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Technical Description <br /> PHYSICAL PRETREATMENT, SEPARATION AND NITRIFICATION INITIATION (may not be <br /> required) <br /> (NOTE. The following may not be required for nitrification where detention periods of 14 hours <br /> or more are anticipated. With reduced solids concentration, the normal calculated aeration de- <br /> mand for the batch process is sufficient for nitrification supplementation. Should external nitrifi- <br /> cation be deemed necessary, the following procedure is used.) <br /> Prior to entering the treatment plant, raw sewage may be collected in a baffled buffer tank. The <br /> buffer tank is anaerobic and sized for a detention period that will allow solid/liquid separation, <br /> retention of.solids and floatable materials, and promotion of facultative anaerobes by degenera- <br /> tion of natural dissolved oxygen levels. <br /> The tank inlet and outlet are level and partially baffled, causing retention of a portion of the sol- <br /> ids. This retention allows the microorganisms to develop large colonies. This simple collection of <br /> solids reduces overall loading to the aeration reactor and hastens the process of converting or- <br /> ganic nitrogen to ammonium ions. It also supplies soluble BOD as effluent product/influent <br /> wastewater to the aeration tank. <br /> The lowering of BOD levels in -the aeration reactor forces depletion of available BOD food <br /> source in the extended aeration phase. This enhances the natural dominance of nitrosomonas and <br /> nitrobacter organisms. These organisms predominate and utilize the dead cells as a carbon <br /> source, converting ammonium nitrogen (NH4),as a nutrient base, to nitrite (NO2) through oxida- <br /> tion. <br /> A portion of the resulting nitrate (NO3) rises to the surface of the reactor and is reduced prior to <br /> reaching the atmosphere. <br /> The nitrosomonas are responsible for conversion of ammonium nitrogen to nitrite, which spon- <br /> sors the rapid nitrobactcr conversion to nitrate: <br /> NH'4+ 3/2 02 --- 2W+H2O+-NO2 (1) <br /> and a portion of the NO2 is then oxidized to NO3: <br /> NO2 + 1/2 02 NO2 —* NO-3 (2) <br /> The use of microprocessor and computer technology allows modifications of the timing cycle <br /> that controls the amount of time the sludge spends in the treatment system. It is this cycle that is <br /> referred to as the Mean-Cell-Residence-Time (MCRT), and is a function of the amount of food <br /> provided to bacteria in the aeration reactor tank(the food-to-microorganism(F:M ratio)). <br /> -9- <br /> TH Technical Services Group,Inc. <br />