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1%W .we <br /> This method of mixing air and waste, under pressure, produces vig- <br /> orous agitation and excellent oxygen transfer as the bubbles rise to NOTES <br /> the surface through the mixed liquor.It is far superior to the conven- <br /> tional surface-effect aerators,as it ensures near-uniform aerobic con- <br /> ditions throughout the entire chamber. <br /> Aeration is automatically selected as continuous or intermittent, de- <br /> pending on the level and age of liquor in the tank. <br /> The amount of air added for complete digestion of sewage need not <br /> be high because of the elevated temperature of the mixed liquor, <br /> which may be as much as 5 degrees higher than the incoming waste. <br /> This higher temperature, plus the floc particle breakup due to the <br /> vigorous air circulation, renders the organic material more readily <br /> digestible by the ever-increasing number of organisms residing in the <br /> tank. <br /> On reaching a predetermined level in the aeration tank, a float switch <br /> initiates the microprocessor, starting the batch cycle which transfers <br /> the mixed liquor to the primary clarifier. During the later stage of <br /> this transfer, any floatables in the clarifier are returned to the aera- <br /> tion chamber via a dual-tube weir system which skims the top sur- <br /> face. The remaining liquid is allowed to settle for approximately 70 <br /> minutes under static, or quiet, conditions. This settling separates the <br /> liquid into two levels;the clear top level is called supernatant and the <br /> lower level is termed activated sludge. <br /> After separation, the supernatant is transferred through an auto- <br /> demand chlorinating line into the chlorine contact tank, which also <br /> acts as a secondary clarifier. Any remaining floatables, along with <br /> the settled sludge remaining in the primary clarifier, are returned via <br /> pump to the aeration tank for additional processing and recycling. It <br /> is this constant recycling that provides a mean-cell-residence-time <br /> (MCRT) of approximately 14 hours and causes the near-total de- <br /> struction of sludge. <br /> In the chlorine contact chamber,sometimes called a secondary clari- <br /> fier, the supernatant, now chlorinated, is held for another 70-minute <br /> period of quiescent settling. This second settling period allows any <br /> remaining solids to settle.After this 70-minute period,approximately <br /> 95%of the treated waste is pumped through optional tertiary filters, <br /> or it may be discharged as secondary effluent. The remaining 5%, <br /> which is inert or activated sludge, is returned to the aeration cham- <br /> ber for reprocessing. <br /> As incoming sewage flow slows, such as during midday, late-night <br /> and early morning hours, the level in the aeration chamber is low- <br /> ered by continued batching. At a predetermined lower level, a float <br /> switch is triggered, reducing the aeration to an intermittent schedule <br /> more suitable to existing sludge conditions and the reduced quantity <br /> of incoming waste. <br /> The system flow is automatically programmed and requires no man- <br /> ual assistance,although an operator override control is provided. <br /> 3 <br />