Constitutive trichloroethylene degradation led by tac promoter chromosomally integrated upstream of phenol hydroxylase genes of Ralstonia sp. KN1 and its nucleotide sequence analysis

Ralstonia sp. KN1-10A is a strain capable of degrading trichloroethylene (TCE) constitutively due to the tac promoter (Ptac) integrated upstream of the phenol hydroxylase genes (phy) in its chromosome. The expression of Ptac was analyzed using luxAB of Vibrio harveyi as a reporter. After determining the nucleotide sequence of phyABCDE required for TCE degradation, a luxAB-encoding fragment was integrated downstream of phyE by homologous recombination in strain KN1-10A, obtaining strain KN1-10A-LX. In the same manner, the luxAB-encoding fragment was integrated into the chromosome of the wild-type strain, KN1. The resultant strain KN1-LX was used to analyze the gene expression caused by phenol induction. The expression induced by Ptac was compared to that by phenol induction. Although the level of luxAB expression led by Ptac was almost equal to that induced by phenol, the TCE degradation rate by the Ptac-carrying KN1-10A-LX was markedly slower than that by the phenol-induced KN1-LX. These results suggest that an important gene for TCE degradation was not transcribed by Ptac in KN1-10A-LX. The nucleotide sequence analysis showed the existence of a small gene, phyZ, upstream of phyA, and Ptac was found to be integrated into the middle of phyZ in KN1-10A-LX. The effect of phyZ on TCE degradation was examined by using recombinant strains expressing phyABCDE with or without phyZ in a plasmid. The coexistence of phyZ markedly accelerated TCE degradation. Through an exhaustive expression analysis, it was demonstrated that the chromosomal integration of Ptac was a very attractive method for high and stable production of phenol hydroxylase for TCE degradation.     

Complete detoxification of tris(2-chloroethyl) phosphate by two bacterial strains: Sphingobium sp. strain TCM1 and Xanthobacter autotrophicus strain GJ10

Tris(2-chloroethyl) phosphate (TCEP), a flame retardant, is recently regarded as a potentially toxic and persistent environmental contaminant. We previously isolated TCEP-degrading bacterium, Sphingobium sp. strain TCM1, which, however, produced a toxic metabolite: 2-chloroethanol (2-CE). This study was undertaken to develop a detoxification technique of TCEP using strain TCM1 with a 2-CE-degrading bacterium: Xanthobacter autotrophicus strain GJ10. TCEP degradation by strain TCM1-resting cells was thermally stable for 30 min at 30 °C. It was optimal at 30 °C and at pH 8.5. In the optimum condition, TCM1 cells up to a final cell density of 0.8 at OD(660) in the reaction mixture were unable to hydrolyze the phosphotriester bonds of 10 μM TCEP completely. The addition of 50 μM Co(2+) to reaction mixture enhanced the hydrolysis and caused the complete hydrolysis at the cell density of 0.8. Strain GJ10 resting cells degraded 2-CE only slightly, which might be attributable to lack of coenzyme regeneration of enzymes involved in the degradation. In contrast, the growing cells degraded approximately 180 μM of 2-CE within 24 h. Based on these results, we designed a two-step TCEP detoxification reaction consisting of TCEP hydrolysis to 2-CE by strain TCM1-resting cells and the following degradation of the resulting 2-CE by strain GJ10-growing cells. The combined reaction completely detoxified 10 μM TCEP, and thus opens a way to microbial detoxification of the potential toxic, persistent organophosphorus compound.     

Binding of zearalenone, aflatoxin B1, and ochratoxin A by yeast-based products: a method for quantification of adsorption performance

A methodology was developed to quantify the efficiency of yeast-based products for adsorption of three mycotoxins: zearalenone (ZEA), aflatoxin B(1) (AFB(1)), and ochratoxin A (OTA). Eight products were tested (yeast cell wall or inactivated yeast). The described experimental protocol based on in vitro tests provided reliable isotherms for each mycotoxin. The most suitable models were the Hill model for ZEA, the Langmuir model for AFB(1), and the Freundlich model for OTA. From these models, original mathematical affinity criteria were defined to quantify the product adsorption performances for each mycotoxin. The best yeast product, a yeast cell wall from baker's yeast, can adsorb up to 68% of ZEA, 29% of AFB(1), and 62% of OTA, depending on the mycotoxin concentrations. The adsorption capacity largely depended both on yeast composition and mycotoxin, but no direct correlation between yeast composition and adsorption capacity was found, confirming that adsorption of mycotoxin on yeast-based products involves complex phenomena. The results of this study are useful for comparing the adsorption efficiency of various yeast products and understanding the mechanisms involved in adsorption.