Integrated anaerobic and aerobic treatment of sewage

This thesis describes results of investigations dealing with sequential concept of anaerobic-aerobic treatment of municipal wastewater. The main purposes of the study were 1) to develop a proper anaerobic hydrolytic pretreatment unit, consisting of a Hydrolysis Upflow Sludge Bed (HUSB-) reactor and 2) to combine this system with proper aerobic post treatment processes, such as the activated sludge process or a stabilization pond system and with a combined anaerobic-aerobic process consisting of the Expanded Granular Sludge Bed (EGSB-) reactor and an upflow micro- aerophilic post-treatment process for complete sewage treatment. The newly develop HUSB reactor serves for removing SS and accomplishing a certain sludge stabilization and raising the biodegradability of the remaining COD. The HUSB-system is operated at the similar retention time as the primary sedimentation tank, viz. HRT=2.5-3.0 hours. These features of the new system result in 1) release of the troublesome high SSaccumulation problems in the post treatment, such as stabilization ponds and UASB or EGSB systems, 2) a shorter overall retention time and lower energy requirements in the different types of aerobic post treatment processes, 3) an improved applicability for some refractory industrial wastewater treatment and 4) and certain extent of sludge stabilization in the HUSB reactor itself at higher temperature conditions or in a complementary sludge recuperation tank operated in parallel with the HUSB-reactor at low temperature conditions. A new process concept, consisting of a sequential HUSB + the EGSB reactor, combined with sludge recuperation reactor, is presented in this study. The total process provides 71 % COD and 83 % SS removal efficiencies at T>15°C and 51 % COD and 77 % SS-removal at T=12°C conditions. A reasonable extent of sludge stabilization, i.e. over 50% hydrolysis of the removed SS can be obtained in the HUSB reactor at higher ambient temperatures, i.e. exceeding 19°C. The applicable hydraulic retention times are 3 hours and 2 hour for the HUSB reactor and the EGSB reactor respectively and two days for sludge recuperation tank. In the EGSB reactor up to 32 - 60% soluble COD removal efficiency can be achieved and the biogas production amounts to 23-70 NL/m 3 (sewage) at ambient temperature (9-21°C), respectively. By applying a complementary treatment using an micro- aerophilic upflow reactor operated at HRT = 1 hr., an almost complete treatment can be achieved at 13°C conditions. Regarding the shorter hydraulic retention times required in this new concept compared to conventional systems, both for the wastewater treatment and sludge stabilization and its reasonable energy recovery, the new system looks very attractive as an alternative for treatment complex wastewaters like sewage. The conventional aerobic activated sludge process and stabilization ponds both were investigated for post treatment at laboratory scale and pilot scale. The operational problems of these systems, such as occurrence of bulking sludge in the activated sludge process and the rather poor performance of stabilization ponds under cold weather condition were discussed and solutions for these problems are proposed. The experimental results obtained demonstrate the practical feasibility of the hydrolysis - aerobic treatment concept for municipal wastewater at ambient temperature. The final effluent quality is equal or better than that of the conventional activated sludge process, and the Chinese discharge standards can be satisfied satisfactorily.

[1]  T. Asano,et al.  Size distributions of particulate contaminants in wastewater and their impact on treatability , 1991 .

[2]  Gatze Lettinga,et al.  Advanced reactor design, operation and economy. , 1986 .

[3]  Anton M. Breure,et al.  Anaerobic waste water treatment , 1984 .

[4]  Jr W. Wesley Eckenfelder Industrial Water Pollution Control , 1967 .

[5]  G. Lettinga,et al.  The use of EGSB and UASB anerobic systems for low strength soluble and complex wastewaters at temperatures ranging from 8°C to 30°C. , 1988 .

[6]  P. M. Geary Evaluation of On-Site Disposal Options , 1993 .

[7]  J. S. Jeris Industrial Wastewater Treatment Using Anaerobic Fluidized Bed Reactors , 1983 .

[8]  A. Schellinkhout,et al.  Full-Scale Application of the UASB Technology for Sewage Treatment , 1992 .

[9]  C. Buisman Biotechnological sulphide removal with oxygen , 1989 .

[10]  K. R. Reddy,et al.  Aquatic plants for water treatment and resource recovery : Proceedings of the Conference on Research and Applications of Aquatic Plants for Water Treatment and Resource Recovery, held July 20-24, 1986, in Orlando, Florida , 1987 .

[11]  Gatze Lettinga,et al.  Upflow anaerobic sludge blanket (uasb) low cost sanitation research project in Bandung/Indonesia: 5th progress report (January-30 September 1987) , 1987 .

[12]  Jerome H. Svore,et al.  BIOLOGICAL TREATMENT OF SEWAGE AND INDUSTRIAL WASTES , 1959 .

[13]  Fernando Fdz-Polanco,et al.  Low temperature treatment of municipal sewage in anaerobic fluidized bed reactors , 1990 .

[14]  Gatze Lettinga,et al.  Anaerobic treatment of raw domestic sewage in UASB-reactors at temperatures from 9-20 C , 1985 .

[15]  A. D. Wheatley,et al.  Effluent treatment by anaerobic biofiltration , 1985 .

[16]  J. E. Schaapman,et al.  Performance of the 5 MLD UASB Reactor for Sewage Treatment at Kanpur, India , 1992 .

[17]  W. A. Pretorius Anaerobic digestion of raw sewage , 1971 .

[18]  G. Lettinga,et al.  Feasibility of the upflow anaerobic sludge blanket (UASB) process for the treatment of low-strength wastes. , 1979 .

[19]  Gatze Lettinga,et al.  Anaerobic treatment of raw sewage at lower temperatures , 1983 .

[20]  A. Noyola,et al.  Anaerobic treatment of domestic sewage with a rotating stationary fixed-film reactor , 1988 .

[21]  Marcos Eduardo de Souza,et al.  Development of Technology for the Use of the UASB Reactor in Domestic Sewage Treatment , 1986 .

[22]  C. Forster,et al.  Anaerobic treatment of dilute wastewaters using an upflow sludge blanket reactor , 1983 .

[23]  G Lettinga,et al.  Anaerobic treatment of raw domestic sewage at ambient temperatures using a granular bed UASB reactor , 1983, Biotechnology and bioengineering.

[24]  P. N. Hobson Book reviewProceedings of the seminar/workshop anaerobic treatment of sewage: Edited by M. S. Switzenbaum. National Science Foundation, 1985, paperback, 385 + vi pp. Free from Environmental Engineering, University of Massachusetts, Amhurst, Massachusetts 01003, USA. , 1986 .

[25]  R. Wijffels,et al.  Anaerobic degradation of the various fractions of slaughterhouse wastewater , 1988 .

[26]  A. E. Greenberg,et al.  Standard methods for the examination of water and wastewater : supplement to the sixteenth edition , 1988 .

[27]  A. M. Saatçi,et al.  Bacterial Die-Off in Waste Stabilization Ponds , 1987 .

[28]  Gatze Lettinga,et al.  Anaerobic treatment of domestic sewage under moderate climatic (Dutch) conditions using upflow reactors at increased superficial velocities. , 1992 .

[29]  T. Hvitved-Jacobsen,et al.  Method for Measurement of Reaeration in Gravity Sewers using Radiotracers , 1991 .

[30]  Gatze Lettinga,et al.  The application of the UASB-reactor for the direct treatment of domestic wastewater under tropical conditions , 1985 .

[31]  Senji Kaneko,et al.  Operation of Centralized Sludge Treatment Facilities , 1991 .

[32]  W. Gujer,et al.  Conversion processes in anaerobic digestion , 1983 .

[33]  J. W. Morris,et al.  Municipal wastewater treatment with the anaerobic attached microbial film expanded bed process , 1981 .

[34]  M. Stenstrom,et al.  Treatment of low strength domestic wastewater using the anaerobic filter , 1983 .

[35]  Carlo Collivignarelli,et al.  Anaerobic-aerobic treatment of municipal wastewaters with full-scale upflow anaerobic sludge blanket and attached biofilm reactors. , 1990 .