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Kinetics of 1,4-dioxane biodegradation by monooxygenase-expressing bacteria

机译:单加氧酶表达细菌对1,4-二恶烷的生物降解动力学

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1,4-Dioxane is a probable human carcinogen, and an important emerging water contaminant. In this study, the biodegradation of dioxane by 20 bacterial isolates was evaluated, and 13 were found to be capable of transforming dioxane. Dioxane served as a growth substrate for Pseudonocardia dioxanivorans CB1190 and Pseudonocardia benzenivorans B5, with yields of 0.09 g protein g dioxane(-1) and 0.03 g protein g dioxane(-1), respectively. Cometabolic transformation of dioxane was observed for monooxygenase-expressing strains that were induced with methane, propane, tetrahydrofuran, or toluene including Methylosinus trichosporium OB3b, Mycobacterium vaccae JOB5, Pseudonocardia K1, Pseudomonas mendocina KR1, Ralstonia pickettii PKO1, Burkholderia cepacia G4, and Rhodococcus RR1. Product toxicity resulted in incomplete dioxane degradation for many of the cometabolic reactions. Brief exposure to acetylene, a known monooxygenase inhibitor, prevented oxidation of dioxane in all cases, supporting the hypothesis that monooxygenase enzymes participated in the transformation of dioxane by these strains. Further, Escherichia coli TG1/pBS(Kan) containing recombinant plasmids derived from the toluene-2- and toluene-4-monooxygenases of G4, KR1 and PKO1 were also capable of cometabolic dioxane transformation. Dioxane oxidation rates measured at 50 mg/L ranged from 0.01 to 0.19 mg hr(-1) mg protein(-1) for the metabolic processes, 0.1-0.38 mg hr(-1) mg protein(-1) for cometabolism by the monooxygenase-induced strains, and 0.17-0.60 mg hr(-1) mg protein(-1) for the recombinant strains. Dioxane was not degraded by M. trichosporium OB3b expressing particulate methane monooxygenase, Pseudomonas putida mt-2 expressing a toluene side-chain monooxygenase, and Pseudomonas JS150 and Pseudomonas putida F1 expressing toluene-2,3-dioxygenases. This is the first study to definitively show the role of monooxygenases in dioxane degradation using several independent lines of evidence and to describe the kinetics of metabolic and cometabolic dioxane degradation.
机译:1,4-二恶烷可能是人类致癌物,并且是重要的新兴水污染物。在这项研究中,评估了20种细菌分离物对二恶烷的生物降解,发现13种能够转化二恶烷。二恶烷用作假单胞假二恶心菌CB1190和苯丙酸假单胞菌B5的生长底物,产量分别为0.09 g蛋白质g二恶烷(-1)和0.03 g蛋白质g二恶烷(-1)。对于由甲烷,丙烷,四氢呋喃或甲苯诱导的表达单加氧酶的菌株,包括三甲基毛孢菌OB3b,vaccoe vaccae JOB5,假拟心菌K1,Pseudomonas mendocina KR1,Ralstonia Pickettii PKO, 。产品毒性导致许多新陈代谢反应的二恶烷降解不完全。短暂暴露于已知的单加氧酶抑制剂乙炔可在所有情况下防止二恶烷氧化,从而支持了单加氧酶参与这些菌株转化二恶烷的假设。此外,含有来自G4的甲苯-2-和甲苯-4-单加氧酶,KR1和PKO1的重组质粒的大肠杆菌TG1 / pBS(Kan)也能够进行新陈代谢二氧六环转化。在代谢过程中,以50 mg / L测得的二恶烷氧化速率范围为0.01至0.19 mg hr(-1)mg蛋白质(-1),对于代谢过程为0.1-0.38 mg hr(-1)mg蛋白质(-1)。单加氧酶诱导的菌株和重组菌株0.17-0.60 mg hr(-1)mg蛋白(-1)。表达颗粒状甲烷单加氧酶的毛孢霉OB3b,表达甲苯侧链单加氧酶的恶臭假单胞菌mt-2和表达甲苯-2,3-二加氧酶的假单胞菌JS150和恶臭假单胞菌F1不会降解二恶烷。这是第一项使用几种独立的证据明确显示单加氧酶在二恶烷降解中的作用并描述代谢和可代谢二恶烷降解动力学的研究。

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