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Assessing chlorinated ethene degradation in a large scale contaminant plume by dual carbon–chlorine isotope analysis and quantitative PCR

机译:通过碳-氯同位素双重分析和定量PCR评估大规模污染物羽流中的氯化乙烯降解

摘要

The fate of chlorinated ethenes in a large contaminant plume originating from a tetrachloroethene (PCE) source in a sandy aquifer in Denmark was investigated using novel methods including compound-specific carbon and chlorine isotope analysis and quantitative real-time polymerase chain reaction (qPCR) methods targeting sp. and A genes. Redox conditions were characterized as well based on concentrations of dissolved redox sensitive compounds and sulfur isotopes in SO ¯. In the first 400 m downgradient of the source, the plume was confined to the upper 20m of the aquifer. Further downgradient it widened in vertical direction due to diverging groundwater flow reaching a depth of up to 50 m. As the plume dipped downward and moved away from the source, O and NO¯ decreased to below detection levels, while dissolved Fe and SO¯ increased above detectable concentrations, likely due to pyrite oxidation as confirmed by the depleted sulfur isotope signature of SO¯. In the same zone, PCE and trichloroethene (TCE) disappeared and cis-1,2-dichloroethene (cDCE) became the dominant chlorinated ethene. PCE and TCE were likely transformed by reductive dechlorination rather than abiotic reduction by pyrite as indicated by the formation of cDCE and stable carbon isotope data. TCE and cDCE showed carbon isotope trends typical for reductive dechlorination with an initial depletion of C in the daughter products followed by an enrichment of C as degradation proceeded. At 1000 m downgradient of the source, cDCE was the dominant chlorinated ethene and had reached the source δC value confirming that cDCE was not affected by abiotic or biotic degradation. Further downgradient (up to 1900 m), cDCE became enriched in C by up to 8‰ demonstrating its further transformation while vinylchloride (VC) concentrations remained low (<1 µg/L) and ethene was not observed. The correlated shift of carbon and chlorine isotope ratios of cDCE by 8 and 3.9‰, respectively, the detection of sp genes, and strongly reducing conditions in this zone provide strong evidence for reductive dechlorination of cDCE. The significant enrichment of C in VC indicates that VC was transformed further, although the mechanism could not be determined. The transformation of cDCE was the rate limiting step as no accumulation of VC occurred. In summary, the study demonstrates that carbon–chlorine isotope analysis and qPCR combined with traditional approaches can be used to gain detailed insight into the processes that control the fate of chlorinated ethenes in large scale plumes.
机译:使用包括化合物特异性碳和氯同位素分析以及定量实时聚合酶链反应(qPCR)方法在内的新方法,研究了丹麦含沙含水层中源自四氯乙烯(PCE)的大量污染物羽流中的氯化乙烯的去向。定位sp。和A基因。还根据SO中溶解的氧化还原敏感化合物和硫同位素的浓度来表征氧化还原条件。在水源下降的前400 m,羽流被限制在含水层的上部20 m。由于地下水流的扩散达到了50 m的深度,它在垂直方向上进一步降级。当烟羽向下浸入并远离源时,O和NO'降至检测水平以下,而溶解的Fe和SO'增加至可检测浓度以上,这很可能是由于黄铁矿氧化所致,如SO'的硫同位素特征减弱所证实的。在同一区域中,PCE和三氯乙烯(TCE)消失了,顺式1,2-二氯乙烯(cDCE)成为了主要的氯化乙烯。如cDCE的形成和稳定的碳同位素数据所示,PCE和TCE可能通过还原性脱氯而不是通过黄铁矿非生物还原而转化。 TCE和cDCE显示出还原性脱氯中典型的碳同位素趋势,其子产物中的C最初耗尽,然后随着降解的进行而富集C。在源下降1000 m时,cDCE是占主导地位的氯化乙烯,并且已达到源δC值,这证实cDCE不受非生物或生物降解的影响。进一步降级(高达1900 m),cDCE的碳富集度高达8‰,这表明其进一步转化,而氯乙烯(VC)的浓度仍然很低(<1 µg / L),没有观察到乙烯。 cDCE的碳和氯同位素比率的相关位移分别为8和3.9‰,sp基因的检测以及该区域的强烈还原条件为cDCE的还原脱氯提供了有力的证据。 VC中C的显着富集表明VC进一步转化了,尽管无法确定其机理。 cDCE的转化是限速步骤,因为没有VC积累。总之,该研究表明,碳-氯同位素分析和qPCR与传统方法相结合可用于深入了解控制大规模羽状流中氯化乙烯命运的过程。

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