Treatment of saline wastewaters from marine‐products processing factories by activated sludge reactor

Abstract An activated sludge reactor, operated at room temperature (20–30° C) was used to treat saline wastewaters generated by marine‐products industries. The system was operated continuously and the influence of the organic loading rates (OLRs), varying from 250 to 1000 mg COD 1−1 day−1, on chemical oxygen demand (COD) removal was investigated. The system, inoculated with NaCl‐acclimated culture, removed up to 98% and 88% of the influent COD concentrations at OLRs of 250 and 1000 mg COD l−1 day−1, respectively. Since the organic pollution is essentially composed of proteins, microorganisms, which produced proteolytic enzymes, were isolated from the activated sludge culture. One bacterium with the highest protease activity, identified as Bacillus cereus, was chosen for protease production in fishery wastewaters of different concentrations containing combined heads and viscera powder. Protease synthesis was strongly enhanced when cells were cultivated in two times diluted fishery wastewaters. The enhancement of protease synthesis could have been due to the presence in effluent of organic matters or salts, which stimulated the growth of the strain and protease production.

[1]  B. Eggum,et al.  Nutritional value of fish viscera silage. , 1981, Journal of the science of food and agriculture.

[2]  M. Nasri,et al.  Production of protease by Bacillus subtilis grown on sardinelle heads and viscera flour. , 2001, Bioresource technology.

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

[4]  Ludzack Fj,et al.  Tolerance of high salinities by conventional wastewater treatment processes. , 1965 .

[5]  A. Bories,et al.  Anaerobic digestion of high-strength distillery wastewater (cane molasses stillage) in a fixed-film reactor , 1988 .

[6]  Hakim Lounici,et al.  Treatment of fishery washing water by ultrafiltration , 1996 .

[7]  Robert L. Irvine,et al.  Treatment of hypersaline wastewater in the sequencing batch reactor , 1995 .

[8]  Thongchai Panswad,et al.  Impact of high chloride wastewater on an anaerobic/anoxic/aerobic process with and without inoculation of chloride acclimated seeds , 1999 .

[9]  D. Patterson Free-Living Freshwater Protozoa , 1991 .

[10]  Júlio M. Novais,et al.  Optimisation of the biological treatment of hypersaline wastewater from Dunaliella salina carotenogenesis , 2001 .

[11]  A. Kembhavi,et al.  Salt-tolerant and thermostable alkaline protease fromBacillus subtilis NCIM No. 64 , 1993, Applied biochemistry and biotechnology.

[12]  F. Kargı,et al.  Effect of salt concentration on biological treatment of saline wastewater by fed-batch operation , 1996 .

[13]  F. Kargı,et al.  Enhancement of biological treatment performance of saline wastewater by halophilic bacteria , 1996 .

[14]  Estrella Aspé,et al.  Treatment of recycled wastewaters from fishmeal factory by an anaerobic filter , 1997, Biotechnology Letters.

[15]  P. Bishop,et al.  Treatment of Saline Domestic Wastewater Using RBCs , 1982 .

[16]  Moncef Nasri,et al.  Biological treatment of saline wastewaters from marine‐products processing factories by a fixed‐bed reactor , 2002 .