Ajit Kumar

Microbial degradation of 2,4-dichlorophenoxyacetic acid: Insight into the enzymes and catabolic genes involved, their regulation and biotechnological implications

Abstract A considerable progress has been made to understand the mechanisms of biodegradation of 2,4-dichlorophenoxyacetic acid (2,4-D). 2,4-D biodegradation pathway has been elucidated in many microorganisms including Cupriavidus necator JMP134 (previously known as Wautersia eutropha, Ralstonia eutropha and Alcaligenes eutrophus) and Pseudomonas strains. It generally involves the side chain removal of 2,4-D by α-ketoglutarate-dependent 2,4-D dioxygenase (tfdA) to form 2,4-dichlorophenol (2,4-DCP); hydroxylation of 2,4-DCP by 2,4-DCP hydroxylase (tfdB) to form dichlorocatechol; ortho or meta cleavage of dichlorocatechol by chlorocatechol 1,2-dioxygenase (tfdC) to form 2,4-dichloro-cis,cis-muconate; conversion of 2,4-dichloro-cis,cis-muconate to 2-chlorodienelactone by chloromuconate cycloisomerase (tfdD); conversion of 2-chlorodienelactone to 2-chloromaleylacetate by chlorodienelactone hydrolase (tfdE) and, finally, conversion of 2-chloromaleylacetate to 3-oxoadepate via maleylacetate by chloromaleylacetate reductase and maleylacetate reductase (tfdF), respectively, which is funnelled to the tricarboxylic acid cycle. The latest review on microbial breakdown of 2,4-D, other halogenated aromatic pesticides, and related compounds was compiled by Haggblom, however, a considerable progress has been made in this area of research since then. Thus, this review focuses on the recent advancement on 2,4-D biodegradation, the enzymes, and genes involved and their biotechlogical implications.

Cloning, expression, purification and three-dimensional structure prediction of haloalkane dehalogenase from a recently isolated Ancylobacter aquaticus strain UV5.

Haloalkane dehalogenase (DhlA) converts 1,2-dichloroethane (1,2-DCA) to 2-chloroethane in the genus Ancylobacter and Xanthobacter autotrophicus GJ10 (XaDhlA) and allows these organisms to utilise 1,2-DCA and some other halogenated alkanes for growth. The DhlA encoding gene (dhlA) was PCR-amplified from the genomic DNA of a recently isolated Ancylobacter aquaticus UV5 strain, cloned and overexpressed in Escherichiacoli BL21 (DE3). The recombinant enzyme was purified by using Amicon ultra-15 centrifugal filter units, an anion-exchange QFF column followed by a gel-filtration column (Sephacryl HR100). Enzyme activity was determined by using 1,2-DCA as a substrate. Three-dimensional structure of the enzyme was predicted using SWISS-MODEL workspace and the biophysical properties were predicted by submitting the amino acid sequence of DhlA on ExPASy server. DhlA (Mr 35kDa) exhibited optimum activity at temperature 37°C and pH 9.0. The enzyme retained approximately 50% of its activity after 1h of incubation at 50°C, and showed moderate stability against denaturing agent urea. The DhlA displayed a Km value of 842μM and kcat/Km ratio of 168mM(-)(1)min(-)(1) for its substrate 1,2-DCA. This DhlA was found to belong to the α/β hydrolase family with a catalytic triad composed of Asp-His-Asp in its active site. This is the first study reporting on the characterisation and reaction kinetics of purified DhlA from A.aquaticus UV5 indigenous to contaminated site in Africa.

Enzyme activity and gene expression profiles of Xanthobacter autotrophicus GJ10 during aerobic biodegradation of 1,2-dichloroethane

Xanthobacter autotrophicus GJ10 has been widely studied because of its ability to degrade halogenated compounds, especially 1,2-dichloroethane (1,2-DCA), which is achieved through chromosomal as well as plasmid pAUX1 encoded 1,2-DCA degrading genes. This work described the gene expression and enzyme activity profiles as well as the intermediates formed during the 1,2-DCA degradation by this organism. A correlation between gene expression, enzyme activity and metabolic intermediates, after the induction of GJ10 grown culture with 1,2-DCA, was established at different time intervals. Haloalkane dehalogenase (dhlA) and haloacid dehalogenase (dhlB) were constitutively expressed while the expression of alcohol dehydrogenase (max) and aldehyde dehydrogenase (ald) was found to be inducible. The DhlA and DhlB activities were relatively higher compared to that of the inducible enzymes, Max and Ald. To the best of our knowledge, this is the first study to correlate gene expression profiles with enzyme activity and metabolite formation during 1,2-DCA degradation process in GJ10. Findings from this study may assist in fully understanding the mechanism of 1,2-DCA degradation by GJ10. It could also assist in the design and implementation of appropriate bioaugmentation strategies for complete removal of 1,2-DCA from contaminated environment.

Ensifer meliloti overexpressing Escherichia coli phytase gene ( appA ) improves phosphorus (P) acquisition in maize plants

The Escherichia coli phytase gene appA encoding enzyme AppA was cloned in a broad host range plasmid pBBR1MCS2 (lac promoter), termed pVA1, and transformed into the Ensifer meliloti 1020. Transformation of pVA1 in Ensifer meliloti {E. m (pVA1)} increased its phosphatase and phytase activity by ∼9- and ∼50-fold, respectively, compared to the transformants containing empty plasmid as control {E. m (pBBR1MCS2)}. The western blot experiments using rabbit anti-AppA antibody showed that AppA is translocated into the periplasm of the host after its expression. Ensifer meliloti harboring AppA protein {E. m (pVA1)} and {E. m (pBBR1MCS2)} could acidify the unbuffered phytate minimal media (pH 8.0) containing Ca-phytate or Na-phytate as sole organic P (Po) source to below pH 5.0 and released P. However, both {E. m (pVA1)} and {E. m (pBBR1MCS2)} neither dropped pH of the medium nor released P when the medium was buffered at pH 8.0 using Tris–Cl, indicating that acidification of medium was important for the enzymatic hydrolysis of phytate. Further experiments proved that maize plants inoculated with {E. m. (pVA1)} showed increase in growth under sterile semi solid agar (SSA) medium containing Na-phytate as sole P source. The present study could be helpful in generating better transgenic bioinoculants harboring phosphate mineralization properties that ultimately promote plant growth.

l-2-Haloacid dehalogenase from Ancylobacter aquaticus UV5: Sequence determination and structure prediction

A novel 25 kDa L-2-haloacid dehalogenase (L-2-DhlB) from a recently isolated Ancylobacter aquaticus strain UV5 indigenous to contaminated site in South Africa is reported here with its gene sequence. The enzyme was purified to 22.1-fold increase in specific activity of 72.9 U/mg protein when the organism was grown in medium supplemented with 5 mM 1,2-dichloroethane (1,2-DCA). L-2-DhlB was optimally active at pH 9.0 and 37°C with poor stability at 50°C, retaining 50% of its activity after 30 min, but inactivated rapidly at 60°C. L-2-DhlB catalyzed monochloroacetate (MCA) with Km and Vmax values of 0.47 mM and 2.4 μM/min, respectively. L-2-DhlB exhibited the kcat value of 4.8/min. Expression of about 100% relative activity of L-2-DhlB on the substrate L-2-monochloropropionate (L-2-MCPA) as compared to 5% on D-2-monochloropropionate (D-2-MCPA) suggested that L-2-DhlB belongs to the family of L-2-haloacid dehalogenases. ES-mass spectroscopy and bioinformatics tools resulted in 693 bp ORF sequence corresponding to 230 amino acid protein. NCBI-BLAST of L-2-DhlB resulted in the detection of a putative conserved domain of hypothetical haloacid dehalogenase (HAD)-like superfamily and subfamily IA.

Two structurally different dienelactone hydrolases (TfdEI and TfdEII) from Cupriavidus necator JMP134 plasmid pJP4 catalyse cis- and trans-dienelactones with similar efficiency.

In this study, dienelactone hydrolases (TfdEI and TfdEII) located on plasmid pJP4 of Cupriavidus necator JMP134 were cloned, purified, characterized and three dimensional structures were predicted. tfdEI and tfdEII genes were cloned into pET21b vector and expressed in E. coli BL21(DE3). The enzymes were purified by applying ultra-membrane filtration, anion-exchange QFF and gel-filtration columns. The enzyme activity was determined by using cis-dienelactone. The three-dimensional structure of enzymes was predicted using SWISS-MODEL workspace and the biophysical properties were determined on ExPASy server. Both TfdEI and TfdEII (Mr 25 kDa) exhibited optimum activity at 37°C and pH 7.0. The enzymes retained approximately 50% of their activity after 1 h of incubation at 50°C and showed high stability against denaturing agents. The TfdEI and TfdEII hydrolysed cis-dienelactone at a rate of 0.258 and 0.182 µMs−1, with a Km value of 87 µM and 305 µM, respectively. Also, TfdEI and TfdEII hydrolysed trans-dienelactone at a rate of 0.053 µMs−1 and 0.0766 µMs−1, with a Km value of 84 µM and 178 µM, respectively. The TfdEI and TfdEII kcat/Km ratios were 0.12 µM−1s−1and 0.13 µM−1s−1 and 0.216 µM−1s−1 and 0.094 µM−1s−1 for for cis- and trans-dienelactone, respectively. The kcat/Km ratios for cis-dienelactone show that both enzymes catalyse the reaction with same efficiency even though Km value differs significantly. This is the first report to characterize and compare reaction kinetics of purified TfdEI and TfdEII from Cupriavidus necator JMP134 and may be helpful for further exploration of their catalytic mechanisms.

Chloroacetaldehyde dehydrogenase from Ancylobacter aquaticus UV5: Cloning, expression, characterization and molecular modeling

1,2-Dichloroethane (1,2-DCE) is oxidatively converted to a carcinogenic intermediate compound, chloroacetaldehyde by chloroacetaldehyde dehydrogenase (CAldA) during its biodegradation by many bacterial strains, including Xanthobacter autotrophicus and Ancylobacter aquaticus. In this study, a 55kDa NAD-dependent CAldA expressed by chromosomally encoded aldA gene, is reported in an indigenous Ancylobacter aquaticus UV5. A. aquaticus UV5 aldA gene was found to be 99% homologous to the plasmid (pXAU1) encoded aldA gene reported in X. autotrophicus GJ10. Pulse-field gel electrophoresis (PFGE) and PCR experiments revealed the absence of pXAU1 in A. aquaticus UV5 and that aldA was chromosomal encoded. A 6× His-tag fused CAldA cloned in pET15b, overexpressed and purified on Co-agarose affinity column using AKTA purification system showed Mr of 57,526. CAldA was active optimally at pH9 and 30°C. The Km and vmax for the substrate, acetaldehyde were found to be 115μM and 650mU/mg, respectively. CAldA substrate specificity was found to be low for chloroacetaldehyde, formaldehyde, propionaldehyde, butyraldehyde, benzaldehyde and glutaraldehyde as compared to acetaldehyde. Computational modeling revealed a predicted structure of CAldA consisting of five β-sheets that comprise seven antiparallel β-strands and 11 mix strands. The Molecular Dynamics and Docking studies showed that acetaldehyde bind to CaldA more tightly as compared to chloroacetaldehyde.

Aerobic degradation of 2,4-dichlorophenoxyacetic acid and other chlorophenols by Pseudomonas strains indigenous to contaminated soil in South Africa: Growth kinetics and degradation pathway

Three indigenous pseudomonads, Pseudomonas putida DLL-E4, Pseudomonas reactans and Pseudomonas fluorescens, were isolated from chlorophenol-contaminated soil samples collected from a sawmill located in Durban (South Africa). The obtained isolates were tested for their ability to degrade chlorophenolic compounds: 2,4-dichlorophenoxyacetic acid (2,4-D), 2,4-dichlorophenol (2,4-DCP) and 2,4,6-trichlorophenol (2,4,6-TCP) in batch cultures. The isolates were found to effectively degrade up to 99.5, 98.4 and 94.0% with a degradation rate in the range of 0.67–0.99 (2,4-D), 0.57–0.93 (2,4-DCP) and 0.30–0.39 (2,4,6-TCP) mgL–1 day–1 for 2,4-D; 2,4-DCP and 2,4,6-TCP, respectively. The degradation kinetics model revealed that these organisms could tolerate up to 600 mg/L of 2,4-DCP. Catechol 2,3-dioxygenase activity detected in the crude cell lysates of P. putida DLL-E4 and P. reactans was 21.9- and 37.6-fold higher than catechol 1,2-dioxygenase activity assayed, suggesting a meta-pathway for chlorophenol degradation by these organisms. This is also supported by the generally high expression of C23O gene (involved in meta-pathway) relative to tfdC gene (involved in ortho-pathway) expression. Results of this study will be helpful in the exploitation of these organisms and/or their enzymes in bioremediation strategies for chlorophenol-polluted environment.