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Bert E. Van Voris - 8 - 17 September 2004 <br /> Supervising Engineer <br /> treatment is the minimum level of treatment capable of consistently and reliably <br /> producing a wastewater with this requisite quality. <br /> In support of the proposed target BOD range of 40— 50 mg/L,the RWD indicates that <br /> such levels have been determined adequate for irrigation disposal of winery wastewater in <br /> unspecified WDRs adopted by an unspecified regional water quality control board. The <br /> technical and environmental basis for these effluent limits may be considered, but will not <br /> be determinant. Musco should identify which regional board it is referencing, and list at <br /> least one representative WDRs order prescribing effluent BOD limitations reflecting the <br /> proposed target range. An effluent BOD limitation in WDRs may not be sufficient for <br /> irrigation with treated winery wastewater under a recycled water project scenario. <br /> Further, as "BOD levels in [the proposed] range can require management of odor <br /> generation in the water prior to irrigation"s means that the proposed BOD range is too <br /> high for the discharge to be considered a recycled water project. The technology Musco <br /> proposes for the higher salinity wastestreams (aerobic treatment followed by <br /> ultrafiltration) is capable of reducing BOD to less than 10 mg/L. Use of this technology <br /> on all wastestreams would guarantee an effluent quality consistently commensurate with <br /> that of"recycled water." Accordingly, while the proposal to treat higher salinity <br /> wastestreams with this technology and RO reflects the implementation of best practicable <br /> treatment and control (BPTC),the proposal to blend this low-BOD RO permeate in the <br /> reservoir with untreated high-BOD wastewater does not. To fully reflect BPTC, all <br /> wastewater impounded in the reservoir must meet the quality"suitable for onsite storage <br /> and land application," particularly as the issue of the reservoir lining has not been <br /> satisfactorily addressed.6 It appears that dual biological treatment trains will be necessary <br /> (one for high salinity wastestreams prior to RO treatment, the other for lower salinity <br /> wastestreams prior to reservoir discharge) <br /> Target TDS Levels. The RWD/RWR grossly characterizes first encountered groundwater <br /> in these areas based on one sampling event of three wells, only one of which is a dedicated <br /> groundwater monitoring well. The RWD/RWR should provide the design details of this <br /> well, as well as a technical report describing this well and its installation, such as <br /> information specified in STANDARD INFORMATION REQUIREMENTS FOR <br /> GROUNDWATER MONITORING WELL INSTALLATION REPORTS. <br /> Table 5, which characterizes the quality of various wastestreams, should provide <br /> information on mass loadings from each wastestream. <br /> The 26 May 2004 Regional Board letter cautioned Musco to recognize that typical <br /> irrigation practices will concentrate waste constituents more than three times, and <br /> recommended Musco utilize the actual concentration factor for local practices in <br /> identifying the target concentration for IDS and IDS constituents. The letter stated, "the <br /> concentration of any waste constituent in leachate moving below the root zone cannot <br /> exceed the concentration of the constituent determined acceptable in groundwater by the <br /> Regional Board." Because Musco proposes to recycle its treated wastewater for <br /> agricultural irrigation, however, the letter stated that Musco's "effluent quality need not be <br /> better in quality than the water supply used for irrigation in the reuse area." The <br />