TY - JOUR
T1 - Assessing chlorinated ethene degradation in a large scale contaminant plume by dual carbon–chlorine isotope analysis and quantitative PCR
AU - Hunkeler, D.
AU - Abe, Y.
AU - Broholm, Mette Martina
AU - Jeannottat, S.
AU - Westergaard, C.
AU - Jacobsen, C.S.
AU - Aravena, R.
AU - Bjerg, Poul Løgstrup
PY - 2011
Y1 - 2011
N2 - 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 SO4 2−.
In the first 400 m downgradient of the source, the plume was confined to the upper 20m of the
aquifer. Further downgradient itwidened in vertical direction due to diverging groundwater flow
reaching a depth of up to 50 m. As the plume dipped downward andmoved away fromthe source,
O2 and NO3
− decreased to below detection levels, while dissolved Fe2+ and SO4 2− increased above
detectable concentrations, likely due to pyrite oxidation as confirmed by the depleted sulfur
isotope signature of SO4 2−. 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 (b1 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
mechanismcould not be determined. The transformation of cDCEwas the rate limiting step as no
accumulation of VC occurred. In summary, the study demonstrates that carbon–chlorine isotope
analysis and qPCR combinedwith traditional approaches can be used to gain detailed insight into
the processes that control the fate of chlorinated ethenes in large scale plumes.
AB - 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 SO4 2−.
In the first 400 m downgradient of the source, the plume was confined to the upper 20m of the
aquifer. Further downgradient itwidened in vertical direction due to diverging groundwater flow
reaching a depth of up to 50 m. As the plume dipped downward andmoved away fromthe source,
O2 and NO3
− decreased to below detection levels, while dissolved Fe2+ and SO4 2− increased above
detectable concentrations, likely due to pyrite oxidation as confirmed by the depleted sulfur
isotope signature of SO4 2−. 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 (b1 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
mechanismcould not be determined. The transformation of cDCEwas the rate limiting step as no
accumulation of VC occurred. In summary, the study demonstrates that carbon–chlorine isotope
analysis and qPCR combinedwith traditional approaches can be used to gain detailed insight into
the processes that control the fate of chlorinated ethenes in large scale plumes.
U2 - 10.1016/j.jconhyd.2010.09.009
DO - 10.1016/j.jconhyd.2010.09.009
M3 - Journal article
C2 - 21030108
SN - 0169-7722
VL - 119
SP - 69
EP - 79
JO - Journal of Contaminant Hydrology
JF - Journal of Contaminant Hydrology
ER -