The chromate reductase purified from Pseudomonas ambigua was found to be homologous with several nitroreductases. Escherichia coli DH5␣ and Vibrio harveyi KCTC 2720 nitroreductases were chosen for the present study, and their chromate-reducing activities were determined. A fusion between glutathione Stransferase (GST) and E. coli DH5␣ NfsA (GST-EcNfsA), a fusion between GST and E. coli DH5␣ NfsB (GST-EcNfsB), and a fusion between GST and V. harveyi KCTC 2720 NfsA (GST-VhNfsA) were prepared for their overproduction and easy purification. GST-EcNfsA, GST-EcNFsB, and GST-VhNFsA efficiently reduced nitrofurazone and 2,4,6-trinitrotoluene (TNT) as their nitro substrates. The K m values for GST-EcNfsA, GST-EcNfsB, and GST-VhNfsA for chromate reduction were 11.8, 23.5, and 5.4 M, respectively. The V max values for GST-EcNfsA, GST-EcNfsB, and GST-VhNfsA were 3.8, 3.9, and 10.7 nmol/min/mg of protein, respectively. GST-VhNfsA was the most effective of the three chromate reductases, as determined by each V max /K m value. The optimal temperatures of GST-EcNfsA, GST-EcNfsB, and GST-VhNfsA for chromate reduction were 55, 30, and 30°C, respectively. Thus, it is confirmed that nitroreductase can also act as a chromate reductase. Nitroreductases may be used in chromate remediation. GST-EcNfsA, GST-EcNfsB, and GST-VhNfsA have a molecular mass of 50 kDa and exist as a monomer in solution. Thin-layer chromatography showed that GST-EcNfsA, GST-EcNfsB, and GST-VhNfsA contain FMN as a cofactor. GST-VhNfsA reduced
Cr(VI) to Cr(III). Cr(III) was much less toxic to E. coli than Cr(VI).Environmental pollution by chromium may be severe. Chromium contamination is known to be prevalent at U.S. Department of Energy sites (29). The electroplating and leather-tanning industries also contribute to environmental contamination with Cr(VI) (23). Chromate compounds containing Cr(VI) are used widely in the cooling towers of heavy industry and atomic power plants, since Cr(VI) prevents corrosion and the growth of organisms (2). Cr(VI) is soluble, toxic, and carcinogenic, whereas Cr(III) is less soluble and less toxic (12). Thus, it is desirable to change Cr(VI) into Cr(III). This approach is taken in the bioremediation of Cr(VI) pollution. It shows promise for solving pollution problems and has advantages over various other physical and chemical methods.Chromate-reducing activities can be found in the cell extracts of many bacteria (4,5,8,10,13,18,25,30,(33)(34)(35). Chromate reductase can reduce the toxicity of Cr(VI) by reducing it to Cr(III) and lowering its solubility (5, 9). The chromate reductase from Pseudomonas ambigua has been purified and characterized (33). Chromate-reducing activities have been associated with DT-diaphorase (7) and aldehyde oxidase (1) in the cell cytoplasm. Cytochrome P450 located in the cell membrane is also known to have chromate-reducing activity (21). It seems that various reductases in the cell can function in chromate reduction. P. ambigua chromate reductase (33) has high homology with Escherichia coli NfsA (59%) ...