Zero valent iron remediation of a mixed brominated ethene
contaminated groundwater
Elizabeth L. Cohen
a,b
, Bradley M. Patterson
a,
⁎, Allan J. McKinley
b
, Henning Prommer
a,c
a
CSIRO Land and Water, Private Bag No. 5, Wembley WA 6913, Australia
b
School of Biomedical, Biomolecular and Chemical Sciences, The University of Western Australia, 35 Stirling Highway, Crawley WA 6009, Australia
c
School of Earth and Geographical Sciences, The University of Western Australia, 35 Stirling Highway, Crawley WA 6009, Australia
article info abstract
Article history:
Received 1 July 2008
Received in revised form 15 September 2008
Accepted 19 September 2008
Available online 30 September 2008
The suitability of a granulated zero valent iron (ZVI) permeable reactive barrier (PRB) remediation
strategy was investigated for tribromoethene (TriBE), cis-1,2-dibromoethene (c-DBE), trans-1,2-
dibromoethene (t-DBE) and vinyl bromide (VB), via batch and large-scale column experiments that
were subsequently analysed by reactive transport modelling.
The brominated ethenes in both batch and large-scale column experiments showed rapid
(compared to controls and natural attenuation) degradation in the presence of ZVI. In the large-
scale column experiment, degradation half-lives were 0.35 days for TriBE, 0.50 days for c-DBE,
0.31 days for t-DBE and 0.40 days for VB, under site groundwater flow conditions, resulting in
removal of brominated ethenes within the first 0.2 m of a 1.0 m thick ZVI layer, indicating that a
PRB groundwater remediation strategy using ZVI could be used successfully.
In the model simulations of the ZVI induced brominated ethene degradation, assuming a dominant
reductive β-elimination pathway via bromoacetylene and acetylene production, simulated organic
compound concentrations corresponded well with both batch and large-scale column
experimental data. Changes of inorganic reactants were also well captured by the simulations.
The similar ZVI induced degradation pathway of TriBE and TCE suggests that outcomes from
research on ZVI induced TCE remediation could also be applied to TriBE remediation.
© 2008 Elsevier B.V. All rights reserved.
Keywords:
Groundwater
Tribromoethene
cis 1,2-dibromoethene
trans 1,2-dibromoethene
Vinyl bromide
1,1,2,2-tetrabromoethane
Permeable reactive barrier
Zero valent iron
PHT3D
1. Introduction
Although extensive research has been undertaken regard-
ing methods to remediate trichloroethene (TCE), the bromi-
nated analogue tribromoethene (TriBE) has been largely
ignored as a soil and groundwater contaminant and to date
very little information exists on potential remediation
strategies. This limited research is largely due to the small
number of cases of environmental contamination by bromi-
nated ethane and ethenes reported. Brominated ethane and
ethenes contamination has been reported at two ground-
water locations (Heitz et al., 1997; Thomas et al., 2004;
Patterson et al., 2007) and one terrestrial water location
(Grigoriadoua et al., 2008).
At one groundwater site, a 230 m long mixed
brominated ethene contaminant groundwater plume consist-
ing of TriBE, cis-1,2-dibromoethene (c-DBE), trans-1,2-dibro-
moethene (t-DBE) and vinyl bromide (VB) that is potentially
discharging into a creek, has been reported (Thomas et al.,
2004; Patterson et al., 2007). The length of the contaminant
plume was reported to be a combined result of the
brominated ethene's low retardation coefficients and limited
natural attenuation (Patterson et al., 2007). Laboratory and
site investigations have shown that the mixed brominated
ethene plume is a result of dissolution of the dense non-
aqueous phase liquid (DNAPL) 1,1,2,2-tetrabromoethane
(TBA) at the presumed source zone, which degraded rapidly
(half-life of 0.2 days) to form TriBE (Patterson et al., 2007).
TriBE has been shown to be toxic to algae, crustaceans and
fish (Canton and Wegman,1983). While there are currently no
World Health Organization (WHO) drinking water guidelines
for TriBE, limited studies (HSDB, 2004) on human toxicity have
Journal of Contaminant Hydrology 103 (2009) 109–118
⁎ Corresponding author. Tel.: +61 8 93336276; fax: +61 8 9333 6211.
E-mail address: bradley.patterson@csiro.au (B.M. Patterson).
0169-7722/$ – see front matter © 2008 Elsevier B.V. All rights reserved.
doi:10.1016/j.jconhyd.2008.09.010
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