Hunkeler Daniel, Aravena Ramon, Berry-Spark Karen, Cox Evan
Centre for Hydrogeology, University of Neuchâtel, Switzerland.
Environ Sci Technol. 2005 Aug 15;39(16):5975-81. doi: 10.1021/es048464a.
The demonstration of monitored natural attenuation (MNA) of chlorinated hydrocarbons in groundwater is typically conducted through the evaluation of concentration trends and parent-daughter product relationships along prevailing groundwater flow paths. Unfortunately, at sites contaminated by mixtures of chlorinated ethenes, ethanes, and methanes, the evaluation of MNA by using solely concentration data and parent-daughter relationships can result in erroneous conclusions regarding the degradation mechanisms that are truly active at the site, since many of the daughter products can be derived from multiple parent compounds. Stable carbon isotope analysis was used, in conjunction with concentration data, to clarify and confirm the active degradation pathways at a former waste solvent disposal site where at least 14 different chlorinated hydrocarbons have been detected in the groundwater. The isotope data indicate that TCE, initially believed to be present as a disposed product and/or a PCE dechlorination intermediate, is attributable to dehydrochlorination of 1,1,2,2-PCA. The isotope data further support that vinyl chloride and ethene in the site groundwater result from dichloroelimination of 1,1,2-trichlorethane and 1,2-dichloroethane, respectively, rather than from reductive dechlorination of the chlorinated ethenes PCE, TCE, or 1,2-DCE. The isotope data confirm that the chlorinated ethanes and chlorinated methanes are undergoing significant intrinsic degradation, whereas degradation of the chlorinated ethenes may be limited. In addition to the classical trend of enriched isotope values of the parent compounds with increasing distance associated to biodegradation, shifts of isotope ratios of degradation byproduct in the opposite direction due to mixing of isotopically light byproducts of biodegradation with compounds from the source are shown to be of high diagnostic value. These data underline the value of stable isotope analysis in confirming transformation processes at sites with complex mixtures of chlorinated compounds.
地下水中氯代烃的监测自然衰减(MNA)通常通过评估沿主要地下水流路径的浓度趋势和母-子产物关系来进行。不幸的是,在受氯代乙烯、乙烷和甲烷混合物污染的场地,仅使用浓度数据和母-子关系来评估MNA可能会导致关于该场地真正活跃的降解机制得出错误结论,因为许多子产物可能来自多种母化合物。在一个曾用作废溶剂处置场地的地方,地下水中至少检测到14种不同的氯代烃,利用稳定碳同位素分析并结合浓度数据,以阐明和确认活跃的降解途径。同位素数据表明,最初被认为是作为处置产物和/或PCE脱氯中间体存在的TCE,可归因于1,1,2,2-PCA的脱氯化氢反应。同位素数据进一步支持,场地地下水中的氯乙烯和乙烯分别是由1,1,2-三氯乙烷和1,2-二氯乙烷的二氯消除反应产生的,而不是来自氯代乙烯PCE、TCE或1,2-DCE的还原脱氯反应。同位素数据证实氯代乙烷和氯代甲烷正在经历显著的自然降解,而氯代乙烯的降解可能有限。除了母化合物的同位素值随与生物降解相关距离增加而富集的经典趋势外,由于生物降解的同位素轻质副产物与来自源的化合物混合,降解副产物的同位素比值向相反方向的变化显示出具有很高的诊断价值。这些数据强调了稳定同位素分析在确认含有复杂氯代化合物混合物场地的转化过程中的价值。