4.7 Article

An X-ray absorption spectroscopic study of the Fe(II)-induced transformation of Cr(VI)-substituted schwertmannite

Journal

JOURNAL OF HAZARDOUS MATERIALS
Volume 431, Issue -, Pages -

Publisher

ELSEVIER
DOI: 10.1016/j.jhazmat.2022.128580

Keywords

Chromium(VI); EXAFS spectroscopy; Iron oxides; Schwertmannite; Redox transformation; Mineralogy

Funding

  1. Australian Research Council [FT200100449]
  2. Environmental Analysis Laboratory (EAL)
  3. Australian Research Council [FT200100449] Funding Source: Australian Research Council

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In this study, the Fe(II)-induced transformation of Cr(VI)-substituted schwertmannite was investigated as a function of pH and the degree of Cr(VI) substitution. The results show that higher levels of Cr(VI) substitution inhibit the transformation, partly due to the consumption of Fe(II) by reaction with Cr(VI). This study enriches our understanding of the interactions between hazardous Cr(VI) and schwertmannite in environmental and engineered systems.
The environmental chemistry of Cr is of widespread interest due to the hazardous nature of Cr(VI). Because of similar atomic size and charge, CrVIO42- can substitute for SO42- within schwertmannite -an Fe(III) oxy-hydroxysulfate mineral that occurs widely in acidic and sulfate-rich systems. The presence of aqueous Fe(II) can induce transformation of schwertmannite to more stable Fe(III) phases (e.g. goethite) which may potentially impact the behaviour of co-associated Cr(VI). Here, we investigate the Fe(II)-induced transformation of Cr(VI)-substituted schwertmannite as a function of pH (4-8) and the degree of Cr(VI) substitution (0.16-13 mol% CrVIO42--for-SO(4)(2-)substitution). Iron K-edge EXAFS spectroscopy revealed that higher levels of Cr(VI) substitu-tion inhibited Fe(II)-induced schwertmannite transformation. Chromium K-edge XANES spectroscopy indicated that this outcome could be partly attributed to consumption of Fe(II) by reaction with Cr(VI), and the resulting formation of a passivating Cr(III)-Fe(III) hydroxide phase which stabilizes schwertmannite at greater levels of Cr (VI) substitution and at higher pH while also decreasing further reduction of structural Cr(VI). Overall, this study enriches our understanding of interactions between hazardous Cr(VI) and schwertmannite in environmental and engineered systems.

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