Fouling characteristics in a membrane bioreactor coupled with anaerobic-anoxic-oxic process for coke wastewater treatment.

Experiments were conducted to investigate the fouling characteristics of a membrane bioreactor combined with anaerobic-anoxic-oxic process for coke wastewater treatment. Supernatant from the oxic tank was characterized as different hydrophilic/hydrophobic fractions by DAX-8 resin, with joint size partition also undertaken. Polysaccharides and proteins, mainly the fraction with molecular weight above 100kDa, were liable to accumulate in the supernatant. Hydrophilic fraction, mainly contributing to the subclass of molecular weight above 100kDa, was found most likely responsible for the flux deterioration by means of dead-end filtration tests. Analyses of particle and membrane pore size distribution revealed that major foulants had size comparable to the pore diameter. It can be inferred that steric factor (i.e. size exclusion) behaved primarily in the initial stage of fouling, while the role of hydrophobic interaction was of less significance.

[1]  G Amy,et al.  Impact of colloidal and soluble organic material on membrane performance in membrane bioreactors for municipal wastewater treatment. , 2006, Water research.

[2]  Zhiwei Wang,et al.  Extracellular polymeric substances (EPS) properties and their effects on membrane fouling in a submerged membrane bioreactor. , 2009, Water research.

[3]  Cristiano Piacsek Borges,et al.  The effects of long-term feeding of high organic loading in a submerged membrane bioreactor treating oil refinery wastewater , 2008 .

[4]  K. Kimura,et al.  Influence of suspension viscosity and colloidal particles on permeability of membrane used in membrane bioreactor (MBR). , 2004, Water science and technology : a journal of the International Association on Water Pollution Research.

[5]  J. Tay,et al.  Coke plant wastewater treatment by fixed biofilm system for COD and NH3-N removal , 1998 .

[6]  J. Leenheer,et al.  Comprehensive approach to preparative isolation and fractionation of dissolved organic carbon from natural waters and wastewaters. , 1981, Environmental science & technology.

[7]  T. Melin,et al.  Correlation of EPS content in activated sludge at different sludge retention times with membrane fouling phenomena. , 2008, Water research.

[8]  Xia Huang,et al.  A systematic insight into fouling propensity of soluble microbial products in membrane bioreactors based on hydrophobic interaction and size exclusion , 2010 .

[9]  Duu-Jong Lee,et al.  Enhanced treatment of coke plant wastewater using an anaerobic–anoxic–oxic membrane bioreactor system , 2009 .

[10]  Hua-Zhang Zhao,et al.  Study on treatment of coking wastewater by biofilm reactors combined with zero-valent iron process. , 2009, Journal of hazardous materials.

[11]  A. Drews,et al.  Recent advances in membrane bioreactors (MBRs): membrane fouling and membrane material. , 2009, Water research.

[12]  Rui Liu,et al.  Behaviour of soluble microbial products in a membrane bioreactor , 2000 .

[13]  T. Fukushima,et al.  Characterization of dissolved organic matter in effluents from wastewater treatment plants. , 2002, Water research.

[14]  Sara Arabi,et al.  Impact of protein/carbohydrate ratio in the feed wastewater on the membrane fouling in membrane bioreactors , 2008 .

[15]  J. Rodríguez,et al.  Treatment of coke wastewater in a sequential batch reactor (SBR) at pilot plant scale. , 2008, Bioresource technology.

[16]  Thomas Melin,et al.  Polymeric compounds in activated sludge supernatant -- Characterisation and retention mechanisms at a full-scale municipal membrane bioreactor. , 2007, Water research.

[17]  S. Judd The status of membrane bioreactor technology. , 2008, Trends in biotechnology.

[18]  W. Simons The Sadtler handbook of infrared spectra , 1978 .

[19]  S. Liang,et al.  Soluble microbial products in membrane bioreactor operation: Behaviors, characteristics, and fouling potential. , 2007, Water research.

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

[21]  El Hani Bouhabila,et al.  Fouling characterisation in membrane bioreactors , 2001 .

[22]  D. Lee,et al.  Bioaugmentation of cyanide-degrading microorganisms in a full-scale cokes wastewater treatment facility. , 2008, Bioresource technology.

[23]  Xia Huang,et al.  Effect of mixed liquor properties on fouling propensity in membrane bioreactors , 2009 .

[24]  David C. Stuckey,et al.  A REVIEW OF SOLUBLE MICROBIAL PRODUCTS (SMP) IN WASTEWATER TREATMENT SYSTEMS , 1999 .

[25]  M K Ghose,et al.  Complete physico-chemical treatment for coke plant effluents. , 2002, Water research.

[26]  F. Smith,et al.  COLORIMETRIC METHOD FOR DETER-MINATION OF SUGAR AND RELATED SUBSTANCE , 1956 .

[27]  P. Nielsen,et al.  Enzymatic activity in the activated-sludge floc matrix , 1995, Applied Microbiology and Biotechnology.

[28]  J. Rodríguez,et al.  Coke Wastewater Treatment by a Three-Step Activated Sludge System , 2008 .

[29]  R. Denoyel,et al.  Characterization of pore structure of a strong anion-exchange membrane adsorbent under different buffer and salt concentration conditions. , 2009, Journal of chromatography. A.

[30]  Hang-Sik Shin,et al.  Sludge characteristics and their contribution to microfiltration in submerged membrane bioreactors , 2003 .

[31]  Pierre Le-Clech,et al.  Fouling in membrane bioreactors used in wastewater treatment , 2006 .

[32]  G Amy,et al.  Correlation between membrane fouling and soluble/colloidal organic substances in membrane bioreactors for municipal wastewater treatment. , 2005, Water science and technology : a journal of the International Association on Water Pollution Research.

[33]  Duu-Jong Lee,et al.  Use of submerged anaerobic–anoxic–oxic membrane bioreactor to treat highly toxic coke wastewater with complete sludge retention , 2009 .

[34]  A. Andreadakis,et al.  Fractionation of proteins and carbohydrates of extracellular polymeric substances in a membrane bioreactor system. , 2009, Bioresource technology.