Biodegradation of the organochlorine insecticide, endosulfan, and the toxic metabolite, endosulfan sulfate, by Klebsiella oxytoca KE-8

Biodegradation of endosulfan, a chlorinated cyclodiene insecticide, is generally accompanied by production of the more toxic and more persistent metabolite, endosulfan sulfate. Since our reported endosulfan degrader, Klebsiella pneumoniae KE-1, failed to degrade endosulfan sulfate, we tried to isolate an endosulfan sulfate degrader from endosulfan-polluted soils. Through repetitive enrichment and successive subculture using mineral salt medium containing endosulfan or endosulfan sulfate as the sole source of carbon and energy, we isolated a bacterium capable of degrading endosulfan sulfate as well as endosulfan. The bacterium KE-8 was identified as Klebsiella oxytoca from the results of 16S rDNA sequence analysis. In biodegradation assays with KE-8 using mineral salt medium containing endosulfan (150 mg l^–1) or endosulfan sulfate (173 mg l^–1), the biomass was rapidly increased to an optical density at 550 nm of 1.9 in 4 days and the degradation constants for - and -endosulfan, and endosulfan sulfate were 0.3084, 0.2983 and 0.2465 day^–1, respectively. Analysis of the metabolites further suggested that K. oxytoca KE-8 has high potential as a biocatalyst for bioremediation of endosulfan and/or endosulfan sulfate.     

Isolation and characterization of a Pseudomonas sp. strain IITR01 capable of degrading α‐endosulfan and endosulfan sulfate

Aim: To isolate bacteria capable of degrading endosulfan (ES) and the more toxic ES sulfate and to characterize their metabolites. Methods and Results: A Pseudomonas sp. strain IITR01 capable of degrading α‐ES and toxic ES sulfate was isolated using technical‐ES through enrichment culture techniques. No growth and no degradation were observed using β‐ES. Thin‐layer chromatography and gas chromatography‐mass spectrum analysis revealed the disappearance of both α‐ES and ES sulfate and the formation of hydroxylated products ES diol, ether and lactone. We show here for the first time the formation of aforementioned metabolites in contrast to ES hemisulfate yielded by an Arthrobacter sp. Metabolism of α‐ES and endosulfate was also observed using the crude cell extract of IITR01. The molecular mass of protein induced during the degradation of α‐ES and sulfate as substrate was found to be approximately 150 kDa as determined by sodium dodecyl sulfate–polyacrylamide gel electrophoresis (SDS–PAGE). Conclusion: We describe characterization of bacterium capable of degrading α‐ES and ES sulfate but not β‐ES. Genetic investigation suggests that a gene nonhomologous to the reported esd may be present in the strain IITR01. Significance and Impact of the Study: This study describes toxic ES degradation by a Pseudomonas species that may be utilized for the bioremediation of the industrial soils contaminated with ES residues.     

Biodegradation of organochlorine pesticide, endosulfan, by a fungal soil isolate, Aspergillus niger

Endosulfan is a chlorinated pesticide widely used in India for the protection of cotton, tea, sugarcane and vegetables. The persistence of endosulfan in environment and toxic effects on biota necessitate its removal. The role of soil fungi in recycling organic matter prompted us to attempt biodegradation of endosulfan using fungi. This study aims at enrichment, isolation and screening of fungi capable of metabolizing endosulfan. In all, 16 fungal isolates were obtained by enrichment of soil samples that had seems exposed to endosulfan before. Isolates were screened by a gradient plate assay, and results were confirmed by broth assay. On the basis of tolerance to endosulfan, an isolate, identified as Aspergillus niger was selected for further studies. The culture could tolerate 400 mg ml⁻¹ of technical grade endosulfan. Complete disappearance of endosulfan was seen on 12 days of incubation. Evolution of carbon dioxide during endosulfan metabolism has indicated the complete mineralization of endosulfan. Change in pH of culture broth to acidic range supported the biological transformation. Thin layer chromography (TLC) analyses revealed the formation of various intermediates of endosulfan metabolism including endosulfan diol, endosulfan sulfate, and an unidentified metabolite. The toxic intermediate, endosulfan sulfate, was also metabolized, further resulting in complete mineralization of endosulfan. Direct desulfurization of endosulfan sulfate or a novel pathway could be the mechanism of endosulfan and endosulfan sulfate degradation in Aspergillus niger. The fungal strain isolated by us could prove valuable for bioremediation of endosulfan contaminated soils and waters.     

Expression and inducibility of endosulfan metabolizing gene in Rhodococcus strain isolated from earthworm gut microflora for its application in bioremediation

The metabolizing potential of a bacterial strain Rhodococcus MTCC 6716, isolated from the gut of an Indian earthworm (Metaphire posthuma) was studied for endosulfan bioremediation. In the present work, the optimum conditions for the maximum growth, kinetic of endosulfan degradation, regression equation, half life and correlation coefficient were studied. Endosulfan induced alterations in the expression of mRNA and protein of specific endosulfan metabolizing marker gene (Esd) was studied. Maximum growth of bacteria was observed at pH 7.0, 30°C and 0.085 M sodium chloride concentration in a liquid culture medium. Endosulfan was degraded by Rhodococcus strain up to 97.23% within 15 days without producing toxic metabolite and with strong correlation coefficient (-0.728) and half life 5.99 days. Endosulfan degradation was mediated through gene(s) present in genomic DNA. Expression of marker gene was found endosulfan concentration dependent. The results suggest that this novel strain (Rhodococcus) may be utilized for bioremediation of endosulfan.     

Biodegradability and biodegradation pathways of endosulfan and endosulfan sulfate

Endosulfan and endosulfan sulfate are persistent organic pollutants that cause serious environmental problems. Although these compounds are already prohibited in many countries, residues can be detected in soils with a history of endosulfan application. Endosulfan is transformed in the environment into endosulfan sulfate, which is a toxic and persistent metabolite. However, some microorganisms can degrade endosulfan without producing endosulfan sulfate, and some can degrade endosulfan sulfate. Therefore, biodegradation has the potential to clean up soil contaminated with endosulfan. In this review, we provide an overview of aerobic endosulfan degradation by bacteria and fungi, and a summary of recent advances and prospects in this research field.     

Biodegradation of endosulfan and endosulfan sulfate by <Emphasis Type="Italic">Achromobacter xylosoxidans</Emphasis> strain C8B in broth medium

Endosulfan is one of the most widely used wide spectrum cyclodiene organochlorine insecticide. In environment, endosulfan can undergo either oxidation or hydrolysis reaction to form endosulfan sulfate and endosulfan diol respectively. Endosulfan sulfate is as toxic and as persistent as its parent isomers. In the present study, endosulfan degrading bacteria were isolated from soil through selective enrichment technique using sulfur free medium with endosulfan as sole sulfur source. Out of the 8 isolated bacterial strains, strain C8B was found to be the most efficient endosulfan degrader, degrading 94.12% α-endosulfan and 84.52% β-endosulfan. The bacterial strain was identified as Achromobacter xylosoxidans strain C8B on the basis of 16S rDNA sequence similarity. Achromobacter xylosoxidans strain C8B was also found to degrade 80.10% endosulfan sulfate using it as sulfur source. No known metabolites were found to be formed in the culture media during the entire course of degradation. Besides, the bacterial strain was found to degrade all the known endosulfan metabolites. There was marked increase in the quantity of released CO₂ from the culture media with endosulfan as sulfur source as compared to MgSO₄ suggesting that the bacterial strain, Achromobacter xylosoxidans strain C8B probably degraded endosulfan completely through the formation of endosulfan ether.     

Isolation and characterization of a Mycobacterium strain that metabolizes the insecticide endosulfan

AIM: The aim of this study was to isolate and characterize a bacterium capable of metabolizing endosulfan. METHODS AND RESULTS: A endosulfan-degrading bacterium (strain ESD) was isolated from soil inoculum after repeated culture with the insecticide as the sole source of sulfur. Analysis of its 16S rRNA gene sequence, and morphological and physiological characteristics revealed it to be a new fast-growing Mycobacterium, closely related to other Mycobacterium species with xenobiotic-degrading capabilities. Degradation of endosulfan by strain ESD involved both oxidative and sulfur-separation reactions. Strain ESD did not degrade endosulfan when sulfite, sulphate or methionine were present in the medium along with the insecticide. Partial degradation occurred when the culture was grown, with endosulfan, in the presence of MOPS (3-(N-morpholino)propane sulphonic acid), DMSO (dimethyl sulfoxide), cysteine or sulphonane and complete degradation occurred in the presence of gutathione. When both beta-endosulfan and low levels of sulphate were provided as the only sources of sulfur, biphasic exponential growth was observed with endosulfan metabolism being restricted to the latter phase of exponential growth. CONCLUSIONS: This study isolated a Mycobacterium strain (strain ESD) capable of metabolizing endosulfan by both oxidative and sulfur-separation reactions. The endosulfan-degrading reactions are a result of the sulfur-starvation response of this bacterium. SIGNIFICANCE AND IMPACT OF THE STUDY: This describes the isolation of a Mycobacterium strain capable of degrading the insecticide endosulfan. This bacterium is a valuable source of enzymes for use in enzymatic bioremediation of endosulfan residues.     

Microcosmic study of endosulfan degradation by Paenibacillus sp. ISTP10 and its toxicological evaluation using mammalian cell line

In the present study, an endosulfan degrading strain Paenibacillus sp. ISTP10 was isolated from activated sludge. Soil microcosms were set up with endosulfan (60 mg kg⁻¹ of dry soil) to evaluate the degradation potency of the strain. Soil samples from the microcosms were collected at regular intervals and the organic compounds were extracted with hexane. GC–MS analysis of the soil extract showed the formation of metabolites of endosulfan such as endosulfan diol and endosulfan ether confirming that the strain degrades endosulfan via a hydrolytic pathway. Methyl tetrazolium (MTT) assay for cytotoxicity and alkaline comet assay for genotoxicity were carried out in human hepato-carcinoma cell line HepG2 to evaluate the toxic potential of endosulfan and its degraded metabolites. The bacterium reduced toxicity as determined by an increase in LC₅₀ value by 75.86 fold and a reduction in Olive Tail Moment by 21 fold after 30 days of treatment. The by-products of degradation were found to be less toxic than the parent compound showing the biodegradation and detoxification potential of endosulfan by Paenibacillus sp. ISTP10.     

Biodegradation of α and β endosulfan in broth medium and soil microcosm by bacterial strain Bordetella sp. B9

Bacterial strains were isolated from endosulfan treated soil to study the microbial degradation of this pesticide in broth medium and soil microcosm. The isolates were grown in minimal medium and screened for endosulfan degradation. The strain, which utilized endosulfan and showed maximum growth, was selected for detail studies. Maximum degrading capability in shake flask culture was shown by Bordetella sp. B9 which degraded 80% of α endosulfan and 86% of β endosulfan in 18 days. Soil microcosm study was also carried out using this strain in six different treatments. Endosulfan ether and endosulfan lactone were the main metabolites in broth culture, while in soil microcosm endosulfan sulfate was also found along with endosulfan ether and endosulfan lactone. This bacterial strain has a potential to be used for bioremediation of the contaminated sites.     

Enrichment of a microbial culture capable of degrading endosulphate, the toxic metabolite of endosulfan

AIMS: The aim of this study was to isolate a source of enzymes capable of degrading endosulphate (endosulfan sulphate), the toxic metabolite of the pesticide endosulfan. METHODS AND RESULTS: A microbial broth culture capable of degrading endosulphate was enriched from endosulfan-contaminated soil by providing the metabolite as the sole source of sulphur in broth culture. No microbial growth was observed in the absence of endosulphate. In the presence of endosulphate, growth of the culture occurred with the concomitant formation of three chlorine-containing compounds. Thin layer chromatography and gas chromatography--mass spectral analysis identified these metabolites as endosulfan monoaldehyde, 1,2,3,4,7,7-hexachloro-5,6-bis(methylene)bicyclo[2.2.1]-2-heptene and 1,2,3,4,7,7-hexachloro-5-hydroxymethylene-6-methylenebicyclo[2.2.1]-2-heptene. The second and third compounds have not been reported in previous metabolic studies. The enriched culture was also able to utilize alpha- and beta-endosulfan as sulphur sources, each producing the hydrolysis product endosulfan monoaldehyde as the sole chlorine-containing metabolite. Alpha-endosulfan was more readily hydrolysed than the beta-isomer. CONCLUSIONS: This study isolated a mixed microbial culture capable of degrading endosulphate. The products of degradation were characterized as novel endosulfan metabolites. SIGNIFICANCE AND IMPACT OF THE STUDY: This study describes the isolation of a mixed microbial culture that is potentially a valuable source of hydrolysing enzymes for use in enzymatic bioremediation, particularly of endosulphate and alpha-endosulfan residues.