Abstract In this work, the stability of arsenate adsorbed Mg(II)–Al(III)/Fe(III)–CO3/SO4 Layered Double Hydroxides (LDHs) under three abiotic anoxic reductive conditions that may be encountered in Tailings Management Facilities (TMFs) were… Click to show full abstract
Abstract In this work, the stability of arsenate adsorbed Mg(II)–Al(III)/Fe(III)–CO3/SO4 Layered Double Hydroxides (LDHs) under three abiotic anoxic reductive conditions that may be encountered in Tailings Management Facilities (TMFs) were evaluated. At pH 8 and 10 mM Fe(II) (aq), the formation of Fe(III)-oxy/hydroxides (FeOHs) occurred for all 5 LDHs but the Fe-based LDHs precipitated the greatest amounts. All LDHs released MgAlFeCO3SO4 > MgAlCO3 > MgFeCO3/MgFeSO4. The solid surfaces remained as As(V) except for MgAlSO4, MgAlCO3, and MgAlFeCO3SO4 LDHs where 10–25% As(III) formed. Finally, at pH 10 and 0.5 mM Fe(II) (aq), the formation of FeOHs occurred to various degrees but a significant amount of CaCO3(s) precipitated. A 2-stage release and re-adsorption mechanism of total As(aq) occurred following the order: MgAlFeCO3SO4 > MgAlSO4 > MgFeCO3 > MgAlCO3 > MgFeSO4. A significant portion of the solid surfaces (30–90%) was found as As(III) for all reacted LDHs. This work provides a guideline for the environmental behavior of As(V) adsorbed LDHs where relevant underwater cover TMF abiotic reducing conditions may exist.
               
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