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I n d u s t r i a l  A p p l i c a t i o n s  a n d Ca s e  S t u d i e s   263


                     was chosen as a component to proxy for all contaminants for two
                     reasons: first, COD measures the most significant contaminant
                     load in the majority of water streams; and second, COD exhibits
                     significantly high values.
                        The overall mass balance is closed by using the assumption
                     that evaporation losses from the steam system amount to 1 t/h
                     (otherwise, there is an “inconsistency” of 1 t/h of water that must
                     be accounted for). The extracted data on contaminant concentrations
                     and water flow rate made it possible to establish the amount of
                     water gained or lost by each operation in the process. The total
                     mass load picked up by the freshwater through each operation was
                     then calculated. The eleven water-using operations—together with
                     the water flow rates entering and leaving each operation—can be
                     represented in the form of a simplified water network, as shown in
                     Figure 11.6.
                        The freshwater COD concentration level for the plant is 30 ppm.
                     There was an existing water reuse between processes currently in
                     the plant, and these reuse streams were left unchanged. The
                     simplified water network presented in Figure 11.6 shows the
                     freshwater-using operations with existing water reuse streams “built
                     in” to each identified operation. The current total freshwater consumed
                     and wastewater generated by this citrus plant were, respectively,
                     240.3 and 246.1 t/h.
                        The existing water network provided a base starting point for the
                     Water Pinch Analysis. The freshwater target was evaluated by using
                     the Composite Curves. The maximum concentration levels were
                     based on the constraints and limitations dictated by process
                     conditions and requirements. This data were represented in the
                     WATER software tool (2005) with identified constraints. The process
                     restrictions on water type permissible for each operation indicated
                     that operations 2, 4, 5, and 10 can use only freshwater as input. Hence,
                     the minimum freshwater required by plant operations was
                     164.4 t/h.
                        Operation 1 is a batch process for which the analysis assumed
                     freshwater must always be available. This increases the plant’s total
                     minimum freshwater requirement [t/h] to 164.9 = 164.4 + 0.5 for
                     operation 1. The current total freshwater feed to the plant is 240.3 t/h.
                     These figures can be used to calculate the maximum theoretical
                     freshwater reduction (MTFWR) that is achievable:

                                 MTFWR    240.3 164.9 ˜  100    31.4 percent  (11.2)
                                             240.3

                        The Water Pinch Analysis was then carried out for the existing
                     water network with maximum concentration levels. The overall
                     freshwater target was calculated using the maximum reuse analysis.
                     Figure 11.7 shows the modified water network represented as a
                     conventional diagram, and the Limiting Composite Curve is plotted
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