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Fificatioil <br /> CONCLUSIONS AND RECOMMENDATIONS <br /> il physical characteristics under the proposed disposal area reveal a silty-ciay/clax�silt tyle__th very slow petmeabilitZ,_6ased onthe percolation testresults. This is due to thection of the embankment, which consists of finer grained spoils from the Brown Sandon and compacted during emplacement. However, the AG-CON_Equipment.husiness is gn_), hat can be considered a favorable structure. By distributing the effluent throughtor Chamber over the entire filter bed arca, the favorable characteristics of these clay soils.e structure itself. can be taken advantage of, such as: 1.Z Ammonium absor)tion, 2.) <br /> bic microsites within the clay latticereventing nitrification and promoting denitnftcation..ury nitrification that has occurred. 3.) Unsaturated flow conditions. 4 ) Substantt,tll) incrs:asmg <br /> S the distance between the soilleftluent interface and the depth to groundwater, and �Urcaler r <br /> zlikelihood o(puthgjen destruction to prevent cut3tmnmatiott of the Iatic�Consideration may he <br /> given to constructing the 10FI� replacement area sinwltaneous with the primary field in the event <br /> the disposal areas need to rest and rehabilitate at some point in the future. <br /> calculationsindicateindicate an effluent concentration that is below the MCL for <br /> The nitrate loading ca <br /> drinking water. Considering the lake will be the"sink" for the effluent that does reach the <br /> groundwater, the dilution effect will be substantial. In fact, the dilution should be so large as to he <br /> immeasurable. <br /> There. should be no. or vct'v little. weight, to the west of the filter bed, between the west side of the <br /> bed and the beginning or heel of the slope. Loading in this area may cause slope failure if saturated <br /> soil conditions develop. The ad .Tegete hasc_(.AB) currently on the surface of the embaL*ment must <br /> be removed and the underlying infiltration sui face must be scored with the backhoe teeth before <br /> irihhralor Chamber installation. <br /> It is important to recognize that all septic systems and disposal areas have a lifespan. This lifespan <br /> is unpredictable due to the numerous operational and environmental factors involved. Operational <br /> factors include checking the toilet regularly to ensure there is no leakage. Environmental factors <br /> include biomat buildup that will occur at the soil/effluent interface within the chambers and a <br /> naturally occurring process illustrated on the attached schematic in Appendix D. (Adapted from <br /> Metcalf and Eddy: Wastewater Engineering Treatment Disposal and Reusel. Biomat buildup is <br /> typically managed by allowing the filter bed to rest and rehabilitate naturally. <br /> If there are to be any food preparation inside the office, disposals or food waste grinders must not he <br /> installed. It is imperative that no chemicals, solvents or petroleum products, other than low <br /> concentrations of household cleaners be introduced into the septic system. <br /> The grass ground cover over the disposal areas will need irrigation during the spring and summer <br /> months. However, care must be given to the amount of water applied so as to not inundate the <br /> system. It is recommended to irrigate with "impact-type" sprinkler heads during the night. 11' <br /> irrigation is needed during the hottest summer days,the irrigation system should activate several <br /> times for short durations. Mitt oxen ler till er should not be cyr/died to the filter bed Yrncr eruu+ul <br /> corer area. <br /> Page -9- <br /> Chesney Coersalti'19 <br />