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FrDetention Time= 6.6 days. The minimum acceptable detention time is 1.0 day. Therefore, the <br /> posed 1,200 gallon septic tank is sufficient volume. <br /> OPERATIONS AND MAINTENANCE PLAN <br /> 1. Fixtures should be checked in each restroom to insure there is no leakage. This should be done <br /> on a weekly basis. <br /> 2. After two years of operation, the septic tank should be inspected by a qualified professional to <br /> determine if the tank should be pumped. <br /> 3. Only shallow rooted plants/shrubs, or a grass should be planted in the landscape area to prevent <br /> root intrusion into the perforated leachline pipe. Additionally, some plants are sensitive to the <br /> ammonium in septic effluent which may cause the plants to die. <br /> V. CONCLUSIONS <br /> The percolation testing revealed an anomaly for the 36" deep test boring. The entire refill water <br /> volume seeped away every 30 minute interval. In comparison, the 42" deep boring perc test result <br /> of 7.4 min/in was more plausible for this soil type. It is assumed the 36" test boring was drilled <br /> into a soil anomaly or a rodent excavation. <br /> Considering the leachline floor area of 2 ft x 100 ft= 200 ftZ x the application rate of the 42" test <br /> boring of 0.80 gals/ft2/day= 160 gpd. Therefore, the leachline can theoretically manage 160 gpd. <br /> According to Table 1.10.2 in the SJC Onsite Wastewater Treatment Systems Standards, the <br /> minimum soil depth from the bottom of the effluent dispersal system to groundwater must be 8 ft <br /> based on the 42" perc rate test result. The Depth to Groundwater maps indicate this separation <br /> distance is easily achieved since the groundwater is greater than 8 ft below grade. <br /> The nitrate loading calculations show the effluent from the proposed facility will theoretically <br /> possess a nitrate-nitrogen concentration of 1.9 mg/L NO3-N. The Federal nitrate Maximum <br /> Contaminant Level (MCL) is 10 ppm NO3-N. This low nitrate-nitrogen contribution by the <br /> proposed Restroom project can be attributed to the denitrification capacity of the soil and the <br /> comparatively large property area in correlation with wastewater ADF. Only Parcel 13 at 3.9 acres <br /> was used in the calculations and not the entire acreage of the Cemetery at 9.94 acres <br /> Considering that Parcel 13 was intermittently farmed, in addition to the surrounding area which has <br /> been farmed for decades, there is a potential for nitrate contamination to the underlying <br /> groundwater from nitrogen fertilizer applications, residual organic matter decomposition, and <br /> OWTSs. This was evidenced by the onsite well water test results found in Appendix E, which <br /> where slightly over the Maximum Contaminant Level (MCL) at 10.3 ppm NO3-N. DBCP was <br /> non-detect(ND). <br /> Page -6- <br /> Chesney Engineering, Inc. <br />