The interactions and adsorption mechanisms of ternary heavy metals on boron nitride
Introduction
Over the years, heavy metal pollution in water has received increasing attention. Copper, cadmium, and nickel are common heavy metals in industrial wastewater. Due to their toxicity and non-biodegradability, they may cause harm to human health and the ecosystem once they are discharged into a receiving water body without appropriate treatment.
Several methods, including chemical precipitation, membrane filtration, and electrochemical treatment have been reported to remove heavy metals from wastewater. Wang et al. (2019) proposed a comprehensive treatment process using hydroxide precipitation coupled with H2O2 oxidation and NaHS sulfide precipitation to achieve the selective removal of Cu, Fe, and Zn from wastewater. Duan et al. (2017) studied the reduction/removal of Cr (VI) using electrically conducting carbon nanotube-polyvinyl alcohol composite ultrafiltration membranes. Zhao et al. (2019a) proposed a new type of capacitive deionization-electrodeionization technology for the treatment of low-level Cu (II) wastewater. Compared to these technologies, the adsorption process could avoid producing large volumes of waste sludge, membrane backwashing effluent, or high energy consumption (Giwa et al., 2019).
The most essential aspect in the application of adsorption is the sorbent. Synthetic adsorbents possess high adsorption capacities to heavy metal ions compared to that of natural sorbents (Han et al. 2017; Chi et al., 2009; Bouhamed et al., 2012). For instance, Hayati et al. (2017, 2016) synthesized polyamide/amine dendrimer-modified carbon nanotubes, which had an adsorption capacity of 3333 mg/g and 3900 mg/g for Cu2+ and Ni2+, respectively. These capacities are much higher than that reported for fly ash-based adsorbents (7 mg/g for Cu2+) or natural clay (2.7 mg/g for Ni2+, 3.3 mg/g for Cd2+) (Duan et al., 2016; Darmayanti et al., 2019; Khan et al., 2019). Boron nitride (BN) has the advantages of excellent thermal stability, superb resistance to oxidation as well as chemical inertness. It has a similar structure to graphene but contains B–N polar bonds. Compared with carbon-based adsorbents, B–N polar bonds have better adsorption capacity (Li et al., 2013). Furthermore, due to BN materials contain the high specific surface area, bulk π systems, defects, and functional groups, recent researches reported shown it has an excellent adsorption performance towards metal ions in the single-contaminant system. (Xue et al., 2016; Mubarak et al., 2018; Liu et al., 2015; Yu et al., 2018).
Generally, industrial wastewater contains a variety of heavy metal ions with different concentrations. For example, the concentrations of Cu2+ and Ni2+ were 8 mg/L and 14 mg/L in electroplating wastewater; Cu2+ and Cd2+ concentrations were 9.3 mg/L and 6.1 mg/L in smelting effluent, and 19.5 mg/L and 34.3 mg/L in copper production effluents, respectively (Ajmal et al., 2001; Zhou et al., 2017; Mavrov et al., 2006). In these complex multicomponent systems, different heavy metal ions may interact and affect the adsorption capacities of specific sorbents (Srivastava et al., 2005; Zhang et al., 2017; He et al., 2018). Moreover, differences in ion concentrations may further affect their interactions. Therefore, these factors increase the difficulty of predicting the performance of sorbents. However, most current studies use the same metal ion concentration in multicomponent metal ion adsorption (Zhou et al., 2019a,Zhou et al., 2019b; Zhao et al., 2019c). In addition, the interaction behavior of heavy metal ions at different concentrations are seldom reported.
In this study, we synthesized BN and discuss its adsorption capacity for Cu2+, Cd2+, and Ni2+ in single-comonent systems. Then, the interactions between the three ions in an equi-concentration ternary system were studied. Following this, the effect of metal ion concentration on their interaction with the BN sorbent was studied based in the ternary system. We also explore the different adsorption mechanisms observed in the experiments using X-ray photoelectron spectroscopy (XPS). This paper provides a deeper understanding of the adsorption behavior of heavy metal ions in multi-component systems that more accurately reflect their behavior under more realistic conditions that exist in complex wastewater streams.
Section snippets
Reagents
Boric acid and melamine were purchased from Aladdin Reagent (Shanghai, China). Sodium hydroxide and nitric acid were purchased from Damao Reagent (Tianjin, China). Copper nitrate, nickel nitrate, and cadmium nitrate were purchased from Guangfu Technology (Tianjin, China). All of the reagents are analytic reagent quality without further purification.
Preparation of BN
The synthesis of BN was based on a two-step method (Li et al., 2017a), with some modifications. Briefly, 0.075 mol boric acid and 0.02 mol melamine
Physical characterization
The XRD spectra (Fig. 1a) of BN showed two characteristic peaks that are consistent with the standard card (pdf-#45–0893) of BN (JADE MDI software). The significant diffraction peaks appeared at the 2θ of 25.15°–26.32° and 42.05°–42.85°, corresponding to the (0002) and (100) planes of hexagonal BN, respectively. The deduced lattice parameters of d0002 = 0.339–0.345 nm and d100 = 0.211–0.214 nm are similar to previous studies (d0002 = 0.356–0.376 nm, d100 = 0.210–0.220 nm) (Li et al., 2014;
Conclusions
This study demonstrated the interaction of Cu2+, Cd2+, and Ni2+ and the adsorption mechanisms on the synthetic BN. The BN is short rod-like, rich in surface pores, and contains hydroxyl, amino, etc. functional groups. The metal ions could be rapidly adsorbed on BN and follow the affinity order of Cu2+>Cd2+>Ni2+ in both the single and the ternary systems. The adsorption behavior changes due to the interaction between metal ions in the ternary system. Cu2+ showed an antagonistic effect on the
Acknowledgements
We are very grateful to the National Natural Science Foundation of China (Grant No. 51608165) and China Scholarship Council (File No. 201806705003) for the financial support for this paper.
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