the sample element (cubic <br />meters), 11 is the number of raindrops in the sample <br />element, and Dj is the diameter (in millimeters) of the <br />jth drop. The reflectivity factor is converted to rainfall <br />rate R through an empirical R-Z power function of the <br />form: <br /> <br />R=aZb <br /> <br />The R-Z parameters used are a = 0.017 and b = <br />0.714 for R in mmlh and Z in mmt-/m3. These para- <br />meters correspond to the relation Z = 300R1.4 (Batlan, <br />1973) which was in use at the Cheyenne. Wyoming, <br />WSR-88D site on 28 July 1997. WSR-88D openlfors <br />have the option of using a tropical rainfall l-R rela- <br />tion (Fulton et a1. 1998), however, this relation was <br />not in use during !he Fort Collins stonn. <br />The operational WSR-88D rainfall products (Smith <br />et al., 1996) underestimated the total rainfall for this <br />storm by a factor of 2.0 compared to rain gage <br />accumulations, Hourly WSR-88D radar-rainfall esti- <br />mates compared with hourly measurements at the <br /> <br />7.1. WSR-88D raillfa" estimates <br /> <br />The precipitation field was estimated from the <br />three-dimensional volume scan reflectivity fields <br />observed by the S-band US National Weather Service <br />WSR-88D (Weather Surveillance Radar, 1988-Doppler) <br /> <br />(I) <br /> <br />seven rain gages nearest to Spring Creek are shown <br />on Fig. 3. WSR-g8D underestimation of rainfall can <br />be attributed to the distinctive doud microphysics of <br />extreme storms, e.g. anomalous drop size distribution, <br />the vertical structure of the storm (Smith et aL. 1996), <br />abnonnal propagation of the radar beam (ground <br />clutter) and radar calibration error. Petersen et al. <br />(1999) present a detailed discussion of radar-rainfall <br />estimation errOrs for the Fort Collins storm. <br /> <br />7.2. Polarimetric radar-rainfall estimates <br /> <br />(2) <br /> <br />The polarimetric weather radar observations used <br />in this study were recorded by the CSU-CHILL <br />research radar facility located near Greeley, Colorado, <br />which is approximately 35 Ian east-southeast of Fort <br />CoHins. The CSU-CHILL S-band radar is dual, line- <br />arly polarized with one-degree beam width. The radar <br />measures the reflectivity in twO orthogonal (horizontal <br />and vertical) polarizations, ZIl and lv. respectively. <br />When the two reflectivities are measured in an <br />approximately simultaneous fashion, the differential <br />reflectivity (in decibels) can be derived by lOR = <br />10 10glO(ZH/Zv), Differential reflectivity ZOR provides <br />an indicator of raindrop oblateness and thus raindrop <br />size (Seliga and Bringi, 1976). For an assumed rain- <br />drop size distribution (RSD). lOR provides an estimate <br />of one of RSD parameters, and when combined with <br />ZH results in a more accurate estimate of rainfall rate <br />