Chromate reduction by Microbacterium liquefaciens immobilised in polyvinyl alcohol

A polyvinyl alcohol-based immobilisation technique has been utilised for entrapping the newly-isolated chromate-reducing bacterium, Microbacterium liquefaciens MP30. Three immobilisation methods were evaluated: PVA-nitrate, PVA-borate and PVA-alginate. Chromate reduction was studied in batch and continuous-flow bioreactors, where the beads maintained integrity during continuous operation. PVA-borate and PVA-alginate cell beads showed a higher rate and extent of chromate reduction than PVA-nitrate cell beads in batch experiments. With the former 100 μM Cr(VI) was removed within 4 days, while only 40 μM Cr(VI) was removed using the latter, and with no increase in Cr(VI) removal subsequently. Cell activity was maintained during immobilisation but the rate of Cr(VI) removal by immobilised cells was only half that of an equivalent mass of free cells. Using PVA-alginate cell beads in a continuous-flow system, chromate removal was maintained at 90–95% from a 50 μM solution over 20 days without signs of bead breakdown.

[1]  P. Urone Stability of Colorimetric Reagent for Chromium, s-Diphenylcarbazide, in Various Solvents , 1955 .

[2]  S. Venitt,et al.  Mutagenicity of chromates in bacteria and its relevance to chromate carcinogenesis , 1974, Nature.

[3]  S. De Flora,et al.  Salmonella typhimurium , 2022 .

[4]  K. Imai,et al.  Immobilization of Enzyme into Poly(vinyl alcohol) Membrane , 1986, Biotechnology and bioengineering.

[5]  John F. Kennedy,et al.  Immobilised Enzymes and Cells , 1990 .

[6]  O. Ariga,et al.  Immobilization of microorganisms with PVA hardened by iterative freezing and thawing , 1987 .

[7]  K. Furukawa,et al.  Immobilization of activated sludge by PVA–boric acid method , 1987, Biotechnology and bioengineering.

[8]  Tsukasa Mori,et al.  Isolation and Characterization of an Enterobacter cloacae Strain That Reduces Hexavalent Chromium under Anaerobic Conditions , 1989, Applied and environmental microbiology.

[9]  K. Y. Wu,et al.  Cell immobilization using PVA crosslinked with boric acid. , 1992, Biotechnology and bioengineering.

[10]  K. Østgaard,et al.  Large-scale production and purification of κ-carrageenase from Pseudomonas carrageenovora for applications in seaweed biotechnology , 1993 .

[11]  H. Ohtake,et al.  Development of a bioreactor system for the treatment of chromate wastewater using Enterobacter cloacae HO1 , 1994 .

[12]  K. Hanaki,et al.  Protection of methanogenic bacteria from low pH and toxic materials by immobilization using polyvinyl alcohol , 1994 .

[13]  Hai Shen,et al.  Modeling hexavalent chromium reduction in Escherichia coli 33456 , 1994, Biotechnology and bioengineering.

[14]  C. Xiao,et al.  Factors affecting hexavalent chromium reduction in pure cultures of bacteria , 1995 .

[15]  J. Tramper,et al.  Characteristics of and selection criteria for support materials for cell immobilization in wastewater treatment , 1996 .

[16]  H. Ohtake,et al.  Optimal operation of bioreactor system developed for the treatment of chromate wastewater using enterobacter cloacae HO-1 , 1996 .

[17]  Chih-Cheng Chang,et al.  Immobilization of Alcaligenes eutrophus using PVA crosslinked with sodium nitrate , 1998 .

[18]  H. Ohtake,et al.  Factors affecting chromate reduction in Enterobacter cloacae strain HO1 , 1989, Applied Microbiology and Biotechnology.

[19]  N. Ahmed,et al.  Reduction of chromate by microorganisms isolated from metal contaminated sites of Karachi, Pakistan , 2000, Biotechnology Letters.

[20]  P. DeLeo,et al.  Reduction of hexavalent chromium by Pseudomonas fluorescens LB300 in batch and continuous cultures , 2004, Applied Microbiology and Biotechnology.

[21]  Henry L. Ehrlich,et al.  Chromate resistance and reduction in Pseudomonas fluorescens strain LB300 , 1988, Archives of Microbiology.