Kuder Tomasz, Wilson John T, Kaiser Phil, Kolhatkar Ravi, Philp Paul, Allen Jon
University of Oklahoma, Norman, Oklahoma 73019, USA.
Environ Sci Technol. 2005 Jan 1;39(1):213-20. doi: 10.1021/es040420e.
The conventional approach to evaluate biodegradation of organic contaminants in groundwater is to demonstrate an increase in the concentration of transformation products. This approach is problematic for MTBE from gasoline spills because the primary transformation product (TBA) can also be a component of gasoline. Compound-specific stable isotope analysis may provide a useful alternative to conventional practice. Changes in the delta13C and deltaD of MTBE during biodegradation of MTBE in an anaerobic enrichment culture were compared to the delta13C and deltaD of MTBE in groundwater at nine gasoline spill-sites. The stable isotopes of hydrogen and carbon were extensively fractionated during anaerobic biodegradation of MTBE. The stable isotope enrichment factor for carbon (epsilonC) in the enrichment cultures was -13 (-14.1 to -11.9 at 95% confidence level), and the hydrogen enrichment factor (epsilonH) was -16 (-21 to -11 at 95% confidence level). The isotope enrichment factors for carbon and hydrogen during anaerobic biodegradation indicate that the first reaction is enzymatic hydrolysis of the O-Cmethyl bond. The ratio of epsilonH to epsilonC was consistent between the enrichment culture and the field site that provided the inoculum, and with the other eight sites, suggesting a common degradation pathway. Compound-specific isotope evidence is discussed in terms of its utility for monitoring in situ biodegradation, in particular, for measuring how much MTBE was degraded. For the studied field sites, significant biodegradation of the original mass of MTBE is suggested, in some cases exceeding 90%.
评估地下水中有机污染物生物降解的传统方法是证明转化产物的浓度有所增加。对于汽油泄漏产生的甲基叔丁基醚(MTBE)而言,这种方法存在问题,因为主要转化产物(叔丁醇,TBA)也可能是汽油的成分之一。化合物特异性稳定同位素分析可能为传统方法提供一种有用的替代方法。将厌氧富集培养中MTBE生物降解过程中MTBE的δ13C和δD变化,与9个汽油泄漏场地地下水中MTBE的δ13C和δD进行了比较。在MTBE的厌氧生物降解过程中,氢和碳的稳定同位素发生了广泛的分馏。富集培养中碳的稳定同位素富集因子(εC)为-13(95%置信水平下为-14.1至-11.9),氢富集因子(εH)为-16(95%置信水平下为-21至-11)。厌氧生物降解过程中碳和氢的同位素富集因子表明,第一步反应是O-C甲基键的酶促水解。富集培养与提供接种物的现场以及其他8个场地之间,εH与εC的比值是一致的,这表明存在共同的降解途径。本文讨论了化合物特异性同位素证据在监测原位生物降解,特别是在测量MTBE降解量方面的实用性。对于所研究的现场场地,表明MTBE原始质量发生了显著的生物降解,在某些情况下超过了90%。