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Zerovalent iron

Term denoting metallic iron, Fe(0), used for permeable reactive barrier in site remediation From Wikipedia, the free encyclopedia

Zerovalent iron
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Zerovalent iron (ZVI) is jargon[clarification needed] that describes forms of iron metal that are proposed for use in groundwater remediation.[1][2][3][4]

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Model A
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Model B
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Venn diagram showing the overlap between ZVIs and PRBs

ZVI operates by electron transfer from Fe0 toward some organochlorine compounds, a common class of pollutants. The remediation process is proposed to generate Fe2+ and Cl and halide-free organic products, all of which are relatively innocuous.[5] Nanoscale ZVIs (nZVIs) are commonly used in remediation of chlorinated compounds and other pollutants.[6]

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Type of ZVI

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  • Bulk Fe. Cast iron, consisting of scrap iron of construction grade, has been used as a reactive material for permeable reactive barriers (PRB) for groundwater remediation. Reactions are generally believed to occur on the Fe (oxide) surface; however, graphite inclusions can also serve as reaction sites.[7]
  • Nanoscale Fe. In addition to using macroscale iron in PRBs, nanoparticles (1-100 nm diameter) of zerovalent iron (nZVI) are effective.[2]
  • Zn. Zinc has shown much higher reactivity toward pentachlorophenol than iron. This indicates that zinc may be used as a replacement for ZVI in dechlorinating chlorinated phenols. Chlorinated phenols are sequentially dechlorinated and thus less-chlorinated phenols have been identified as a reduction product.[8]
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Type of contaminants treated

Treatment of many kinds of pollutants has been proposed, but few have been demonstrated in solving environmental challenges.

  • Cadmium (Cd2+) is converted to immobile Cd metal.[9]
  • Chloramines are effectively reduced by ZVI.[10]
  • Nitrate reduction by iron powder is observed at pH ≤ 4.[11] Ammonia is the end product. Using nanoscale iron, Nitrogen gas (N2) is the product.[12]
  • Nitrated aromatics are reduced by bulk iron.[7][13][14]
  • Chlorinated pesticides such as DDT, DDD, and DDE. The rates of dechlorination are enhanced by the surfactant Triton X-114.[15]
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Further reading

  • Tratnyek, P. G.; M. M. Scherer; T. J. Johnson; Matheson, L.J. (2003). Permeable reactive barriers of iron and other zerovalent metals. In: Tarr M. A. (ed.), Chemical Degradation Methods for Wastes and Pollutants; Environmental and Industrial Applications. Environmental Science and Pollution Control, Marcel Dekker, New York, pp 371–421. doi:10.1201/9780203912553.ch9

Notes

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