ReviewProgress in antimony capturing by superior materials: Mechanisms, properties and perspectives
Graphical abstract
Introduction
Environmental degradation caused by pollutants have motivated interests in developing functional materials for capture of them such as heavy metals and organic contaminants. This is especially true when the pollutants are largely released into environment due to the anthropogenic activities. Antimony (Sb) is listed as one of poisonous heavy metals due to its certified adverse effects on humans and biological systems [86]. Natural processes such as rock weathering and volcanic activities, especially the anthropogenic activities such as exploitation and overuse of materials containing Sb in manufacturing industries, resulting in serious Sb decontamination in aquatic systems. Nowadays, many countries and areas have increasing aggravations of Sb pollution, such as China [36], [63], [137], Canada [91], Italy [94], Iran [108] and India [18]. Unfortunately, the capturing/removal of Sb species was not paid attention until the detectable toxicity and harm to humans at 1990 s.
Sb has a typical of s2p3 outer electric orbits with four oxidation states (-3, 0, +3 and + 5). They are subjected to hydrolyze in aquatic systems and mainly existed in negatively-charged pentavalent (Sb(V)) and uncharged trivalent (Sb(III)) species, in which Sb(III) is ten times more toxic than Sb(V). Among various technologies, adsorption is one of the most important methods for the removal of toxic metals involving the merits of simplicity, economics and high efficiency. Considerable researches have been devoted to concentrate and adsorb Sb species by the natural minerals with abundant hydroxyl groups via surface complexation, including goethite (α-FeOOH), hydrous ferric oxide (HFO), hematite (α-Fe2O3), maghemite (γ-Fe2O3), ferrihydrite and magnetite (Fe3O4) [32], [52], [96], [97], [124], [125]. However, the natural minerals generally have a low purity, instability, low adsorption rate and powered nature [29]. Thus, various types of advanced synthetic materials have been intentionally designed and developed for effective removal of Sb species from aqueous media. Fig. 1 illustrates important developmental progresses of synthetic materials for the removal of Sb such as bimetallic (hydro)oxides, mixed matrix membranes (MMMs) and metal–organic frameworks (MOFs). To date, there are numerous reviews summarizing the speciation, toxicity, distribution, mobility and fate of Sb, as well as the removal technologies using iron-based materials for Sb [20], [27], [35], [39], [62], [112], [121], [123]. However, to the best of the author’s knowledge, recent advances of various advanced synthetic materials for the capturing of Sb has not yet been reported. Similar literature reviews regarding other heavy metals such as arsenic have been reported [69]. Considering the worsening contamination and rigorous Sb regulation in water, it is of great importance and urgency to give a comprehensive summary about the recent advances on the development of artificial materials for Sb pollution control.
In this review, we provide a critical summary of the state of the art in the fields of design, properties and removal mechanism for capturing of Sb species by superior materials. Firstly, we discuss the possible removal mechanism combing the chemical properties of Sb species. Secondly, we critically review the recent progress on the application of bimetal-based (hydro)oxides, nanostructured materials, and polymer-host materials. Moreover, the material fabrication path, removal performance and mechanism are systematically summarized. Finally, future challenges and perspectives for capturing of Sb are addressed in this review.
Section snippets
Possible mechanisms for Sb capturing
The predominant existing species of Sb are highly related to pH values and potentials, where Sb(V) mainly existed as Sb(OH)6− having an octahedral configuration with a pKa of 2.72, and Sb(III) predominantly existed as Sb(OH)3 with a pyramidal configuration and a pKa of 11.6 at a wide pH range, respectively. The comparison of chemical properties of Sb(III) and Sb(V) are listed in Table 1. Correspondingly, the removal performance and mechanisms are closely related to their chemical properties.
Bimetal-based materials
Metal and metallic oxides have been proposed as low-cost and effective adsorbents for Sb removal via redox reaction and surface complexation, such as by iron oxides [32], [38], [105], [145], manganese oxides [46], [115], [118], [127], alumina oxides [45]and zirconium oxides [54], [79]. Table 3 shows some reported metal-based materials for the removal of Sb. It can be found that most of the bimetal (hydro)oxides possess better removal capacities than the single-metal (hydro)oxides. Here in this
Nanostructured materials
In general, nanomaterials have outstanding removal capacities for heavy metal ions due to their unique size-dependent properties [19], [113]. Here in this section, we focus on discussing the removal of Sb by nanomaterials in the categories of metal–organic frameworks (MOFs), magnetic nanocomposite, and novel functionalized nanocomposite materials. We also assess possible improvements in the real applicability of these nanomaterials.
Polymer-based composite materials
Polymers have attracted tremendous interests in environmental applications on account of their good chemical stability, high mechanical properties and easy processing. In this section, we will discuss the designed neat polymers and polymer-host composite materials utilized for Sb removal, respectively.
Conclusion and perspective
In this review, we examined the recent progresses on superior and novel materials for the removal of Sb species, mainly including bimetal-based materials, MOFs, nanocomposites, and polymer-based materials. The possible removal mechanisms are highly related to the chemical properties of Sb species. Firstly, comparisons and characteristics of ordinary bimetal oxides and LDHs are concluded. Secondly, MOFs (e.g., Zr-based and Fe-based MOFs) exhibit superior removal properties for Sb species.
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
Pengfei Qi and Yan Wang contribute equally to this manuscript. This research was supported by National Natural Science Foundation of China (52000110), Natural science foundation of Shandong Province (ZR2019QD019), and Program for Taishan Scholar of Shandong Province.
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