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

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• 作者：Daniel Hunkeler^a ; ^{Daniel.Hunkeler@unine.ch} ; Yumiko Abe^a ; Mette M. Broholm^b ; Simon Jeannottat^a ; Claus Westergaard^c ; Carsten Suhr Jacobsen^e ; ^f ; Ramon Aravena^d ; Poul L. Bjerg^b
• 关键词：Groundwater ; Chlorinated ethenes ; Biodegradation ; Stable isotopes ; qPCR
• 刊名：Journal of Contaminant Hydrology
• 出版年：2011
• 出版时间：25 January 2011
• 年：2011
• 卷：119
• 期：1-4
• 页码：69-79
• 全文大小：1614 K

文摘

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 Dehaloccocoides sp. and vcrA genes. Redox conditions were characterized as well based on concentrations of dissolved redox sensitive compounds and sulfur isotopes in SO₄²⁻.

In the first 400 m downgradient of the source, the plume was confined to the upper 20 m 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, O₂ and NO₃⁻ decreased to below detection levels, while dissolved Fe²⁺ and SO₄²⁻ increased above detectable concentrations, likely due to pyrite oxidation as confirmed by the depleted sulfur isotope signature of SO₄²⁻. 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 ¹³C in the daughter products followed by an enrichment of ¹³C as degradation proceeded. At 1000 m downgradient of the source, cDCE was the dominant chlorinated ethene and had reached the source δ¹³C value confirming that cDCE was not affected by abiotic or biotic degradation.

Further downgradient (up to 1900 m), cDCE became enriched in ¹³C 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 Dehaloccocides sp genes, and strongly reducing conditions in this zone provide strong evidence for reductive dechlorination of cDCE. The significant enrichment of ¹³C 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.