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the sludge spends in the treatment system. This cycle is referred to <br /> as mean-cell-residence-time(MCRT), and is a function of the amount NOTES <br /> of food provided to bacteria in the aeration reactor tank (the food- <br /> to-microorganism ratio, F:M). <br /> There are three basic classifications of the activated sludge process <br /> which are defined by the process loading range to the microorgan- <br /> isms: high, conventional, and low.The following shows typical ranges <br /> of the MCRT and F:M for each loading range: <br /> MCRT, F/M <br /> Process day Ib BODS/day/lb MLVSS <br /> High Rate 3-5 0.4-1.5 <br /> Conventional Rate 5-15 0.2-0.4 <br /> Low Rate 15-30 0S-0.2 <br /> Note: lbs/day x 0.01157 = g/kg <br /> In the complete-mix, activated-sludge process, the characteristics of <br /> the mixed liquor are similar throughout the aeration tank. That is, <br /> the influent waste is rapidly distributed and operating characteristics <br /> measured in terms of solids, oxygen uptake rate (OUR),MLSS, and <br /> soluble BOD concentration are nearly identical throughout the tank, <br /> with a very low level of food available to a large mass of microorgan- <br /> isms at any given time. <br /> This is the principal reason for the system's ability to handle surges <br /> in the organic loading without producing a change in effluent quality. <br /> Critical design factors are the tank's length-to-width ratio, amount of <br /> air introduced, and wastewater velocity throughout the tank. <br /> The system is operated at recommended design standards of MISS <br /> of about 3,000 to 6,000 mg/l. The quantity of sludge returning from <br /> the clarifier is 25 to 100 percent of design flow. This percentage is <br /> required in order to maintain the aeration solids. <br /> To ensure that a dissolved oxygen (DO) of 0.05 ppm minimum exists <br /> at all points, a minimum oxygen input of 2.0 mg/1 is maintained at <br /> the effluent end of the aeration chamber. Therefore, air is supplied <br /> at a rate of 0.8 to 115 cubic feet/gallon of wastewater with an addi- <br /> tional mixing factor of 1.5 to 2.0 cubic feet/gallon. <br /> r <br /> For siring the air delivery system, the cubic-feet-of-air requirement <br /> is expressed as cubic feet of air required per pound of BOD re- <br /> moved from the aeration reactor.The minimum air/organic loading <br /> recommended by most state agencies is 1,000 cubic feet/pound of <br /> BOD. <br /> Well-designed systems will sometimes expand this to 1,500 cubic <br /> feet/pound of BOD removed, allowing a residual airbase for com- <br /> pensation of higher organic loadings than anticipated and to support <br /> further processing of ammonium nitrogen (NH,). <br /> 12 <br />