This study presents the degradation of phenanthrene by Mycoplana sp. MVMB2 isolated from petroleum contaminated soil and the media optimization by factorial design experiments. The Plackett-Burman design was used to evaluate the effects of eight variables (potassium dihydrogen phosphate, disodium hydrogen phosphate, magnesium sulfate, calcium chloride, ferrous sulfate, glucose, inoculum concentration, and phenanthrene concentration) on phenanthrene degradation. Based on the results, the critical medium components having significant influence on the degradation were found to be disodium hydrogen phosphate, magnesium sulfate, ferrous sulfate, and phenanthrene. Furthermore, these four variables were used as central composite design parameters. The optimum minimal salt medium composition obtained by conventional and factorial design experiments for the degradation of phenanthrene by Mycoplana sp. MVMB2 at pH 6.5 and 308C were found to be, potassium 2.5 g/L dihydrogen phosphate, 0.3505 g/L disodium hydrogen phosphate, 0.5501 g/L magnesium sulfate, 0.02 g/L calcium chloride, 0.0261 g/L ferrous sulfate, 0.6756 g/L phenanthrene, 0.5 g/L glucose, 0.5 g/L ammonium sulfate, and inoculum 5% v/v. The phenanthrene degradation was confirmed by analyzing the metabolites formed.Abbreviations: ANOVA, analysis of variance; CCD, central composite design; PAH, polycyclic aromatic hydrocarbon; RSM, response surface methodology 51
A study on bioremediation of soil contaminated with petroleum sludge was performed using Bacillus pumilus/MVSV3 Accession number JN089707 . In this study, 5 kg of agricultural soil was mixed well with 5% oil sludge and fertilizers containing nitrogen, phosphorus and potassium-N:P:K . The treatment resulted in 97% removal of total petroleum hydrocarbon TPH in 122 d in bacteria mixed contaminated soil when compared to 12% removal of TPH in uninoculated contaminated soil. The population of the microorganism remained stable after introduced into the oil environment. The physical and chemical parameters of the soil mixed with sludge showed variation indicating improvement and the pH level decreased during the experiment period. Elemental analysis and Gas Chromatography-Mass Spectroscopy GC-MS analysis revealed the bacterial ability to degrade oil sludge components. Growth experiments with Trigonellafoenumgraecum Fenugreek showed the applicability of bioremediated soil for the production.
Bioremediation of Phenanthrene by Mycoplana sp. MVMB2 Isolated from Contaminated SoilThe effect of nutrient and surfactant addition on the biodegradation of phenanthrene was studied in a batch scale soil-slurry system using isolated Mycoplana sp. MVMB2strain. The study was conducted using an artificially phenanthrene spiked and as well as contaminated soil from petrochemical industrial site. Maximum phenanthrene degradation and subsequent high microbial growth were observed at optimum pH (pH 6) and C/N/P ratio (100:20:3). To investigate maximum substrate degradation potential of Mycoplana sp. MVMB2, very high concentrations of phenanthrene (50-200 mg/kg soil) were used. The organism was capable of degrading >60% for a concentration below 20 mg/kg soil and >40% for concentrations up to 200 mg/kg within 8 days. Further the influence of five different surfactants namely Span 80, Tween 20, Triton X-100, cetyl trimethyl ammonium bromide, and sodium dodecyl sulfate were tested at their critical micelle concentration (CMC) levels for phenanthrene degradation in the soil. The addition of surfactant enhanced the biodegradation and a maximum of 84.49% was obtained for Triton X-100. Complete phenanthrene degradation by Mycoplana sp. MVMB2 was observed at 3 CMC concentration of Triton X-100. The optimized parameters obtained were used for the degradation of phenanthrene present in the contaminated soil and 98.6% biodegradation was obtained. Thus, the results obtained in the study suggested that biodegradation of phenanthrene by Mycoplana sp. MVMB2 appeared to be feasible to remediate phenanthrene rich contaminated sites.
This study presents the degradation of phenanthrene using immobilized Mycoplana sp. MVMB2 isolated from contaminated soil. Papaya stem pretreated by two stage processes, treating with acid or alkali and drying, was used for the immobilization of Mycoplana sp. Alkali pretreated papaya stem was found to be most effective in cell uptake compared to acid treated one. The maximum immobilization capacity at various physiochemical conditions for the alkali pretreated papaya stem was found to be at 320 min time, pH 6.5, 308C temperature, and 18.6 Â 10 6 cells/mL initial concentrations. The adsorption mechanism of Mycoplana sp. MVMB2 on pretreated papaya stem was assessed using various kinetic and isotherm models. The immobilization of Mycoplana sp. MVMB2 on to pretreated papaya stem was corroborated by scanning electron microscopy and Fourier transformed IR spectroscopy analysis. The performance of immobilized cells in batch reactor showed more than 95% phenanthrene degradation within 72 h, whereas, free cells were found to require 120 h. The immobilized cells also showed better degradation performance in the packed column study.Abbreviations: BCICP, bacterial cells immobilized C. papaya L.; HRT, hydraulic retention time; PDR, phenanthrene degradation rate; SEM, scanning electron microscopy 870
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