Biodegradation kinetics of trichloroethylene and 1,2-dichloroethane by Burkholderia (Pseudomonas) cepacia PR1 sub(31) and Xanthobacter autotrophicus GJ10
The biodegradation kinetics for chlorinated aliphatic hydrocarbons trichloroethylene (TCE) by Burkholderia (Pseudomonas) cepacia PR1 sub(31) and for 1,2-dichloethane (1,2-DCA) by Xanthobacter autotrophicus GJ10 were determined using an initial rate method to determine the applicable rate law and rel...
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Veröffentlicht in: | International biodeterioration & biodegradation 1999-03, Vol.43 (1-2), p.57-61 |
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Format: | Artikel |
Sprache: | eng |
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Zusammenfassung: | The biodegradation kinetics for chlorinated aliphatic hydrocarbons trichloroethylene (TCE) by Burkholderia (Pseudomonas) cepacia PR1 sub(31) and for 1,2-dichloethane (1,2-DCA) by Xanthobacter autotrophicus GJ10 were determined using an initial rate method to determine the applicable rate law and relevant kinetic parameters under aerobic conditions. A first order linear rate law applied to 1,2-DCA biodegradation by X. autotrophicus GJ10. The first order rate constant was determined to be 0.014 ml/min/mg. A non-linear rate law applied to TCE biodegradation by B. cepacia PR1 sub(31). The maximum specific degradation rate constant was determined to be 0.8 nmol/min/mg protein, and the half saturation constant was determined to be 0.026 mM (3.47 ppm). Error analysis performed on our analytical methods and computations, using a logarithmic differentiation method, indicated the relative error of our reported rate constants to be approximately 17%. Knowledge of the kinetic rate laws and kinetic parameters governing the biodegradation of TCE and 1,2-DCA by these strains will further the application of these strains in the environmental field and in waste treatment applications. |
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ISSN: | 0964-8305 |
DOI: | 10.1016/S0964-8305(98)00069-9 |