McKelvie Jennifer R, Mackay Douglas M, de Sieyes Nicholas R, Lacrampe-Couloume Georges, Sherwood Lollar Barbara
Department of Geology, University of Toronto, ON, Canada.
J Contam Hydrol. 2007 Dec 7;94(3-4):157-65. doi: 10.1016/j.jconhyd.2007.05.008. Epub 2007 Jun 12.
Compound-specific isotope analysis (CSIA) was used to assess biodegradation of MTBE and TBA during an ethanol release study at Vandenberg Air Force Base. Two continuous side-by-side field releases were conducted within a preexisting MTBE plume to form two lanes. The first involved the continuous injection of site groundwater amended with benzene, toluene and o-xylene ("No ethanol lane"), while the other involved the continuous injection of site groundwater amended with benzene, toluene and o-xylene and ethanol ("With ethanol lane"). The delta(13)C of MTBE for all wells in the "No ethanol lane" remained constant during the experiment with a mean value of -31.3 +/- 0.5 per thousand (n=40), suggesting the absence of any substantial MTBE biodegradation in this lane. In contrast, substantial enrichment in (13)C of MTBE by 40.6 per thousand, was measured in the "With ethanol lane", consistent with the effects of biodegradation. A substantial amount of TBA (up to 1200 microg/L) was produced by the biodegradation of MTBE in the "With ethanol lane". The mean value of delta(13)C for TBA in groundwater samples in the "With ethanol lane" was -26.0 +/- 1.0 per thousand (n=32). Uniform delta(13)C TBA values through space and time in this lane suggest that substantial anaerobic biodegradation of TBA did not occur during the experiment. Using the reported range in isotopic enrichment factors for MTBE of -9.2 per thousand to -15.6 per thousand, and values of delta(13)C of MTBE in groundwater samples, MTBE first-order biodegradation rates in the "With ethanol lane" were 12.0 to 20.3 year(-1) (n=18). The isotope-derived rate constants are in good agreement with the previously published rate constant of 16.8 year(-1) calculated using contaminant mass-discharge for the "With ethanol lane".
在范登堡空军基地进行的乙醇释放研究中,采用化合物特异性同位素分析(CSIA)来评估甲基叔丁基醚(MTBE)和叔丁醇(TBA)的生物降解情况。在一个现有的MTBE羽流范围内进行了两次并排的连续现场释放,形成两条通道。第一次是连续注入用苯、甲苯和邻二甲苯改性的场地地下水(“无乙醇通道”),而另一次是连续注入用苯、甲苯、邻二甲苯和乙醇改性的场地地下水(“有乙醇通道”)。在实验期间,“无乙醇通道”中所有井的MTBE的δ(13)C保持恒定,平均值为-31.3±0.5‰(n = 40),这表明该通道中没有任何显著的MTBE生物降解。相比之下,在“有乙醇通道”中测得MTBE的(13)C显著富集了40.6‰,这与生物降解的影响一致。在“有乙醇通道”中,MTBE的生物降解产生了大量的TBA(高达1200μg/L)。“有乙醇通道”中地下水样品中TBA的δ(13)C平均值为-26.0±1.0‰(n = 32)。该通道中TBA的δ(13)C值在空间和时间上保持一致,表明实验期间没有发生显著的TBA厌氧生物降解。利用报道的MTBE同位素富集因子范围为-9.2‰至-15.6‰,以及地下水样品中MTBE的δ(13)C值,“有乙醇通道”中MTBE的一级生物降解速率为12.0至20.3年^(-1)(n = 18)。同位素推导的速率常数与先前发表的使用“有乙醇通道”中污染物质量排放计算的16.8年^(-1)的速率常数高度一致。