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<br />U/"V\rl U <br /> <br />I <br /> <br />model to include the facility for separate representation of <br />the hillslope and stream network phases of the hydrograph <br />formation process (Kemp, 1998). <br /> <br />I <br /> <br />(Ii) Separation of routing elements with different <br />non~Jinearities <br /> <br />Different catchment elements (e.g. overland flow, <br />streamflow, channel flow, concentrated storage elements) <br />may be characterised by different non-linearities in their <br />routing response. A model structure that allows the <br />separate representation of routing elements with different <br />non-linearily characteristics (e.g. Kemp, 1998) offers <br />distinct advantages, as extrapolation of the routing <br />characteristics for individual elements can be achieved in a <br />more controlled fashion than for the lumped response of a <br />combination of different elements. <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />'I <br /> <br />4.3,3 Catchment Representation in Model <br /> <br />This section provides recommendations on how the <br />functionalities of a selected model should be used to <br />ensure adequate representation of the real catchment's <br />runoff response. <br /> <br />I <br /> <br />I <br /> <br />(a) General considerations <br /> <br />Most hydrograph models are highly conceptual in <br />nature; in setting up a model representation of the <br />catchment, the modeller should therefore try to define <br />conceptual model elements that match the routing <br />response of the main components of the real catchment, <br />without necessarily attempting to exactly match physical <br />catchment features (e.g. individual drainage lines, drainage <br />divides). How this can best be achieved will depend on the <br />specific features of the selected model. However, the most <br />important factor determining the quality of the modelling <br />results is the modeller's understanding of the routing <br />functions incorporated in the modelling package and <br />hisiher appreciation of the catchment response under flood <br />conditions. More specific guidance on selected model <br />configuration issues is provided in the next section. <br /> <br />I <br /> <br />I <br /> <br />I <br />I <br /> <br />(b) Specific issues <br /> <br />(i) Degree of catchment homogeneity <br /> <br />The model should be subdivided into as many sub- <br />catchments as required to represent the broad variation in <br />Large to Extreme flood response resulting from differences <br />in topographic, drainage system, land cover and land use <br />attributes (see recommendations on the minimum number <br />of sub-catchments provided in Book V Section 3). In many <br />cases, the variation in parameter sets for the different sub- <br />catchments' can be directly related to differences in <br />measurable catchment characteristics. However, where <br />different parameter sets for the sub-catchments have to be <br />determined by calibration, the specification of variation in <br />parameter values should be restricted to those sub- <br />catchments for which calibration information is available. <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />(iI) Representation of important catchment <br />features <br /> <br />Major catchment features may have a significant <br />influence on <:etohment flood response, and may "xhlbit <br />significantly different routing characteristics compared to <br />the rest of the catchment, particularly when extrapolated to <br />extreme events. All the significant natural storage areas <br />(e.g. swamps, extensive flood plains, off-channel storage <br />areas) and distribotary or effluent channel systems should <br />be identified and adequately represented. Consideration <br />should also be given to the modelling of anthropogenic <br />features, such as the specification of diversion channel <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />UVV" VI - L...;;>ull.auv" v. L.a'l:I""'v L...^""""'''''' .vvu.. <br /> <br />capacities, or road/rair crossings that may act as retarding <br />basins during extreme events. <br /> <br />(iii) Representation of catchment areas close to a <br />reservoir <br /> <br />In the vicinity of a reservoir, the routing response varies <br />from near zero delay for rainfall on the inundated areas, to <br />significant delays for rainfall excess from the less directly <br />connected areas draining to the storage. The modelled <br />hydrographs and the calibrated modei parameters can be <br />quite sensitive to the representation of these areas, <br />particularly when the inundated area constitutes a large <br />part of the total catchment. Considerable care should be <br />exercised in ensuring that the routing characteristics of the <br />inundated parts of the catchment and the areas close t6 it <br />have been realistically represented. <br /> <br />(iv) Modelling of changed catchment conditions <br /> <br />The effects of likely changes to the catchment during <br />the design life of the structure need to be considered. <br />Uribanisation and destruction of vegetation by clearing or <br />fire may reduce the response time of the catchment and <br />increase the peak flow, while soil conservation measures <br />over a large portion of a catchment may have the opposite <br />effect. Generally, a rather aribitrary allowance must be <br />made for these effects. Construction of a reservoir may <br />inundate appreciable lengths of streams in the catchment <br />and can lead to large decreases in travel time and <br />increases in flood peaks, despite the attenuation resulting <br />from the routing effect of the reservoir. This effect is <br />discussed and examples are given by Weeks and Stewart <br />(1982), Brown (1982) and Watson (1982). The last two <br />references give examples where the inflow flood peak is <br />increased by 85% by the construction of a dam. It is <br />therefore important to consider this effect when using a <br />model to derive design floods for a dam if it has been <br />calibrated to pre-dam conditions. <br />In general, allowance for different catchment conditions <br />can be made more easily by runoff routing than by unit <br />hydrograph models. In runoff-routing models the different <br />routing characteristics of existing or future catchment <br />conditions can be incorporated by the judicious selection of <br />parameters and the types of routing elements. With the unit <br />hydrograph approach it is more difficult to relate differences <br />in specific catchment conditions to changes in model <br />parameters, particularly with unit hydrograph models that <br />are lumped rather than distributed in nature. <br /> <br />4.3.4 Determination of Model Parameter Values <br /> <br />(aJ Genera/considerations <br /> <br />Calibration of a flood event model for application to <br />design flood estimation is traditionally restricted to the <br />selection of parameter values to achieve a fit between <br />observed and estimated hydrographs. Attention is focused <br />on the collation of concurrent streamflow and rainfall data <br />corresponding to the largest events on record, where <br />considerable effort is required to ensure that the temporal <br />and spatial distribution of the rainfall data is representative <br />of the actual processes. <br />The ability of a model to reproduce historic events <br />certainly gives some confidence to the validity of <br />subsequent design estimates. However it is possibie . <br />perhaps even probable - that the available historic <br />information is not relevant to the design floods of interest. <br />In a well gauged catchment the AEPs of the calibration <br />floods ara Hkely to range between 1 in 5 tc;> 1 in 20. While it <br />would be expected that floods of this magnitude will <br />activate some floodplain storage, the non-linear nature of <br />catchment flood response is such that the catchment <br />