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V. CONCLUSIONS AND RECOMMENDATIONS <br /> The soil physical characteristics under the subject property reveal that most of the area for APN <br /> 179-160-20 has been subject to apparent compaction sufficient enough to negatively influence <br /> per <br /> as measured by percolation. Compaction has occurred from the parking of heavy <br /> machinery on this Parcel. To overcome this problem, an engineered system may be designed, or <br /> seepage pits may be installed in accordance with EHD requirements. <br /> Surface soils in potential disposal areas reveal a silty clay/clayey silt type soil with increasing <br /> permeability with increasing depth,based on the percolation test results. If a new septic system is <br /> proposed in the future, Infiltrator Chambers should be considered for leachlines. By distributing <br /> the effluent through these Chambers over a shallow distribution area, the favorable characteristics <br /> of the clay surface soils can be taken advantage of, such as: 1.) Ammonium absorption, <br /> 2.) Anaerobic microsites within the clay lattices preventing nitrification and promoting <br /> denitrification for nitrification that has occurred, 3.)Unsaturated flow conditions, 4.)Increasing <br /> the distance between the soil/effluent interface and the depth to groundwater, and 5.) Greater <br /> likelihood of pathogen destruction to prevent contamination of the underlying groundwater. <br /> As referenced in the Introduction, it will be the requirement of the EHD that if commercial <br /> development of Parcels APN 179-160-18 and 19 should ever occur,these two Parcels must <br /> connect to public water and sewer. <br /> It is generally recognized from soil physics,that water percolating from a fine-grained soil into a <br /> coarser-grained soil will be impeded until near saturation is reached in the fine/coarse-grained soil <br /> interface. These characteristics were observed in the subsurface soils and are beneficial for the <br /> prevention of nitrification and the promotion of denitrification. <br /> The nitrate loading calculations suggest a current effluent concentration that is below the MCL for <br /> drinking water and is roughly equivalent with the current nitrate concentration in the on-site <br /> domestic well water. <br /> It is important to recognize that all septic systems and disposal areas have a lifespan. This <br /> lifespan is unpredictable due to the numerous operational and environmental factors involved. <br /> Operational factors include checking toilets regularly to ensure there is no leakage. <br /> Environmental factors include biomat buildup that will occur at the soil/effluent interface which is <br /> a naturally occurring process. Biomat buildup is typically managed by allowing the disposal area <br /> to rest and rehabilitate naturally. <br /> L�� <br /> Chesney Consulting <br />