Surface charge and growth of sulphate and carbonate green rust in aqueous media

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Abstract

We report the first determination of the point of zero charge of sulphated and carbonated green rust particles. Green rust has been recognised as a prevalent mineral in environments such as hydromorphic soils, groundwaters and anoxic Fe(II)-rich water bodies, and the evolution of its net surface charge with pH has direct implications for the uptake of contaminants, metals and nutrients in such settings. We find that the surface of both sulphated and carbonated green rust is positively charged at pH < 8.3, whereas it is negatively charged at pH > 8.3. Thus, alkaline settings will promote enhanced adsorption of metallic cations. However, the behaviour of ionic species surrounding green rust is more complicated than that predicted by simple pH-dependent adsorption, as our experiments suggest that green rust likely grows via dissolution-reprecipitation during Ostwald-ripening. This implies that adsorbed species are potentially subject to repetitive steps of release into solution, re-adsorption and co-precipitation during particle growth. The growth rate of green rust particles is highest within the first 50. min of aging, and appears to decrease towards an asymptote after 200. min, suggesting that particle growth controls on the uptake of dissolved species will be most important during the early steps of green rust growth. Our findings thus contribute to a better understanding of the controls that green rust may exert on dissolved ions in a variety of anoxic environments. © 2013 Elsevier Ltd.

Figures

  • Fig. 1. Typical XRD spectra of freshly precipitated and glycerol-coated GRSO4 (Fig. 1A) and GRCO3 (Fig. 1B). Open circles represent the scan of the same glycerol-coated sample re-analysed after 22 h outside the anoxic cabinet. The similarity of the scans highlights the efficiency of glycerol to prevent oxidation.
  • Fig. 2. Evolution of pH versus the relative amount of titrant added during the formation of sulphated green rust. Light grey circles represent the experimental data obtained starting with x = 0.33. Darker circles were obtained starting with x = 0.35. Our data are in good agreements with previous work (light grey curve). The two red crosses indicate the points where the reaction was sub-sampled and the solid products analysed by TEM. At pH 6.5, solid products consist of a mixture of green rust hexagons and lepidocrocite/goethite spikes. At pH 10.2, green rust hexagons have partially transformed to darker magnetite crystals.
  • Fig. 4. Total dissolved [Fe(aq)T] plotted against pH for both green rust species. The dependence of log Fe(aq)T upon pH is supported by the coefficient of determination (R2 = 0.91) on the regression line.
  • Fig. 3. Evolution of pH versus the relative amount of titrant added during the formation of carbonated green rust (Fig. 3A) using different titrant solutions. During the titration, GRSO4 is the first green rust species to form as indicated by the red spectrum (Fig. 3B, pH 7). Anion substitution, i.e. GRSO4 to GRCO3 conversion, starts when [CO3 2 ] > [SO4 2 ].
  • Fig. 5. Charge balanceQ (in mol g 1) calculated from the proton titrations performed in various electrolytes for GRSO4 (A) and GRCO3 (B). Circles are the data obtained from traditional titrations using Eq. (5) on pre-weighed solid (black circles) or in situ precipitated minerals (grey and open circles). Open triangles were obtained from our developed protocol using Eq. (6). The point of zero charge is given by the common intersection point of the curves.
  • Table 1 XRD crystal peak parameters and associated sizes (calculated from Eq.
  • Table 2 Crystallographic and complexation parameters used for the surface complex modelling.
  • Fig. 6. XRD spectra showing an increase in crystallinity (increase in peak height and decrease in peak broadening) during the first 250 min of GRCO3 ageing (A). Long term ageing (>4 h) leads to the conversion of GR to magnetite, as exemplified for GRSO4 by the decrease of GR peaks and the appearance of magnetite peaks (B).

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CITATION STYLE

APA

Guilbaud, R., White, M. L., & Poulton, S. W. (2013). Surface charge and growth of sulphate and carbonate green rust in aqueous media. Geochimica et Cosmochimica Acta, 108, 141–153. https://doi.org/10.1016/j.gca.2013.01.017

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