Sorption–desorption of antimony species onto calcined hydrotalcite: Surface structure and control of competitive anions
Graphical abstract
Introduction
In recent years, antimony (Sb) has been described as a critical issue in many research papers because of its high toxicity to human health and impact on the environment [22], [71], [64]. Sb is considered a priority pollutant by the European Union [11], [77] and the United States Environmental Protection Agency [18], [19].
High concentrations of antimony in aquatic systems are related to anthropogenic sources. Dissolved Sb in groundwater have been reported in the range 0.01–1.5 μg L−1 [31], [21] and from ng L−1 to a few mg L−1 in freshwaters [51], [69]. Antimony is around 1 mg L−1 in riverwater [21], [69] while in marine water is around 0.2 mg L−1 [51].
In aquatic environment antimony occurs as free metal ions or inorganic and organic complexes associated with clay minerals, iron oxides and microorganisms [1], [59]. Antimony exists in a variety of oxidation states and the most commons are 3+ and 5+, depending on pH and redox potential. Sb(III) is known to be 10 times more toxic than Sb(V) and both forms have higher toxicity than organic antimony species. At pH ranging from 2.7 to 10.4, Sb(III) occurs as antimonous acid [Sb(OH)3], and at high pH values as antimonite [Sb(OH)], while Sb(V) is found as antimonate [Sb(OH)6−], respectively [77], [22], [52], [42], [5], [70], [71].
Several studies have reported the ability of layered double hydroxides (LDH's) to remove anion contaminants such as oxyanions from aqueous solutions due to their characteristics and surface properties [26], [34], [6], [76], [46], [33].
Hydrotalcite is a layered double hydroxide, a class of anionic clay, formed by Mg2+ and Al3+ within brucite-like positively charged layers, compensated with carbonate and water molecules [3], [63]. Layered double hydroxides can be calcined to eliminate interlayer anions, which can be replaced by others during rehydration to recover their original layered structure. The formed mixed oxides are mostly amorphous, with high specific surface area and ability to recover the layered structure in aqueous solution [75], [37].
The most interesting properties of the calcined hydrotalcite for sorption include large surface area, high anion exchange capacity and good thermal stability [4], [7], [65]. Mechanisms as sorption on the external surface, intercalation by anion exchange and intercalation by reconstruction of calcined product, known as “memory effect”, can participate of uptake of anions from aqueous solution by this material [16], [10].
The complexity of aquatic systems can modify the sorption behavior of species of interest. Factors as surface area, competing ion, temperature and sorbent particle size are important to investigate sorption of anion onto LDH. Therefore, this study aimed to use calcined hydrotalcite in sorption processes of antimony species in competition with nitrate, sulfate and phosphate, applying mathematical modelling associated to the EDXRF analysis to predict sorption-desorption behavior.
Section snippets
Sorbent
Hydrotalcite (Mg6Al2(OH)16CO3) purchased from Sigma–Aldrich (St. Louis, MO, USA) was calcined at 500 °C by 4 h, according other authors [12], [17], [37], [38], to obtain a magnesium aluminum mixed oxide (HTC).
Characterization
Point of zero charge (pHPZC) was determined by intersection of curves from potentiometric titration in different ionic strengths (0.1, 0.01 and 0.001 mol L−1 KCl), according to [41]. A third degree Gaussian fitting was applied using cftool (Interactive Environment for Fitting Curves to
Characterization
The pHPZC (12.2) for calcined hydrotalcite was determined by the intersection of the curves (see Figure 1 in Supplementary Material), and since it was higher than the sample pH in water (11.5), positive charges predominate on the surface [37], [60], [26]. Li et al. [37] obtained pHPZC 11.6 for hydrotalcite calcined at 500 °C while Han et al. [29] reported values ranging from 12.0 to 12.5 for uncalcined Mg–Al LDH's.
The high specific surface area, 301.3 m2 g−1, measured by BET method, was similar to
Conclusions
Calcined hydrotalcite showed to be an excellent sorbent for the Sb(III) and Sb(V) removal from aqueous solutions. Their high sorption efficiency is attributed to the small sorbent particles and large surface area. Geometry and structure seem to affect the sorption capacity, larger for Sb(III) pyramidal and with a lone pair and lower for Sb(V) octahedral.
A low ability of the sorbent to desorb antimony species was verified with positive hysteresis indexes and very low mobilization factors, in
Acknowledgements
The authors would like to thank the Conselho Nacional de Desenvolvimento Cientifico e Tecnológico (CNPq, Brazil) under Grants 309927/2015-3 and 304066/2015-0 (Researcher grant), and Fundação Araucária (FAP-FA, Brazil) under Grants 507/2014 (Researcher grant) and 302/2012 (Research grant) for their financial support and fellowships.
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2022, Journal of Hazardous MaterialsCitation Excerpt :A field study has also demonstrated efficient removal of Sb from shooting ranges using Fe adsorbents (Okkenhaug et al., 2016). Other examples of promising mineral-based adsorbent of Sb include Mn minerals such as hydrotalcite and biogenic manganese oxide, and Fe-Mg layered double hydroxide (LDH) with interlayered hydroxyl (Cao et al., 2020; Constantino et al., 2018; Wang et al., 2019). Adsorbents amended with organic substances have also emerged as novel Sb removal tools.