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' r <br /> i <br /> J <br /> !i <br /> During manually controlled operational checking, the clarifier will not be filled to the <br /> overflow weir unless the aeration chamber has been filled to the standby level switch. <br /> Manually control the mixed liquor transfer (MLT) pump until the desired level is reached in <br /> the clarifier. Continue manual operation to.#start the discharge pump. If the liquor in the <br /> chlorine contact chamber has not remained at least 20 minutes for chlorine contact, the <br /> liquor should not be discharged without regulatory authorization. Next,.the chlorine return <br /> (CLR) pump can be momentarily operated to check its operation in the same manner. <br /> The CLR pump is not required in some inst a Ilations, so check your blueprints to be sure. <br /> C. BIOLOGICAL BUILDUP AND STABILIZATION <br /> FM <br /> As with all other biological sewage treatment systems, this system requires a period of <br /> time to build up the biologically active solids to an ,acceptable level of efficiency. This <br /> buildup can be accomplished within ten days under normal loading conditions. <br /> Before biological buildup occurs, the odorklof the liquor in the aeration chamber will be <br /> similar to dishwater except when the influent is anaerobic or septic tank effluent. As the <br /> buildup progresses, the odor may vary slightly. When biological stabilization occurs, the <br /> liquor has an earthy odor and the color becomes dark brown. If the operator carefully <br /> observes these changes in odors and colors during the buildup period, it will be easy to <br /> recognize a regression to such conditions at any future time. <br /> Septic tank effluent may be very dark brown or blackish in color. Initial odor will be of <br /> ammonia and will dissipate rapidly once Fexposed 'to the oxygen within the aeration <br /> chamber. During this constant aeration, sulfides will be released into the atmosphere. It is <br /> recommended that the building be vented€I If septic tank effluent contains bluing dyes <br /> r typical of those found in RV holding-tank chemicais, the color will reflect colors of the <br /> E� dye. Since these dyes are generally inorgak ic, some color may be apparent in the final <br /> discharge. <br /> E� <br /> During startup period, the operator should make daily tests of percent solids. The settled <br /> sludge should reach a level of 30 to 40%. If settled sludge level does not build up, or if <br /> after a period of satisfactory operation the sludge level falls below 30%, excess aeration <br /> should be suspected. This condition is corrected by decreasing the time the aeration <br /> pumps run during the standby period or by throttling the air valves on the air feed lines. <br /> However, the aeration pumps should never be set to operate for less time than it takes to <br /> maintain a minimum level of dissolved oxygen. Any time less than 3 out of 15 minutes will <br /> not give enough mixing of the activated sludge in the aeration chamber. <br /> If, after operating satisfactorily for a period of time, the liquor in the aeration chamber <br /> changes from dark brown to a gray or black and the solids appear thicker than before, <br /> with about 45% sludge in the settling test, a'kdeteriora#ing condition is present. If the plant <br /> is not under continuous organic loading, overcome `this condition by placing the MLT <br /> switch in manual (M) mode, thus allowing. the MLT, pumps to run continuously. This <br /> procedure may be applicable only at night when flows into the plant are at a minimum. <br /> The foregoing procedure can be continued a long as desired until the liquor in the <br /> aeration has been brought to an acceptable'rcondition; that is, solids to be less than 35 to i <br /> 40%. If this procedure cannot lower the percentage of solids, sludge wasting is indicated. E <br /> r <br /> i <br /> f : <br /> F <br /> 2 <br /> I <br /> I <br /> i <br /> { <br />