The performance of an activated sludge wastewater treatment process consisting of an aeration tank and a secondary settler has been studied. A tanks-in-series model with back¯ow was used for mathematical modeling of the activated sludge wastewater treatment process. Nonlinear algebraic equations obtained from the material balances of MLSS (mixed liquor suspended solids or activated sludge), BOD (biological oxygen demand) and DO (dissolved oxygen) for the aeration tank and the settler and from the behavior of the settler were solved simultaneously using the modi®ed Newton-Raphson technique. The concentration pro®les of MLSS, BOD and DO in the aeration tank were obtained. The simulation results were examined from the viewpoints of mixing in the aeration tank and¯ow in the secondary settling tank. The relationships between the overall performance of the activated sludge process and the operating and design parameters such as hydraulic residence time, in¯uent BOD, recycle ratio and waste sludge ratio were obtained.List of symbols A m 2 cross-sectional area of the settler b l/h microorganism decay coef®cient bf back¯ow parameter C Ã mg/l saturated oxygen concentration C mg/l dissolved oxygen concentration G L g/m 2 h limiting solids¯ux G S g/m 2 h solids settling¯ux due to gravityh overall volumetric mass transfer coef®cient K o mg/l saturation constant for oxygen or DO K s mg/l saturation constant for activated sludge or MLSS k m 3 /g constant of settling characteristics m number of hypothetical stages in tanks-in-series model Q m 3 /h¯ow rate r 1 mass of DO used/activated sludge produced r 2 mass of DO used/activated sludge decay S mg/l BOD X mg/l MLSS (activated sludge concentration) X L mg/l MLSS corresponding to the limiting solids¯ux Y x/s mg/mg yield of growth rate V m 3 volume of aeration tank V 0 m/h constant of settling characteristics Greeks symbols a sludge recycle ratio s h hydraulic residence time l max l/h maximum speci®c growth rate of activate sludge x sludge wastage ratio Subscripts out ef¯uent in in¯uent r recycle
IntroductionIn order to treat the domestic and industrial wastewater, the activated sludge process has been the most commonly used [1,2]. It is considered to be the most cost-effective way to remove the organic materials from wastewater. Besides that, it is very¯exible and can be adapted to almost any type of biological wastewater treatment problem. The design and operation of the treatment processes, however, have not been elucidated. They are highly empirical and accurate description of the performance of activated sludge wastewater treatment processes is still dif®cult. In most previous studies, an ideal mixing approximation, i.e. the perfect mixing model [3,4] or the plug¯ow model [4,5] has been used to model mixing in aeration tanks. Little work deals with imperfect or actual mixing in aeration tanks [e.g. 6±8]. In most of them, the mixing model used to represent imperfect and actual mixing is an axial dispersion model which contains one parameter, the axial dispersion coef®cient, cha...