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r } <br /> r � <br /> National pollution Discharge Ehmination System(NPDES)Permit AppliLatron <br /> . Flag City New West No 1003,6437 West Banner Street,Lodi,California <br /> Page 2 <br /> The bed is fluidized by a constant 50 gpm recirculation of water that dilutes incoming <br /> groundwater from the site After passing through the fluidized bed, the re-circulated water <br /> passes through a re-oxygenation tower The oxygen from air is augmented with an oxygen <br /> booster to increase the capacity of the bioreactor Solids such as calcium carbonate particles <br /> that may be formed as a result of oxygenation are removed by a bead filter Nutrients -- <br /> particularly nitrogen, phosphorus, and potassium —are metered to the bioreactor in a solution <br /> to enhance the bio-activity Two 1,000- pound granular activated carbon (GAC) units will <br /> be placed in series downstream of the bioreactor to polish the treated water and prevent any <br /> breakthrough of contaminants from the bioreactor Sample ports will be located before, <br /> between, and after the absorption vessels to monitor for breakthrough It is estimated that <br /> breakthrough would occur approximately every 14 years <br /> The ERI-4000 bioreactor is designed to treat a contaminant mass loading of up to 250,000 <br /> gpm-ppb (for example, 25 gpm with 10,000 ppb, or 2 5 gpm with 100,000 ppb) As far as <br /> hydraulic Ioadings are concerned, the bioreactor can handle groundwater flow rates of up to <br /> 35 gpm, so it is well suited for the proposed groundwater extraction rate of 25 gpm <br /> Generally, contaminant concentrations decrease substantially in the first several weeks of <br /> groundwater extraction During the initial startup phase, groundwater flow rates to the <br /> bioreactor will likely be less than 25 gpm and will be gradually increased as the contaminant <br /> concentrations decrease as to not overload the bioreactor <br /> • The water will be treated on site and discharged into the onsite storm drain3 ure Fi which <br /> drain (Figure ) <br /> discharges into the White Slough The discharge water will be permitted under California <br /> Regional Water Quality Control Board (CRWQCB) General Order 5-00-119 for discharge to <br /> surface waters All monitoring will be done in accordance with CRWQCB General Order 5- <br /> 00-119 <br /> All construction activities, including utility tie-in, trenching and paving, will be permitted by <br /> appropriate authorities and done in a workmanlike manner See Figure 2 for the designated <br /> disposal area, the onsite storm drain inlet <br /> 3 See Attachment B <br /> 4 See Figures 4 and 5 <br /> 5 The anticipated average flow for the proposed system will be 25 gpm over a one year <br /> interval The maximum flow rate will not exceed 35 gpm The bioreactor can handle flow <br /> rates of up to 35 gpm <br /> 6 Water samples will be collected monthly from the system influent bioreactor discharge <br /> and mid between carbons, effluent, and outfall sampling points for analysis by a California- <br /> certified laboratory A summary of analyses and analytical methods to be used for samples <br /> collected at each sampling point is shown in Table 5 <br />