One-pot synthesis of layered double hydroxide hollow nanospheres with ultrafast removal efficiency for heavy metal ions and organic contaminants
Graphical abstract
Introduction
The supply of safe and clean drinking water is essential to humans and other lifeforms. Water pollution mainly occurs when pollutants are directly or indirectly discharged into bodies of water without adequate treatment. The contaminants accumulated from industrial effluents and agricultural wastes contain health hazardous chemicals, such as heavy metals and organic pollutants, which pose serious risks to human health and ecological systems. In particular, arsenic and chromium are heavy metal ions that are highly toxic to the human body, and long-term exposure to arsenic and chromium are responsible for skin, liver and lung cancer, kidney damage and anaemia (Naujokas et al., 2013; Kieber et al., 2002; Islam et al., 2017). Due to their serious virulence, the WHO (World Health Organization) defines the acceptable level as 10 ppb for the maximum concentration of arsenic and 50 ppb for chromium in safe drinking water (USEPA, 2003; WHO, 2008).
In recent years, many conventional techniques have been developed for the removal of heavy metal ions from wastewater, including adsorption, chemical precipitation, chemical redox reactions, electrochemical treatments, membrane processes, and ion exchange (Islam et al., 2017; Tchobanoglous et al., 2003; Al-Shannag et al., 2015; Admassie et al., 2015; Sounthararajah et al., 2015; Vijayakumar et al., 2015). Among the aforementioned methods, adsorption is considered to be one of the most economical and effective techniques owing to its simplicity, ease of operation and cost effectiveness (Wen et al., 2017). This technique is easy to operate and equally effective in the removal of toxic pollutants, even at low concentrations. Since the effectiveness and efficiency is the core of the adsorption technique, high surface area and active adsorption sites are necessary for the adsorbents (Zeng et al., 2015; Guo et al., 2014).
Layered double hydroxides (LDHs, [M2+1−xM3+x(OH)2]x+[(An−)x/n]x−·mH2O) in the form of anionic clays have attracted increasing attention for the adsorption of anionic inorganic and organic pollutants thanks to their layered structure, high surface area, porous structure and interlayer ion exchange (Abellan et al., 2015; Zubair et al., 2017). Easily prepared LDHs, such as MgAl-LDH, CaFe-LDH, and ZnAl-LDH, have been widely applied as adsorbents for various organic dyes and heavy metal ions due to their high adsorption capacity, low-cost and non-toxicity (Shan et al., 2015; Wu et al., 2012; Li et al., 2014). In particular, spherical LDH microparticles with porous structures have attracted significant attention for their structural stability and high surface area, which are essential factors enhancing their removal capabilities for water pollutants (Li et al., 2014; Sun et al., 2015; Lei et al., 2017a, 2017b; Lin et al., 2015). To control the morphology and porosity in the LDH structure, hydrothermal methods have been employed in aqueous media using surfactants (Sun et al., 2015), sacrificial templates or urea as a precipitating agent (Li et al., 2014; Lei et al., 2017a, 2017b; Lin et al., 2015). The porous LDH particles have been applied as adsorbents for anionic organic dyes and heavy metal ions. Despite enhancing the adsorption efficiency for pollutants, several considerable problems remain, such as the toxicity of the surfactants, multiple steps for the synthesis and the performance limit for heavy metal removal. Therefore, developing a simple, nontoxic, low-cost synthetic strategy with some unique features towards excellent remediation performance is still a great challenge.
In this work, Mg/Fe-LDH hollow nanospheres with high specific surface area were synthesized by a simple ethylene glycol-mediated thermal method using only two metal precursors, Mg2+ and Fe3+. After calcination at 400 °C for 1 h, the Mg/Fe-LDH was oxidized to Mg/Fe layered double oxide (LDO) retaining the hollow sphere shape, which could rapidly purify water contaminated by heavy metals to drinking water standards. In addition to the heavy metal adsorption tests, excellent catalytic performance for the reduction of 4-nitophenol by introducing Au nanoparticles into the LDO nanosphere structure was also observed.
Section snippets
Materials
Magnesium acetate tetrahydrate (Mg(OAc)2·4H2O, 98%), iron (III) chloride hexahydrate (FeCl3·6H2O, 98%), sodium arsenate dibasic heptahydrate (Na2HasO4·7H2O, 99.99%), potassium dichromate (K2Cr2O7, 99.99%), ethylene glycol (C2H6O2, 99.9%), iron (III) sulfate hydrate (Fe2(SO3)3·xH2O, 97%), chloroauric acid (HAuCl4, 99.99%), sodium borohydrate (NaBH4), 4-nitrophenol, sodium chloride (NaCl, 99.5%), sodium carbonate monohydrate (Na2CO3·H2O, 99.5%), potassium phosphate (KH2PO4, 99%), sodium sulfate
Synthesis of MF-LDH and MF-LDO hollow nanosphere
The preparation strategy for constructing the Mg/Fe-LDH (MF-LDH) and the thermally oxidized MF-LDH (MF-LDO) nanospheres with hollow cores is shown in Fig. S1, which involves simple one-step thermal reaction between Mg(OAc)2 and FeCl3 in ethylene glycol as the solvent. The morphologies of the nanospheres were characterized by SEM and TEM (Fig. 1a–d). As-synthesized MF-LDH nanospheres have a hollow structure with a 500 nm flower shape (Fig. 1a and b). The hollow flower structure is retained after
Conclusion
In summary, Mg/Fe layered double hydroxide (MF-LDH) hollow nanospheres were prepared by a simple thermal method. After the calcination at 400 °C, the MF-LDH was converted into the corresponding oxide, Mg/Fe layered double oxide (MF-LDO), retaining the hollow nanosphere structure. The MF-LDO nanospheres showed excellent removal efficiency for both As(V) and Cr(VI) ions, with maximum adsorption capacities of 178.6 mg g−1 [As(VI)] and 148.7 mg g−1 [Cr(VI)], and complete heavy metal removal
Acknowledgement
This research was supported by the National Research Council of Science and Technology through the Degree and Research Center Program (DRC-14-1-KBSI).
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2022, Journal of Cleaner ProductionCitation Excerpt :The low concentrations of Cr(VI) in tests 4, 8, 12 and 16 (i.e. A1B4C4, A2B4C3, A3B4C2 and A4B4C1) indicated that sufficient Co2Fe1–CO3-LDH is able to adsorb formed Cr(VI) during the treatment. These results were consistent with excellent adsorption performance of LDHs for Cr(VI) observed in previous studies and preliminary confirmed our hypothesis that newly formed Cr(VI) during AOPs can be absorbed by Co2Fe1–CO3-LDH immediately after its formation (Ling et al., 2016; Ma et al., 2017; Mubarak et al., 2018). The removal of TOC followed similar trends as the removal of total Cr (Table 2, Fig. S4).