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Total Nitrogenis-the summation of ammonia-nitrogen (NH,)and organic nitrogen (proteins;amino acids- <br /> enzymes). Since the septic tank is predominately anaerobic,_nitrogen cannot�exist in its-oxidized state as <br /> nitrate for any length of time in-the septic tank effluent, and if it does,-it is quickly reduced to NO or NO2. If <br /> nitrate existed in septic tank effluent,this would also be added,to ammonium and organic nitrogen to arrive <br /> at Total:Nitrogen: Not all of the Total Nitrogen analytically determined will be ultimately converted into <br /> f nitrate. The percentage is indeterminable due to numerous factors. <br /> Additional wastewater constituents may consist of coffee;juices or other similar type liquids to the system. <br /> It is imperative:that no industrial or commercial chemicals, solvents, excessive cleaners,etc. are introduced <br /> into the.septic system, as well as..other items such as sanitary napkins, any paperproducts other than toilet <br /> paper, cloth, plastic,cigarettes; etc. It is also imperative that no garbage disposals are installed. This will <br /> /prevent concentrated organic loading and prolong the lifespan of the wastewater disposal system. <br /> NLS§3.3. To quantify the anticipated nitrogen concentration for use in thenitrate.loading calculations, <br /> influent samples were obtained from three sequential on-site septic tanks. The first tank sampled was the <br /> lift station tank receiving influent from the Dry GoodsBuilding. Influent from this tank is pumped to a two <br /> compartment septic-tank on top of the mound system.-The second compartment of this septic tank was then <br /> sampled. The-third_tank sampledwas the dosing tank immediately after the-septic tank and before the i <br /> effluent gravity flows into the mound soil. <br /> The following Table summarizes.the analytical test results of influent.from the referenced three tanks. The <br /> scientific literature typically-assigns 70-90%of the Total Nitrogen.in septic tank effluent to be in the form <br /> of ammonium, while 10 to 30% is in the organic form. The percentages next to the Ammon ia=Nitrogen and <br /> Organic Nitrogen.concentrations indicate the percent these constituents comprise Total Nitrogen. In <br /> addition, concentrations of weak;medium and strong strength wastewaters have also.been presented for <br /> comparison purposes from Wastewater Engineering, 3'd Ed., in the three columns on.the right. <br /> TABLE 7 <br /> TANK FACATFON < �^ t a X <br /> 6Dry Goods Septic-Tank DOM ng - ` ewater Engineering <br /> Wast <br /> x Metcalf&Eddy 3'"Ed <br /> Bnild>ng Lift. j Sec©nd Tank <br /> ANALYTE F !' ationi <br /> (ConcentrsrimglL <br /> sStationTank ' _ .Co>Irepartment� I <br /> �- =Weak ;,Medi m =e Strong <br /> Ammonia Nitrogen(NHa N) 254 mg/L-(89%) 136 mg/L(80%) 113 mg/L(87%) 12 25 50 <br /> Organic Nitrogen 33 mg/L.(1.1V.) 34 mg/L(20%). 17 mg/L(13%) 8 IS 35 <br /> Total Kieldahl Nitrogen: 287 mg/L 170 mg/L.- _ 130 mg/L 20 40 85 <br /> Total Suspended Solids 180 mg/L ,372 mg/L 68 mg/L 100 220 .350 <br /> (TSS) <br /> Biochemical Oxygen .395 mg/L - -267 mg/L 164 mg/L 110 220 400 <br /> Demand(BODS) - <br /> Total Alkalinity 1080 mg/L 683 mg/L 585 mg/L 50 1.00 200 <br /> As noted, the TKN nitrogen concentrations in the effluent decrease in.each subsequent tank from <br /> 287 mg/L in the Lift Station to 130 mg/L in the Dosing Tank; a 55%decrease in nitrogen <br /> concentration. These analyses confirm the scientific premise that significant nitrogen <br /> decomposition occurs in septic tanks. In addition,the strength of the domestic effluent from the <br /> Winery can be classified as a strong wastewater. This may be due io a lack of a dilution effect that <br /> would normally be observed in household wastewater analysis from.showers, laundry, sinks, etc. <br /> 16 <br /> Chesney Consulting <br />