Novel adsorbent synthesized from red mud and acid mine drainage for enhanced contaminant removal: Industrial waste transformation, adsorbent performance and metal(loid) removal mechanisms.

[Display omitted] • AMD catalyzed red mud transformation into an effective adsorbent. • Sb(V), As(V), and Pb(II) removal capacities were 1638, 109 and 519 mg/g respectively. • Ca-bearing phases and Fe-(hydr)oxides played key roles in Sb and As immobilization. • A silicate gel that coats the Sb precipitates ensures their high stability at low pH. • Convertible sulfates play the dominant role in Pb(II) removal via formation of PbSO 4. Antimony (Sb), arsenic (As), and lead (Pb) are toxic metal(loid)s that can cause serious environmental pollution. The above emphasizes the need for a development of efficient technologies for metal(loid) removal, especially from low-pH environments due to the increased mobility of the contaminants under acidic conditions. Herein, for the first time, removal of Sb(V/III), As(V/III), and Pb(II) from acidic waters is described, using low-cost adsorbents synthesized from red mud (RM; a solid waste from the alumina industry) under the catalysis by acid mine drainage (AMD; acidic effluents from mines). The reactions between RM and AMD were studied to describe Fe/S/Ca/Al/Si speciation transformations during the adsorbent formation. In addition, Sb/As/Pb adsorption behavior and the relationship between adsorbent properties and Sb/As/Pb removal efficiencies were investigated. The maximum removal capacities for Sb(V), Sb(III), As(V), As(III), and Pb(II) reaching 1,637.8, 80.2, 109.2, 16.4, and 518.7 mg/g, respectively. The primarily Ca2+ from the Ca-bearing compounds (determined in RA2, synthesized under S RM /L AMD 2:1) contributed to Sb(V) removal (via precipitation of CaSb 2 O 5 (OH) 2 and formation of Sb-bearing precipitate, with silicate gel nanospheres securing high stability of the immobilized Sb). In the As immobilization process, Fe(III) (hydr)oxides (formed in RA4, synthesized under S RM /L AMD 4:1) such as goethite (α-FeOOH) and bernalite (Fe(OH) 3) played a dominant role. Convertible sulfates (e.g., CaSO 4 and Al 2 (SO 4) 3) in RA10 (synthesized under S RM /L AMD 10:1) ensured a high removal capacity for Pb(II) across a wide pH range (2 to 7) via PbSO 4 precipitation. In contrast, the formation of PbCO 3 and Pb 3 (CO 3) 2 (OH) 2 was the main mechanism for Pb(II) removal by unamended RM at pH 5.0, while no contaminant removal capacity was observed at pH 2.0. [ABSTRACT FROM AUTHOR]