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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I, <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />discussed in Section 3.3.2, which has provided empirical <br />evidence concerning the shape of the intermediate part of <br />the rainfall frequency curve, a region of particular relevance <br />to the assessment of adequacy of many existing spillways. <br /> <br />The reduclion in relative uncertainty, however, is likely <br />to have its greatest impact on the estimation of Rare to <br />Extreme floods. This is a region where "the computation of <br />hydrologic probabilities is based on arbitrary assumptions <br />about the probabilistic behaviour of hydrologic processes <br />rather than on empirical evidence or theoretical knowledge <br />and understanding of these processes" (Klemes, 1993). <br />Improving the consistency of the manner in which such <br />assumptions are applied in practice will thus minimise the <br />potential for differences in the results obtained by different <br />hydrologists. The main strategy available for reducing the <br />impact of relative uncertainty is to ensure that the <br />practitioners undertaking the work are appropriately <br />qualified and supervised. In addition, prescriptive <br />procedures relating to the estimation of floods beyond the <br />credible limit of extrapolation are justifiable as without <br />empirical evidence or scientific justification there can be <br />little rational basis for departing from a consensus <br />approach. <br /> <br />5,6.2 Evaluation of Uncertainty <br /> <br />There are several techniques to assess model <br />uncertainty. The techniques most commonly used to <br />assess the uncertainty of extreme flood estimates are <br />sensitivity analysis and Monte Carta simulation, though <br />other techniques may also be suitable. The available <br />literature on uncertainty analysis is extensive and highly <br />mathematical. While there are many papers dealing with <br />the theoretical aspects of different techniques and <br />comparative analyses, fewer papers have been written on <br />techniques that are applicable to practical design problems. <br />Thus, while the importance of uncertainty analysis is <br />widely recognised, there are few tools available to the <br />practitioner that can be used routinely for design. The <br />foliowing sections outline the characteristics of a few <br />methods which have the potential to be readily applied to <br />practical problems. <br /> <br />(a) Sensitivity analysis <br /> <br />Sensitivity analysis is a simple technique used to <br />identify the parameters that have the greatest impact on the <br />outcome of interest. It does not quantify uncertainty in an <br />absolute sense, but rather is used to indicate the degree to <br />which uncertainty in certain parameters impacts upon the <br />results. The analysis involves the perturbation of inputs or <br />model parameters from a base value, and then using some <br />criterion (such as flood peak and/or volume) to measure the <br />change in model response. <br />The sensitivity of the resuUs to the most influential <br />parameters should be investigated and quantified in all <br />design situations. If there are significant differences in <br />outcome within the range of parameter uncertainly then the <br />likely range of consequences should be explicitiy <br />considered when developing mitigation strategies. <br />Uncertainties can be simplistically quantified by <br />undertaking a separate assessment for the most sensitive <br />input(s), and weighting \he resuUs based on the asses~ <br />probabilities of their occurrence. For example, Laurenson <br />and Kuczera (1998) recommend that the uncertainty <br />associated with the AEP of the PMP be directly <br />incorporated into a risk analysis by performing an <br />assessment for each of the AEPs in Table 5 and weighting <br />tf\e results using the associated $lJbjeellve probabilities. <br />While accurate estimates of probabilities for different class <br />intervals are usually not available, the adoption of <br /> <br />............" VI - ........".,"'"....,...... .......,l:f......... L..^.........,... I ,........... <br /> <br />subjective probabilities in this manner does provide an <br />objective basis for incorporating judgement into the <br />outcome. <br /> <br />(b) Monte Carlo Methods <br /> <br />Monte Carlo analysis is perhaps the most commonly <br />used method in practice. The most important input <br />parameters are treated as variables having a specified <br />distribution rather than being fixed values. Numerous <br />computer simulations are conducted where each simulation <br />uses a set of input parameters that are selected at random <br />from continuous (or discrete) probability distributions. <br />Different probability distributions may be used. for the <br />various parameters, and the characteristics of the <br />distributions are selected to be representative of the <br />uncertainty of each input (as well as preserving the <br />dependencies between the parameters). In each simulation <br />run of the Monte Carlo analysis the results are stored, and <br />by generating many replicates one obtains samples that <br />describe the probability distribution of the outputs. The <br />characteristics of the resulting sample (e.g. the mean, <br />standard deviation, or percentile statistics) can be used to <br />describe and evaluate the decision i{l1plications of <br />uncertainty in the model inputs. Examples of application of <br />this approach to rainfall-runoff models can be found in <br />Krajeweski et al. (1991), Kuczera and Williams (1992), and <br />Haan et al. (1995). <br /> <br />The uncertainty regarding the selection of the <br />distributions used to characterise the inputs is one of the <br />major difficulties with the method. An assessment of the <br />distributions may be based on judgement and experience, <br />or from the literature. Available evidence (e.g. Haan et aI., <br />1988) suggests that good estimates of the means and <br />variances of the input parameters are of greater importance <br />than the actual form of the distribution adopted. Thus while <br />there may be uncertainty regarding the distributional <br />characteristics of the input variables, it is considered that <br />the method does provide an objective basis for assessing <br />uncertainly. <br /> <br />Latin Hypercube sampling (McKay, 1988) is a stratified <br />sampling approach that is more efficient than traditional <br />Monte Carlo simulation. An example of its application to the <br />HEC-1 flood event model is provided in Melching (1995). <br />Thompson et al. (1997) discuss other sampling strategies <br />that increase the efficiency of the simple Monte Carta <br />method. <br /> <br />(c) Other Techniques <br /> <br />While Monte-Carta techniques are robust, they can be <br />computationally intensive, especially for low probability <br />outcomes. As a result, there has been considerable interest <br />in alternative procedures which could offer computational <br />savings. Alternative techniques that have been used with <br />flood event models include point estimate methods (Rogers <br />et aI., 1985; Binley et aI., 1991), and first and second order <br />analysis techniques (Haan et aI., 1995; Melching et aI., <br />1990; Melching, 1992). A useful review of the different <br />methods is provided by Melching (1995). <br /> <br />While these other methods have the potential to be <br />more efficient, they are generally applicable to a more <br />restricted set of conditions. Several studies have been <br />conducted on comparing the efficacy of different techniques <br />(e.g. see Melching, 1995), and it may generally be <br />concluded that at this stage Monte Carlo techniques are <br />perhaps the only approach that can be relied upon to <br />provide estimates of uncertainty in systems that are highly <br />non-liJ\ear or Iligllly variable. <br />