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<br /> <br />88 <br /> <br />FL Ogd~n n Ill./ Journal of Hydrology 228 (2000) 82-/00 <br /> <br />'lI; <br />!' <br />~ <br /> <br />FL Ogd~11 rl al./ Journal of Hydrolot.Y 228 (2000) 82-JOO <br /> <br />" <br /> <br />than when using ZH alone. Another important dual <br />polarization radar observable is the differential propa- <br />gation phase shift t/)op (degrees) (Sachidananda and <br />Zmi.::, 1986). The specific differential propagation <br />phase shifl, K[lp (degreeslkml is given by one half <br />the spatial gradient of the ctJop_ The tPoP signal is <br />quite noisy. so a low-pass filter was used to smoolh <br />!pop along each ray. The parameter Kop is useful in <br />hydrometeorology, because it is insensitive 10 hail, <br />independent from measurements of the reflectivity <br />factor, and nearly linearly proponionallo high rainfall <br />rates ($achidananda and Zmic, 1986). <br />In a smdy of radar-rainfall estimation errors using <br />difft:rent radar observables, Chandrasekar et al. (1993) <br />estimated the fracliona! standard deviation (FSD) of <br />lwon!y rainfall rate estimate to be 45% for rates up to <br />]0 mm/h and increases to 55'1'c- when Iherate is as high <br />as 150 mmlh. When lH and lOR was used in combina- <br />tion 10 estimale the rain rate, FSD was 60% for rates <br />up 10 10 mmlh and 25% for higher rales. When using <br />Kill' as an estimalor, Ihey estimated FSD values of 80, <br />25 and 15% for rainfall rates of 20,80 and 200 mmlh, <br />respectively. Gorgucci et al. (1994) emphasized that <br />conventional rainfall rate estimates using lH and ZoR <br />are unstable when lOR values are !ow due to measure- <br />ment errors. They suggested a robust estimator which <br />uutperfonn conventional estimators particularly al <br />very low and very high rainfall rates. Chandrasekar <br />(]997) refined that estimator. <br />The three radar observables mentioned above were <br />used to estimate the rainfall rate from the polarimetric <br />radar data. Each observable was used within the range <br />where it is believed to be physically related to the <br />rainfall rate. Dual polarization rainfall rate estimates <br />were obtained according to the following multi-para- <br />meter algorithm: <br />If KDI' > 1.:!50lkm and ZH > 40.0 dBZ the rainfall <br />rate (mmlh) is calculated using the relation by Ryzh- <br />kov and Zmic (1995): <br /> <br />R(Kop,2D1.) = 52.0KSp~f>Zu~+n <br /> <br />If the above conditions are not met, but lOR> -0.5, <br />then the relationship developed by Chandrasekar <br />(1997) is u;,ed: <br />R(Z[)l~,Zt!l = I 17 x JO-C(Z::,~t~)(JO-OAO~ Zu..) (4) <br /> <br />If neither of the above conditions are true, then <br /> <br />~ <br /> <br />with redislribution (Ogden and Saghafian, 1997). The <br />model can be used 10 simulate single events, or comin- <br />uous periods of record. CASC2D accepts rainfall <br />input at any number of painls in space with any <br />temporal resolution, which allows the model to <br />readily accept radar-rainfall estimates. <br />Infiltration into the soil is oplionally modeled using <br />either the Green and Ampt (191 I) method, or the <br />Green and Ampt Redisuibution (GAR) method <br />(Ogden and Saghafian, 1997). The GAR technique <br />is similar to the method described by Smith et al. <br />(1993), with the assumption of rectangular soil moist- <br />ure profiles and the addition of an analytically-derived <br />unsalUrated capillary head term (Ogden and Saghafian, <br />1997). The GAR option allows accurate simulation of <br />infiltralion when there are muhiple ponding periods. <br />The original Green and Ampt (1911) equalion is: <br /> <br />the Battan (1973) Z-R relation given in Eq. (2) is <br />applied. <br />The polarimetric radar measurements are spaced <br />125 m along the radar beam. Rain rate estimates <br />were produced by compUling mean values of 2H. <br />20R and KDf> over seven adjacent radar measuremenls <br />(bins), and applying the abqve polarimelric algorithm. <br />These rainfall estimales are then gridded to a hexago- <br />nal grid with the centers of hexagons 707 m apart, <br />which is approximalely the beam width of the radar <br />over the Spring Creek watershed. Hexagonally <br />centered grids were selected to reduce Ihe bias due <br />10 grid orientation. Rain gage accumulations were <br />compared with the nearesl radar pixel. The polari- <br />metric hourly radar accumulations compare very <br />well wilh hourly rain gage accumulations, as shown <br />in Fig. 3. The slope of the best-fit regression line <br />through the polarimetric hourly rainfall estimates is <br />0.991, indicating thai the polarimetric rainfall algo- <br />rithm produces unbiased hourly precipitation esti. <br />mates compared with the gage observations. <br />Therefore, there is no need 10 multiply the dual polar- <br />. ization estimates by any factor (bias adjustment). <br />From Fig. 3, it is clear that the uncalibrated polari- <br />metric rainfall estimates are significantly more accu- <br />rate than the uncalibraled single-polarization WSR- <br />88D rainfall estimates of this storm based on the <br />operulional algorithm in use at the Cheyenne, Wyom- <br />ing, WSR-88D on 28 July 1997. The polarimetric <br />radar-rainfall eSlimates are also considered superior <br />to rain gage measuremenls because of their finer <br />spacellime resolution. <br /> <br />f~K.[H,(\- 8,) + 1] <br /> <br />where:fis the infiltration rate (ur): K, the soil satu- <br />rated hydraulic conductivity (UT): H. the Green and <br />Ampt capillary head term (L): 8. the soil effective <br />porosity (dimensionless); 8, the soil initial water <br />content (dimensionless); F the cumulative infiltrated <br />depth (L). <br />Eq. (5) was used to model infiltration during the <br />storm that occurred during the evening of 28 July <br />1997, because of high initial soil moislUre contents, <br />and the lack of significant periods of rainfall hiatus. <br />Once ponding occurs in CASC2D, surrace water is <br />accumulated in each model grid cell until the specified <br />retention depth for Ihat cell is exceeded. Thereafter, <br />the overland flow is routed in two orthogonal direc- <br />tions using Manning's equalion with the diffusion <br />wave form of the de St. Venant equations to estimate <br />the friction slope. When overland flow reaches a <br />model grid-cell that contains a defined channel, the <br />flow is passed inlo Ihe channel and routed using a one- <br />dimensional. explicit, diffusive-wave routing lech- <br />nique. A full description of the current capabilities <br />of CASC2D is given in Ogden (1998). <br /> <br />8. Hydrologic model CASC2D <br /> <br />(3) <br /> <br />CASC2D (Julien et aI., 1995; Ogden. 1998) is a <br />physically-based, distributed-parameler, fiilite-differ- <br />ence hydrologic model that simulates infiltration <br />excess (Hononian) runoff. CASC2D operates on a <br />digital elevation model of the watershed, using square <br />grids that Iypically range from 10 to 120 m on a side. <br />The original formulalion of CASC2D was reponed in <br />Julien et a!. (1995). The original CASC2D formula- <br />tion has been significantly enhanced with the addition <br />of continuous soil moisture accounting (Ogden and <br />Senarath, 1997), a variety of channel cross-seclions <br />(Ogden, 1994), and Green and Ampt infiltration <br /> <br />Water levels in Horsetooth Reservoir (Fig. 2) are <br /> <br />9, Calibration of CASC2D on Horsetooth <br />watershed <br /> <br />(5) <br /> <br />recorded digitally every 15 min. The first storm on the <br />morning of 28 July had a significant effecl on the <br />Horsetooth watershed; between 08:30 and 11:30 <br />MDT Ihe water surface elevation in Horsetooth Reser- <br />voir rose approximately 7 cm more Ihan Ihe amount it <br />would have due solely to CST project diversions. This <br />indicates Ibal approximately 1 cm of runoff occurred <br />from the contributing area. Radar observations from <br />the morning of 28 July suppon the assenion that a <br />significant storm passed over the watershed. <br />The soil hydraulic parameters published in Ihe <br />NRCS county soil survey are approximate values; <br />actual values must be obtained by calibration. During <br />the second storm during the evening of 28 July, the <br />water surface elevation in Horsetooth Reservoir rose <br />by 37 em belween 18:30 and 22:30 MDT. This rise <br />exceeds that due to CBT diversions by 35 cm. indical- <br />ing a basin-average runoff of approximately 5 cm <br />from Ihe contribuling area. Given that the morning <br />stonn on 28 July produced significant runoff, it is <br />reasonable to assume that it saturated the upper few <br />cm of the soil column. At Ihe beginning of the evening <br />stonn, the upper soil layer was likely near saturation. <br />This condition presents a unique' opponunity for cali- <br />braling the soil hydraulic conductivity field of the <br />watershed. Under high initial water content condi- <br />tions, the Green and Ampt equation (5) states Ihat <br />infiltration rates are very close to the saturated hydrau- <br />lic conductivity of the soil, and that soil capillary head <br />plays a minor role. The occurrence of the significant <br />storm during the morning on 28 July allows a one- <br />parameler calibr.lIion of the dominant soil hydraulic <br />propeny (saturated hydraulic conductivity), because <br />the soils were nearly saturated at the beginning of <br />the evening SlDnn. <br />After reviewing the characteristics of the soils in <br />the Horsetooth walershed they were assigned one of <br />six textural classifications. The ephemeral stream <br />network in the Horsetooth watershed (Fig. 2) was <br />modeled assuming trapezoidal cross-sections. The <br />polarimetric radar-rainfall fields were used as model <br />input during Ihis calibration. <br />The runoff into the reservoir was simulated for a <br />period of 10 h (14:00-24:00 MDT). The observed rise <br />in the reservoir level was caused by three separate <br />sources: CBT diversion inflows (10 ml/s), direct <br />runoff inlo the lake, and direct rainfall. Each source <br />was considered. The soil hydraulic conductivity <br />