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<br />Time and Space Increments <br /> <br />The.incremenls of time and space need 10 be <br />carefully selected during model design. Data, such <br />as temperature and precipitation readings, usually are <br />available as point measurements in time and space. and <br />inlegration in both dimensions usually is accomplished <br />by the method of fmite incremenl.s. <br /> <br />The complexity of a model to represent a hydro- <br />logic system varies with Ihe magnitude of the time and <br />space increments utilized. Large increments, how- <br />ever, cannol be used for phenomena which change <br />over relatively small i'lcremenls of space and time. In <br />addition, the time increment can be chosen to coin- <br />cide wilh Ihe period of cycllc changes in certain hydro- <br />logic phenomena so thai net changes in these phenom- <br />ena during a time interval are usually negligible. For <br />example, storage changes within a hydrologic syslem <br />from year to year are often insignificant whereas, the <br />magnilude of Ihese changes from month 10 month <br />are frequently appreciable and need to be considered. <br />As one attempts to achieve fmer resolution in time <br />and space, improved defmition of Ihe hydrologic pro- <br />cesses is required. Short-term transient effects or ap- <br />preciable variations in space cannot be neglected, and <br />Ihe required malhematical model, therefore, becomes <br />more complex with an accompanying increase in re- <br />quired computer capacity and capability. <br /> <br />However, as shown on Figure 3.2, it is often <br />possible to simplify high resolution models by elimin- <br />ating processes which do not appreciably affect the <br />output of interest. For example, in modeling Ihe <br />rural portions of the watershed, bolh a daily time <br />incremenl. (Figure 3.3) and an hourly time increment <br />(Figure 3.4) were used. For Ihe daily time increment <br />model, all of the hydrologic processes are included. <br />On the olher hand, to estimate peak surface runoff <br />rates from cloudburst storms, some processes, such as <br />snowmelt and soil moisture movement, need not be <br />included bul a high degree of resolution in Ihe time <br />dimension is necessary. For this reason, the hourly <br />time increment model (Figure 3.4) represenls fewer <br />processes than the daily model, but at a high degree <br />of time resolution. Thus, the application is a prime <br />consideration in_model formulation. <br /> <br />For Ihe urban hydrology model of the sludy, <br />a 3D-minute time increment and small space units <br />(zones) were adopled. Zones were dermed to enable <br />spatially varying watershed conditions, such as slope <br />and infiltration rate, to be considered by the model <br />and marked offas shown by Figure 2.2 along hydro- <br />logic boundaries matching points of data availability. <br />The probable issues in reaching flood management de- <br />cisions were considered in selecting the time and space <br />increments for the models. <br /> <br />System Processes <br /> <br />The system processes included in the hydrologic <br />models of this study (for bolh urban and rural drain- <br />age areas) are discussed in the following paragraphs. <br /> <br />Precipitation <br /> <br />Waler enters the hydrologic syslem as precipita- <br />tion. Precipitation on a catchment area is estimated <br />by a spatial integralion techriique, such as Ihe isohye- <br />lal melhod or the Thiessen v.eighting procedure, from <br />point data from a gage network. The Thiessen network <br />was applied in this study (Figure 2.7), and Ihe inpul <br />hydrographs for individual storm events were deter- <br />mined by a compuler program. Since rain causes Ihe <br />major flood events in the Salt Lake Valley, the <br />snow accumulation and melt processes are not in- <br />cluded in the model. <br /> <br />Surface Water Inflows <br /> <br />Streamflow is precipitation which streams and <br />rivers collect from a drainage area. If only a portion <br />of the drainage area is included within the boundary <br />of the area being modeled, streamflow inpuls to the <br />modeled area are either measured or estimaled by cor- <br />relation. <br /> <br />Interceplion <br /> <br />Rainfall excess is calculated by subtracting inter- <br />ception on the leaves of trees and other intercepting <br />objects from the measured precipitation. The rate of <br />interception is assumed to reduce exponentially with <br />an increase in interception storage. and can be expressed <br />as follows: <br /> <br />i ; ie -PIS, <br />co <br /> <br />. (3.2) <br /> <br />in which <br />icc capacity rate of inflow into intercep- <br />tion storage <br />; rate of precipilation <br /> <br />P ; cumulative precipitation <br />S, ; volume of interception slorage capacity <br />expressed as an average depth over the <br />catchmenl area <br /> <br />The actual interception rate, iea' is defmed by the fol- <br />lowing expressions: <br /> <br />iea = i, for i ~ ice' <br /> <br />. . (3.3) <br /> <br />and <br /> <br />iea = ice' for i > ice <br /> <br />2S <br />