AI Article Synopsis

  • - In laboratory studies, sulfidated nanoscale zero-valent iron (S-nZVI) demonstrated enhanced effectiveness for removing toxic chromium (Cr(VI)) from contaminated water, showcasing better reactivity and electron selectivity.
  • - Field applications involved injecting S-nZVI particles into a chromium-contaminated aquifer, resulting in a significant reduction of Cr(VI) and chromium concentrations, as well as improved groundwater quality over a considerable distance from the injection site.
  • - Analysis of samples from the aquifer confirmed that the iron particles transformed chromium into a less harmful form (Cr(III)) and maintained effectiveness over time, indicating that S-nZVI is a viable method for cleaning up contaminated groundwater.

Article Abstract

In a number of laboratory studies, sulfidated nanoscale zero-valent iron (S-nZVI) particles showed increased reactivity, reducing capacity, and electron selectivity for Cr(VI) removal from contaminated waters. In our study, core-shell S-nZVI particles were successfully injected into an aquifer contaminated with Cr(VI) at a former chrome plating facility. S-nZVI migrated towards monitoring wells, resulting in a rapid decrease in Cr(VI) and Cr concentrations and a long-term decrease in groundwater redox potential observed even 35 m downstream the nearest injection well. Characterization of materials recovered from the injection and monitoring wells confirmed the presence of nZVI particles, together with iron corrosion products. Chromium was identified on the surface of the recovered iron particles as Cr(III), and its occurrence was linked to the formation of insoluble chromium-iron (oxyhydr)oxides such as CrFe(OH). Injected S-nZVI particles formed aggregates, which were slowly transformed into iron (oxyhydr)oxides and carbonate green rust. Elevated contents of Fe were detected even several months after injection, indicating good S-nZVI longevity. The sulfide shell was gradually disintegrated and/or dissolved. Geochemical modelling confirmed the overall stability of the resulting Cr(III) phase at field conditions. This study demonstrates the applicability of S-nZVI for the remediation of a Cr(VI)-contaminated aquifer.

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Source
http://dx.doi.org/10.1016/j.jhazmat.2020.124665DOI Listing

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