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r <br /> In addition to estimating wastewater loading rates, climatic stress must also be considered regarding <br /> the loading of the septic system. Leachfields must transmit two hydraulic loads: the effluent load <br /> and the climatic load during the rainy season. The average yearly rainfall in the Stockton area is <br /> 13.50 inches which is significant enough to influence hydraulic loading. When soils with <br /> hydraulically limiting horizons (such as clays or a high groundwater table) are used for disposal, <br /> hydraulic stress occurs when the total effluent load plus precipitation exceeds the transmission rate <br /> through the clay horizons. During the rainy season, both climatic and effluent loads may have to <br /> be stored above these limiting horizons. If the project leachfield contains inadequate storage <br /> capacity, which is a possibility, the seepage pits will then manage the effluent flow. <br /> To reduce wastewater flows originating from the Kingdom Hall, "ultra low-flow" sinks and 1.5 <br /> gallon flush toilets should be installed in the restrooms and apartment area. Sinks should have <br /> spring-loaded fixtures to prevent accidental overuse and the apartment should have a low-flow <br /> shower head. <br /> It is assumed there are no future expansion plans of the new Kingdom Hall, If the possibility exists <br /> for expansion of the apartment area, or the addition of kitchen facilities, the entire operation and <br /> design of the septic system must be reviewed and may have to be revised. <br /> I <br /> VI. NITRATE LOADING <br /> To calculate the nitrate loading for the proposed project, it is important that accurate wastewater <br /> flow volumes be projected as best they can. The initial flow volume for the Kingdom Hall has been <br /> established at an Average Daily Flow of 1400 gallons. This flow volume is similar to a housing <br /> L subdivision or industrial/commercial facility whereby the maximum flow can be determined and <br /> there is usually not much deviation from this initial flow volume. <br /> 1.2 As sewage enters septic tanks, approximately 25% to 33% is part of protein, with the remaining <br /> portion as urea. In the septic tank and the soil environment, ammonia from urea/protein <br /> decomposition, combine with water to form the ammonium ion - the precursor to nitrate. Aerobic <br /> bacteria oxidize ammonium to nitrate usually within two to five feet of unsaturated (aerobic) soil. <br /> This is called nitrification. Virtually complete nitrification of ammonium nitrogen occurs in the <br /> -� unsaturated zone in well-aerated soils under leachfields. However, as referenced, the indigenous <br /> soils are not well aerated due to their high clay content. This factor may attenuate nitrate formation <br /> and promote denitrification. Denitrification is the only mechanism in the soil which can <br /> significantly reduce nitrate concentrations in percolating effluent. It is the biological and chemical <br /> lj <br /> 6 <br /> Vaf zy Ag P�fsearch <br />