McKelvie Jennifer R, Hyman Michael R, Elsner Martin, Smith Christy, Aslett Denise M, Lacrampe-Couloume Georges, Lollar Barbara Sherwood
Stable Isotope Laboratory, University of Toronto, Toronto, Ontario, Canada.
Environ Sci Technol. 2009 Apr 15;43(8):2793-9. doi: 10.1021/es803307y.
Carbon isotopic enrichment factors (epsilonC) measured during cometabolic biodegradation of methyl tert-butyl ether (MTBE), ethyl tert-butyl ether (ETBE), and tert-amyl methyl ether (TAME) by Pseudonocardia tetrahydrofuranoxydans strain K1 were -2.3 +/- 0.2 per thousand, -1.7 +/- 0.2 per thousand, and -1.7 +/- 0.3 per thousand, respectively. The measured carbon apparent kinetic isotope effect was 1.01 for all compounds, consistent with the expected kinetic isotope effects for both oxidation of the methoxy (or ethoxy) group and enzymatic SN1 biodegradation mechanisms. Significantly, delta13C measurements of the tert-butyl alcohol and tert-amyl alcohol products indicated that the tert-butyl and tert-amyl groups do not participate in the reaction and confirmed that ether biodegradation by strain K1 involves oxidation of the methoxy (or ethoxy) group. Measured hydrogen isotopic enrichment factors (epsilonH) were -100 +/- 10 per thousand, -73 +/- 7 per thousand, and -72 +/- 20 per thousand for MTBE, ETBE, and TAME respectively. Previous results reported for aerobic biodegradation of MTBE by Methylibium petroleiphilum PM1 and Methylibium R8 showed smaller epsilonH values (-35 per thousand and -42 per thousand, respectively). Plots of Delta2H/Delta13C show different slopes for strain K1 compared with strains PM1 and R8, suggesting that different mechanisms are utilized by K1 and PM1/R8 during aerobic MTBE biodegradation.
在四氢呋喃氧化假诺卡氏菌K1菌株对甲基叔丁基醚(MTBE)、乙基叔丁基醚(ETBE)和叔戊基甲基醚(TAME)进行共代谢生物降解过程中测得的碳同位素富集因子(εC)分别为-2.3±0.2‰、-1.7±0.2‰和-1.7±0.3‰。对所有化合物测得的碳表观动力学同位素效应均为1.01,这与甲氧基(或乙氧基)氧化及酶促SN1生物降解机制预期的动力学同位素效应一致。重要的是,对叔丁醇和叔戊醇产物的δ13C测量表明,叔丁基和叔戊基不参与反应,并证实菌株K1对醚的生物降解涉及甲氧基(或乙氧基)的氧化。MTBE、ETBE和TAME测得的氢同位素富集因子(εH)分别为-100±10‰、-73±7‰和-72±20‰。先前报道的石油甲基杆菌PM1和石油甲基杆菌R8对MTBE进行好氧生物降解的结果显示εH值较小(分别为-35‰和-42‰)。Δ2H/Δ13C图显示,与PM1和R8菌株相比,K1菌株具有不同的斜率,这表明在好氧MTBE生物降解过程中,K1与PM1/R8利用了不同的机制。