2006
DOI: 10.1061/(asce)0733-9372(2006)132:2(199)
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Field Monitoring of a Permeable Reactive Barrier for Removal of Chlorinated Organics

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Cited by 77 publications
(32 citation statements)
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“…It appears from the overview of treatable contaminants that Fe 0 might be regarded as a technology with the potential to manage all classes of contaminants (inorganic ions, organic poisons, and harmful germs). This impression is supported by articles which reported on quantitative removal of species (e.g., 1,2-dichloroethane, dichloromethane, methylene blue, triazoles) which were proven to be not reducible by Fe 0 [83][84][85]. The performance of Fe 0 materials for water treatment has been adapted in recent years via multiple different methodologies, for a wide range of applications, including: (i) decreasing the particle size to nano-scale in order to enhance the reactivity of the material as a function of mass [86]; (ii) embedding noble bimetallic particles into the Fe 0 structure in order to improve the galvanic properties of the material [87]; (iii) embedding Fe 0 into appropriate porous support materials [14,48]; and (iv) embedding Fe 0 with complimentary adsorbent materials [88][89][90].…”
Section: /H2o System For Contaminant Mitigationsupporting
confidence: 59%
See 1 more Smart Citation
“…It appears from the overview of treatable contaminants that Fe 0 might be regarded as a technology with the potential to manage all classes of contaminants (inorganic ions, organic poisons, and harmful germs). This impression is supported by articles which reported on quantitative removal of species (e.g., 1,2-dichloroethane, dichloromethane, methylene blue, triazoles) which were proven to be not reducible by Fe 0 [83][84][85]. The performance of Fe 0 materials for water treatment has been adapted in recent years via multiple different methodologies, for a wide range of applications, including: (i) decreasing the particle size to nano-scale in order to enhance the reactivity of the material as a function of mass [86]; (ii) embedding noble bimetallic particles into the Fe 0 structure in order to improve the galvanic properties of the material [87]; (iii) embedding Fe 0 into appropriate porous support materials [14,48]; and (iv) embedding Fe 0 with complimentary adsorbent materials [88][89][90].…”
Section: /H2o System For Contaminant Mitigationsupporting
confidence: 59%
“…The two examples in Section 4.3 and the parameters in Tables 1 and 2 PRBs [83,141] have not been satisfactorily rationalized [122,123]. It is evident that the composition of contaminated waters and effluents vary to a large extent.…”
Section: Discussionmentioning
confidence: 99%
“…For example, several investigators documented reduced concentrations of heavy metals in groundwater flowing through permeable reactive barriers [7][8][9][10][11][12]. Others reported decreased concentrations of petroleum hydrocarbons [13][14][15] and chlorinated solvents [7,8,10,13,16,17] at field sites equipped with reactive barriers. Moreover, Robertson et al [18] reported a successful application of reactive barrier technology for nutrients in groundwater.…”
Section: Introductionmentioning
confidence: 99%
“…Wadley et al (2005) suggested mixing iron and bentonite into aquifer contaminated by free-phase PCE and TCE was an effective means of source zone remediation in both laboratory and field tests, as bentonite can prevent potential mobilization of free-phase chlorinated solvent. Lai et al 2006 demonstrated a PRB with zero-valent iron to remove chlorinated aliphatic hydrocarbons, which was installed at the Vapokon site, Denmark, and achieved about 92.4-97.5% removal after 4 years. Borden (2007) injected an emulsified oil substrate into a phreatic aquifer to form a 15-m-long biologically active permeable reactive barrier to treat groundwater contaminated by chlorinated solvents and perchlorate in a pilot test.…”
Section: Introductionmentioning
confidence: 99%