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
Hauptverfasser: Inguva, S, Shreve, G S
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.
ISSN:0964-8305
DOI:10.1016/S0964-8305(98)00069-9