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Bert E. Van Voris • - 11 - 17 September 2004 <br /> Supervising Engineer <br /> Contrary to the RWD's contention that a 100-year return period"is not typically used as a <br /> basis for design,s'1 the RWD must demonstrate that Musco has sufficient storage and <br /> disposal capacity to ensure all its processing wastewater is contained onsite(or permitted <br /> use areas) during the wettest years (interpreted as a rainfall year with 100-year recurrence <br /> frequency). Industrial discharges may reduce production during very wet years as a trade- <br /> off to storage structures and still ensure compliance with permit prohibitions against <br /> offsite discharge. <br /> To ensure that discharge can be conducted without threatening offsite discharge, waste <br /> discharge requirements typically set the maximum effluent flow limitation(daily <br /> maximum, monthly daily average, or both) based on the design flow values employed in <br /> the 100-year water balance. Maximum average daily flows are typically employed in <br /> water balances for municipalities and industries with constant production levels (e.g., milk <br /> or cheese processors). Some municipalities specify only dry weather flows and provide <br /> estimates of anticipated inflow and infiltration flows during wet weather months. Water <br /> balances for seasonal industries often employ maximum average daily flows for each <br /> specific processing `season.' <br /> The project's Water Balances should provide sufficient technical documentation for all <br /> assumptions and calculated values, and contain intermediate columns documenting all input <br /> values. For example, references used for crop coefficients should be cited and columns <br /> representing evaporation losses from and rainfall contributions to the reservoir should be <br /> included. Total annual leaching values should also be expressed as million gallons. Leaching <br /> losses attributable to the assumed irrigation efficiency of 80 percent should also be included. <br /> Proiected Process Flows. In Section 10.1.1,the RWD proposes maximum totalized flow limits of <br /> 45 million gallons (MG) monthly and 292 MG annually, and requests that limitations be expressed in <br /> terms of maximum monthly and annual limits, not daily maximum volumes. Elsewhere, the RWD <br /> indicates, but does not explain,that process wastewater flows may potentially be less than 182 MG <br /> annually.12 <br /> Comment: Table 2 should separate process wastewater flows from storm water flows to <br /> identify the maximum anticipated discharge flow resulting solely from olive processing; <br /> storm water flows should be handled separately in the water balance, and be based on <br /> assumptions of storm water flows based on rainfall intensity and catchment area. Daily <br /> maximum discharge flow limitations will be necessary to ensure wastewater generation <br /> flows do not exceed the hydraulic and treatment capacities of wastewater treatment unit <br /> processes and operations. The RWD should identify what these capacities will be. <br /> The RWD's Table 2, Estimated Process Wastewater Flow, presents maximum, average, and minimum <br /> daily flows (in 1,000 gals/day) for each month from January 2003 through April 2004, and includes storm <br /> water "falling in the process areas." The RWD's 100-Year Water Balance (Table 15) uses a maximum <br /> annual discharge of 182 MG. Values for monthly wastewater flows in Table 15 employ variable design <br /> flows ranging from 13 MG (December through January) to 16 MG(August through November). <br /> Comment: Discharge flows in the 100-Year Water Balance should reflect Musco's <br /> proposed maximum monthly and annual discharge flows of 45 and 292 MG, respectively. <br />