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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 /> <br />I <br />I <br />I <br /> <br />Un.r\r I U <br /> <br />concern. It is common to adopt a single interval to <br />represent flows in excess of the maximum design inflow <br />(usually the PMP Design Flood), where the probability <br />assigned to inflows in this uppermost interval is equal to <br />the exceedance probability of the inflow event at the <br />lower boundary of the interval, and the representative <br />flow magnitude for the interval is notionally increased <br />over the maximum design value. <br /> <br />. Discrete probability distribution of outflows. Depending <br />on the degree of non-linearity of the spillway rating <br />curve, outflows may be discretised into class intervals of <br />equal magnitude, or else intervals can be selected to <br />provide more accuracy in the region of interest (e.g. for <br />flows just above and below the spillway capacity). <br /> <br />. Probabifity distribution of initial slorage volume. The <br />analysis of a time series of storage level or storage <br />volume is used to define the probability distribution of <br />initial storage volume. The time series of reservoir <br />storage volume could be derived directly from the <br />historical record, but in most cases a synthetic time <br />series of storage volume, derived from simulation <br />ibeilaviour analysis) studies, would be more <br />appropriate. In the latter approach the current operating <br />rules can be applied to the historic hydroclimatic <br />sequence, thus providing a long stationary series <br />relevant to the system under consideration. The usual <br />time interval for behaviour analyses is one month, which <br />allows the within-season variation of storage volume to <br />be taken into account in the frequency analysis. If the <br />time series of reservoir storage volume is derived <br />directly from the historicai record, or else if the synthetic <br />results are derived using a daily time-step model, then <br />the correlation between inflows and storage volume can <br />be implicitly accounted for by using the storage level <br />prior to the commencement of any flood which occurred <br />during the month. This is of course not possible if the <br />results are obtained from a monthly simulation model, <br />but in general a synthetic series is to be preferred as it <br />is assumed that greater benefits are to be had from <br />consideration of a long time series than from <br />incorporation of the dependence between inflows and <br />storage contents. <br /> <br />(c) Deterministic relationship between inflow, <br />storage volume and outflow <br /> <br />The conditional probability of a specified outflow event <br />occurring, given that the conditioning event is in a specific <br />class interval, can be determined using a deterministic <br />relationship between inflows, outflows, and storage volume <br />(the 1-8-Q relationship). The I-S-Q relationship has to be <br />determined for a range of peak inflows (corresponding to a <br />range of design rainfalls for selected exceedance <br />probabilities) and for a set of initial storage values. The <br />process of computing the conditional probability of a <br />specified outflow event is illustrated in Figure 9 for the case <br />where the reservoir inflow was chosen as the conditioning <br />event and the initial storage volume as the secondary <br />variable. From this figure it is seen that the conditional <br />probability of a specified outflow event is evaluated as the <br />width of the storage volume probability interval (P[Q;II;]) that <br />translates an inflow in the interval I; into an outflow in the <br />interval A.. <br />As different design rainfall durations result in different 1- <br />S-Q relationships, the computed value of the storage <br />volume probability interval will also depend on the rainfall <br />duration used. The critical rainfall duration to be used in the <br />analysis. is the one that translates into the highest outflow; <br />this also produces the largest estimate of conditional <br />outflow probability. Unfortunately the critical rainfall duration <br />varies with reservoir drawdown, and in some cases it is <br /> <br />CUUK VI - t:.5UIIli:lLtUlI VI L.dlyt::: lU CAlIt::HIl::: rluuu:::, <br /> <br />necessary to compute separate I-S-Q relationships for <br />different durations, and to derive an outflow frequency <br />curve as the envelope of frequency curves derived for <br />different durations. <br /> <br />Another complication is that the above formulation <br />assumes that the two distributions of storage volume and <br />inflows are independent. This may not be the case, but if <br />such correlation is found to be significant then the <br />calculations must be based on the appropriate conditional <br />selection of input variables. <br /> <br />The evaluation of the 1-8-Q relationship is the most time <br />consuming element of the process. Many tens of individual <br />runs are required to define the I-S-Q relationship in <br />sufficient detail, though it is possible to automate the <br />processing of different initial starting levels. <br /> <br />The computation of the conditional probabilities is <br />readily undertaken using spreadsheet software and is not <br />resource intensive; it can also be undertaken manually. <br /> <br />(d) Computation of outflow probabilities <br /> <br />The derivation of the outflow frequency curve by <br />Laurenson's (1974) joint probability approach involves the <br />calculation of a transition probability matrix. Each element <br />in this matrix represents the conditional probability of an <br />inflow within the given inflow interval resulting in an outflow <br />in a specified interval. The total probability of an outflow in <br />that interval can then be obtained as the sum of the <br />probabilities over all the inflow intervals, i.e. all the inflow <br />and initial storage combinations that produce an outflow in <br />the specified range. Outflow AEPs are then computed as <br />the cumulative probability over all outflow ranges exceeding <br />the flood magnitude of interest. <br />An example of the application of this approach is given <br />in Section 6.4. <br /> <br />5,3 Concurrent Tributary Flows <br /> <br />5,3.1 Overview <br /> <br />In some design situations it is desirable to determine <br />the flow in an adjacent catchment that is likely to coincide <br />with design floods in the stream of interest. The most <br />common requirement for this is the assessment of the <br />incremental impact of reservoir failure, where it is desirable <br />to identify separately the inundation due to the direct <br />consequences of dam failure and the floods generated from <br />adjacent catchments. <br /> <br />There are a number of methods available for the <br />assessment of concurrent flov c' (see, for example, Green, <br />1996). In the context of risk analysis it is important to focus <br />on those methods that yield AEP-neutral estimates. In <br />essence, the issue of concurrent flooding is another joint- <br />probability problem, and the method of Laurenson (1974) <br />described in Section 5.2 can be applied directly to the joint <br />occurrence of floods in tributaries and adjacent <br />catchments. With the analysis of concurrent flows, the <br />deterministic I-S-Q relationship referred to in Section 5.2 is <br />replaced by the relationship between total flows <br />downstream of the confluence and the joint occurrence of <br />upstream flows of differing magnitudes, and the marginal <br />distnbution of storage volume is replaced by the probability <br />distribution of flows in the adjacent tributary. Careful <br />consideration needs to be given to the specification of the <br />marginal distribution of tributary inflows as the two flow <br />distributions will be correlated. Also, peak discharges are <br />unlikely Illl coincide. <br /> <br />While application of Laurenson's (1974) method should <br />satisfy the AEP-neutral requirement, it does involve <br />considerable resources. In some design situations the <br />