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Mr. Mike Owens • - 2 - • 15 May 2001 ' <br /> Finding#25 has been corrected to indicate drainage into ASB No.2. <br /> Comments included in Mr. Hayes' e-mail of 14 May 2001 <br /> 3. Your comment no. 2 in your letter of April 23rd regarding discharges fro [sic] sludge dewatering <br /> states "Prior to discharge to ASB No. 2, the leachate will be sampled and analyzed to ensure <br /> that it meets the effluent limits in the WDRs"; Finding No. 25 states, in part, "Sampling of the <br /> sludge wastewater will be conducted to assure that the influent limitations for Pond I are not <br /> exceeded. " Previous correspondence has addressed the fact that the finding should be <br /> referenced to ASB #2 instead of Overflow Pond #1. Beyond that, however, neither the existing <br /> or the proposed WDRs contain influent concentration limits for discharges or influent to ASB #2. <br /> The only effluent concentration limit contained in the WDRs is applicable to the effluent from <br /> ASB #2. The WDRs require that the concentration of TDS in ASB #2 shall not exceed 1,100 <br /> mg/L on an average daily basis and shall not exceed a maximum of 2,110 mg/L in anyone day. <br /> The WDRs also state that dissolved oxygen in the upper 1.0 foot of ASB No.I and No.2 shall be <br /> maintained at a minimum of 1.0 mg/L. <br /> According to Mike Owens, current data indicates that the concentration levels of TDS in both <br /> ASBs has been averaging between 500 and 600 mg/L. The amount of wastewater generated by <br /> sludge dewatering, based on conservative,preliminary calculations is anticipated to be very <br /> small(50,000 gallons per day) compared to the capacity of ASB #2, which is approximately <br /> 3,000,000 gallons and the average daily discharge of the wastewater treatment system of <br /> 2,000,000 gallons per day. Based on simple mass balance calculations and the extensive amount <br /> of waste characterization done to date, it is very unlikely that wastewater generated by sludge <br /> dewatering would have a significant impact on effluent water quality from ASB #2. <br /> Therefore we suggest that Finding No. 25 be revised to eliminate the last sentence <br /> Finding No. 25 has been revised, first to indicate that sludge decant wastewater will be routed to <br /> a drainage that flows to ASB No.2. The last sentence of the finding has also been revised to <br /> read, " Sampling of the sludge wastewater will be conducted to monitor the influent to ASB No. <br /> 2 and to assure that the effluent limitations from ASB No. 2 to irrigation and percolation fields <br /> are not exceeded. <br /> While the WDRs did not set limits on the influent to ASB No. 2, sampling the decant from the sludge is <br /> important because discharge to ASB No.2 is considered a discharge to land. Failure to conduct the <br /> described monitoring would be a violation of the revised WDRs. <br /> Additionally, Mr. Hayes' e-mail of 14 May 2001 includes two comments specific to the 23 April 2001 <br /> letter from Regional Board staff. First, Mr. Hayes indicates that Fox River"seeks reasonable assurance <br /> that resources and funds applied to the closure will not be at risk if the closure of the impoundment is <br /> conducted in accordance with the closure plan that has been submitted." The Regional Board stated in <br /> the 23 April 2001 letter that based on the analytical data submitted we have agreed with Fox River's <br /> conclusion that the sludge material remaining in the impoundment is inert. Additionally, we have <br /> conditionally concurred with the Closure Plan submitted in February 2001. Beyond the statements <br /> already given in the 23 April 2001 letter, the Regional Board can provide no other assurances regarding <br /> the closure. The Discharger (Fox River) is responsible for accurately and thoroughly characterizing the <br />