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Technical Description <br /> C = constant of 8.34 <br /> A = lbs of BODS entering daily <br /> DENITRIFICATION 0,ALLOCATION <br /> The conversion of ammonium to nitrate demands a support process to sustain the reaction. With <br /> oxygen being the only common acceptor, 02 demand/delivery is taken into the design considera- <br /> tion of the batch process. <br /> The energy produced by oxidation of NH., and NO, is used by nitrifying organisms primarily to <br /> produce new biomass. These bacterial cells can be represented by the approximate formula <br /> C5H70,N.The biomass synthesis reaction for nitrosomonas and nitrobacter is: <br /> NH4+ HCO3 +4CO, + H2O C5H702N + 502 (3) <br /> This synthesis reaction requires an input of energy to proceed. During nitrification. this energy is <br /> obtained from NH., and NO2 oxidation equations I and 2; therefore, reactions shown in equations <br /> I and 3 usually occur simultaneously. The energy yield from the oxidation of one mole of NH, or <br /> NO, is much less than the energy required to produce one mole of bacterial cells as (C5H702N). <br /> Equations 1, 2; and 3 then must be proportioned so that after energy transfer efficiencies are <br /> taken into account, the energy used equals energy produced. The biological nitrification is then <br /> expressed as: <br /> NH,+ 1.83 02+ 1.98 HCO; 0.021 CIH702N+ 0.98 NO, + 1.041 R20+ 1.88 H,CO, (4) <br /> which can be used to estimate the three important parameters associated with the nitrification <br /> process: oxygen requirements, alkalinity consumption, and nitrifier biomass production. <br /> Nitrogen removal is accomplished in the Nitro-Raptor system without additional equipment or <br /> chemicals. Nitrogen enters the system in the raw wastewater in the form of organic nitrogen and <br /> ammonia (NH4). It is removed from the system in the form of nitrogen gas (N2). The actual proc- <br /> ess by which ammonia nitrogen is converted to nitrogen gas is a three-step process. First is nitri- <br /> fication, the conversion of ammonia nitrogen to nitrite (NO2). Second is the conversion of nitrite. <br /> to nitrate (NO3). Third is denitrification, the conversion of nitrate nitrogen-to-nitrogen gas (N2). <br /> All of these steps are accomplished by microbiological action. However, the different steps re- <br /> quire different microorganisms and different reactor conditions. <br /> Steps 1 and 2 both require greater than 0.5 g/m3 dissolved oxygen, take place in the aeration <br /> chamber, and occur as an ongoing process. Step 3 occurs in the absence of dissolved oxygen, and <br /> since the aeration chamber receives forced air 24 hours a day, takes place in the clarifier. <br /> Nitrogen removal in the 'vitro-Raptor process is considerably greater than that of flowthrough <br /> and single-tank, sequencing-batch reactor systems. The Nitro-Raptor system achieves an average <br /> of 96.4%total nitrogen removal. <br /> AERATION DETENTION <br /> The Nitro-Raptor system's superior low-sludge-producing performance is obtained, in pan, by <br /> combining the complete-mix hydraulic design with the detention times of the extended-aeration <br /> designs. This combination effectively produces a low F:M ratio and a subsequent high MCRT. <br /> This promotes the development of specific, high-process microorganisms. <br /> - ]1 - <br /> 7-H Technical Services Group,Inc. <br /> i <br />