Simultaneous and synergistic effect of heavy metal adsorption on the enhanced photocatalytic performance of a visible-light-driven RS-TONR/TNT composite
Graphical abstract
Introduction
Removal of reactive elements from wastewater has attracted much attention, because of non-biodegradability, potential carcinogenicity and other health risks, as well as adverse ecological impacts (Garg et al., 2004; Konstantinou and Albanis, 2004; Nishiyama et al., 2016; Rafatullah et al., 2010; Wu and Tseng, 2008). The practice of discharging industrial effluent contaminates water with many hazardous substances, including heavy metal ions, radioactive ions, dyes, and other organic pollutants. The toxicity and persistence of heavy metals causes great environmental concern (Kabra et al., 2008) and one of the most common organic pollutants in the aquatic environment is dye. Heavy metals and dyes are often present together in wastewater and coexist in contaminated environments, posing threats to human health and the environment (Parshetti and Doong, 2011). Such co-contamination presents many challenges for effective waste management and remediation.
Recent studies have shown the utility of titanate nanomaterials for environmental remediation (Dhandole et al., 2016; Konstantinou and Albanis, 2004). Since the discovery of structurally modified titanium-based materials, 1D titanate nanotubes (TNTs) have been demonstrated to be a promising nanostructured absorbent for removing heavy metals and various toxic elements (Dhandole et al., 2018a; Nishiyama et al., 2016). The advantages of the large specific surface area and high pore volume of synthesized titanate nanotubes afford a simple, cost-effective, and environment-friendly technology (Chen et al., 2010; Xiong et al., 2011). These properties make titanate nanotubes (TNTs) useful not only as adsorbents to remove and recover heavy metals and toxic elements (Moon et al., 2000), but also for diverse applications such as in lithium ion batteries (Lan et al., 2005), hydrogen storage devices (Lim et al., 2005), ion exchange membranes (Feng et al., 2007; Sun and Li, 2003) and gas sensors (Han et al., 2007), as well as photocatalysts (Bavykin et al., 2006; Kim et al., 2018a).
Photocatalysis has emerged as an alternative technology to address pollution by organic compounds. Several studies have reported the use of modified TiO2 nanomaterials in photocatalytic decomposition and degradation strategies for organic pollutants, including dyes (Aarthi et al., 2007; Doong and Tsai, 2015). However, the photocatalytic activity of TiO2-based nanostructures is limited due to their wide optical bandgap energy that absorbs only in the short wavelength range of the UV spectrum, limiting the utility of TiO2-based nanostructures for photocatalytic applications.
Previous reports have highlighted the effect of metal co-doping on reducing the optical bandgap energy of metal oxide semiconductors (e.g., TiO2), which increases the charge separation of photogenerated electron-hole pairs and shifts the absorption wavelength toward the visible light region. However, reducing the bandgap energy is not sufficient for enhancing the performance of photocatalysts, due to the high recombination rate of photogenerated charge carriers (Dhandole et al., 2018b; Kim et al., 2018a, 2018b). Several studies have reported limiting the charge recombination rate by depositing metal, metal oxide, or metal sulfide nanoparticles on the photocatalyst (Hou et al., 2009; Wilson et al., 2012Yan et al., 2018; ). The deposited nanoparticles facilitate charge transfer, greatly enhancing photocatalytic performance for degradation of organic pollutants.
Mono-remediation approaches target either the recovery or degradation of pollutants in wastewater. Few reports are available on TiO2-based dual remediation techniques for simultaneous removal of heavy metal ions and degradation of organic contaminants (Doong et al., 2012; Kyung et al., 2005). The challenge lies in the structural and/or optical properties of the nanomaterials that limit practical solutions for remediation of wastewater with multiple contaminants in an economic and environment-friendly way. To address these concerns, we previously designed an efficient TiO2 nanorod and titanate nanotube (RS-TONR/TNT) photocatalyst for degradation of organic co-contaminants under visible light irradiation (Kim et al., 2018a, 2018b). However, bare RS-TONR/TNT alone did not show significant enhancement in photocatalytic activity. That was achieved by loading with copper ions, which enhances the catalytic reaction by improving charge transport in the composite. In the present study we eliminated the need for copper loading on RS-TONR/TNT by directly using the composite for simultaneous adsorption and degradation reactions.
The objective of the present study was to evaluate the capacity of the RS-TONR/TNT composite to remove various heavy metals and explore a synergistic effect of metal adsorption on the photocatalytic degradation of organic pollutants, using Orange (II) dye and Bisphenol A as test compounds. Because the photocatalytic performance of RS-TONR/TNT was maximized with adsorbed Cu, experiments were conducted with Cu to investigate associated mechanisms. Methanol (MeOH), EDTA, p-chlorobenzoic acid (pCBA), and benzoic acid (BA) were used as probes to detect reactive oxygen species (ROS) and Cu species, and a charge transfer mechanism was proposed.
Section snippets
Chemical reagents
Most of the chemical reagents were used without further purification. Na2HPO4 (Kanto Chemicals, 99%), NaCl (JUNSEI Chemicals, 99.5%) and P25 (Degussa), RhCl3·3H2O (Kojima, 99%), Sb2O3 (Acros, 99%), NaOH (Samchun, 98%), Cu(NO3)2·3H2O (JUNSEI, 99%), Pb(NO3)2, Cd(NO3)24H2O, N2O6Zn6H2O, Orange (II) sodium salt (Aldrich, 85%), methanol (MeOH, Aldrich, 99.8%), para-chlorobenzoic acid (pCBA, Aldrich, 99%), benzoic acid (BA, Aldrich, 99.5%), 4-hydroxylbenzoic acid (4-HBA, Aldrich, 99%), formaldehyde
Simultaneous heavy metal ion removal and degradation of organic pollutants
This work demonstrated simultaneous removal of heavy metal ions from water and decomposition of organic pollutants by the Rh and Sb co-doped TiO2 nanorod and titanate nanotube composite (RS-TONR/TNT). Adsorption of the various heavy metal ions by the RS-TONR/TNT composite was examined at a concentration of 25 mg metal/L. Fig. 1 shows that adsorption of all ions approached equilibrium within 20 min of reaction time. The adsorption of Pb(II) was particularly rapid in the first 5 min, likely
Conclusions
Simultaneous and synergistic removal of heavy metals ions and degradation of organic pollutants in solution by a RS-TONR/TNT composite was studied under visible light. Experimental results show the composite has a high adsorption capacity for heavy metal ions, following the sequence Pb(II) > Cd(II) > Cu(II) > Zn(II). Photocatalytic degradation of Orange (II) dye and BPA by the composite was enhanced in solution containing these heavy metals but greatest in solution containing Cu(II) ions.
Acknowledgments
This research was supported by the Korea Research Fellowship Program through the National Research Foundation of Korea (NRF) funded by the Ministry of Science and ICT (2017H1D3A1A02014020). This work was also supported by the NRF grant funded by the Korea government (MSIT) (No. 2019R1A2C1006402).
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Equal contributions.