New insights into stoichiometric efficiency and synergistic mechanism of persulfate activation by zero-valent bimetal (Iron/Copper) for organic pollutant degradation

https://doi.org/10.1016/j.jhazmat.2020.123669Get rights and content

Highlights

  • DCP oxidation can be notably enhanced by Fe/Cu compared to nZVI.

  • The rate constant of DCP oxidation is linearly correlated to the Cu ratio in Fe/Cu.

  • A synergistic effect exists between Cu and Fe in activating persulfate.

  • The Fe and Cu species in Fe/Cu determine their synergistic effects in DCP oxidation.

  • Cu atoms on Cu2O layers are the sites dominantly responsible for PS activation.

Abstract

Extensive studies have been devoting to investigating the catalytic efficiency of zero-valent iron (Fe0)-based bimetals with persulfate (PS), while little is known in the stoichiometric efficiency, underlying mechanisms and reaction center of zero-valent bimetallic catalysts in activating PS. Herein, nanoscale zero-valent Fe/Cu catalysts in decomposing 2,4-dichlorophenol (DCP) have been investigated. The results show that the increase of Cu ratio from 0 to 0.75 significantly enhances the DCP degradation with a rate constant of 0.025 min−1 for Fe0 to 0.097 min−1 for Fe/Cu(0.75) at pH ∼3.3, indicating Cu is likely the predominate reaction centers over Fe. The PS decomposition is reduced with the increase of Cu ratios, suggesting the stoichiometric efficiency of Fe/Cu in activating PS is notably enhanced from 0.024 for Fe0 to 0.11 for Fe/Cu(0.75). Analyses indicate Cu atoms are likely the predominant reaction site for DCP decomposition, and Fe atoms synergistically enhance the activity of Cu as indicated by DFT calculations. Both SO4- and ⦁OH radicals are responsible for reactions, and the contribution of SO4- is decreased at higher pH conditions. The findings of this work provide insight into the stoichiometric efficiency and the reaction center of Fe/Cu catalysts to activate PS for pollutant removals.

Introduction

Sulfate radical (SO4-)-based catalytic oxidation for the destruction of refractory organic pollutants has received great interests in treating contaminated groundwater and soils (Zhong et al., 2015; Liu et al., 2014), because of its relatively higher redox potential of 2.5–3.1 V compared to the hydroxyl radical (⦁OH; 1.8–2.7 V) (Huang et al., 2017). Both peroxymonosulfate (PMS) and persulfate (PS) have been used as precursors for SO4- generation (Zhong et al., 2015; Zhang et al., 2018). To promote SO4- yield, great progress has been made in applying transition-metal oxide (e.g. Co, Fe, Cu, and Mn)-based catalysts for enhancing the PS and PMS activations (Liang and Guo, 2010; Lei et al., 2015; Anipsitakis and Dionysiou, 2003). Compared with PMS, PS is relatively low-cost and more stable for practical use but more difficult to be activated, restricting its extensive applications (Yu et al., 2016).

Recent studies show that a combination of transition metals such as Co/Fe, Mn/Fe, and Cu/Fe to form binary metallic oxides can significantly enhance PS/PMS activation (Deng et al., 2013; Bao et al., 2019). Within these element combinations, Cu and Fe are particularly considered to be favorable for the heterogeneous PS activation due to their benign nature compared to other metals like Co (Lei et al., 2015). For instance, two parallel studies developed a novel Fe(II)/CuO system, and a similar synergistic effect of Fe(II) with CuO was observed for activating PS (Zhang et al., 2018, 2017). Besides, a binary Fe/Cu oxide catalyst, CuFeO2 has also shown a great capability for organic pollutant degradation with PS as the oxidant (i.e. about one magnitude greater than that with Fe2O3) (Feng et al., 2016). A common explanation for such synergistic effects is that the acceleration of electron cycling within the redox couples between the two metals in composites [e.g. Cu(II)/(I) and Fe(III)/Fe(II)] (Deng et al., 2013; Feng et al., 2016; Zhang et al., 2013). Interestingly, evidence also suggests that the presence of Cu(I) is of particular importance on enhancing PS activation and therefore the SO4-/⦁OH radical generation (Zhang et al., 2018; Feng et al., 2016; Xia et al., 2017). Recently, Huang and coworkers discovered that the synergistic efficiency of a Fe/Mn oxide catalyst (Mn1.8Fe1.2O4) was highly related to the stoichiometric ratio of the two metals, which is likely due to the different roles of the two metals with Mn primarily acting as active site and Fe(III) as adsorption site (Huang et al., 2017). A very recent study conducted by Bao and coworkers has also reported that the stoichiometric efficiency of the Co/Fe oxides plays a crucial role in PMS activation and radical generation for oxidizing sulfamethoxazole (Bao et al., 2019). However, the stoichiometry of Fe/Cu on its capability for PS activation and radical generation remains unclear, and the corresponding radical generation performance can certainly vary accordingly.

In addition to metallic oxides, their zero-valent forms particularly Fe° nanoparticles (nZVI) have also been studied to activate PS/PMS for removing organic pollutants (Liang and Lai, 2008; Xiong et al., 2014). More strikingly, better performances of pollutant removal by nZVI with PS have been frequently observed compared to its oxides (Xiong et al., 2014; Guan et al., 2015). This is likely due to their low reduction potentials [e.g. (Fe2+/Fe°) = -0.44 V] (Liu et al., 2020), benefiting for PS activation and pollutant removal. Because of the important role of nZVI in groundwater remediation, different nZVI-based binary nanoparticles (e.g. Fe/Pd, Fe/Cu) have been developed and shown their superiority in promoting electron transfer and pollutant removal (He and Zhao, 2008; Fang et al., 2018a). Importantly, our previous studies have also shown that the reductive transformation of organic pollutants by zero-valent binary metals (e.g. Fe/Cu) is highly related to the stoichiometric ratio of Fe/Cu under anaerobic conditions (Fang et al., 2018a; Xu et al., 2019). This unique feature probably also determines their capability in activating PS. Nevertheless, knowledge of the performance of nanoscale zero-valent Fe/Cu and underlying mechanisms in consideration of its stoichiometric efficiency is still unknown.

In the present study, binary zero-valent Fe/Cu nanoparticles with different stoichiometric ratios were prepared and characterized, and the prepared nanoparticles were systematically examined for their performance in PS activation. 2,4-dichlorphenol (DCP) was selected as the model compound, to investigate the catalytic oxidation efficiency of Fe/Cu catalysts with PS under the pH-controlled conditions, because it is a representative for phenolic compounds with a well-known structure and a high solubility. Accordingly, the stoichiometric efficiency of Fe/Cu for PS activation and DCP degradation has been systematically analyzed by combining the findings of batch experiments with the structural evolution and elemental states of Fe/Cu nanoparticles during the activation processes and theoretical calculations. In final, the underlying mechanisms of synergistic effects of Fe and Cu determining the stoichiometric efficiency of the catalysts were systematically addressed.

Section snippets

Chemicals

All chemical reagents were of analytical or higher grade and detailed in the supporting information.

Preparation of zero-valent Fe/Cu

Zero-valent iron/copper nanoparticles (Hereafter denoted as Fe/Cu (x) for simplicity, x refers to the mass ratio of Cu) were prepared with a modified method according to our previous study (Fang et al., 2018a). In a typical synthesis, proper amounts of FeSO4·7H2O and CuSO4·5H2O salts were dissolved into 80 mL of methanol/water (5:3; v/v), resulting in a Cu content (x) ranging from 0 to 1. The

Characteristics of the Fe/Cu (x) catalysts

The morphologies and structures of the Fe/Cu catalysts with different Fe/Cu ratios are shown in Figure S1, and a representative of TEM images for the Fe/Cu catalyst (x = 0.75) is illustrated in Fig. 1a, clearly showing a nanowire-like morphology with a diameter of 40–50 nm and a length up to several micrometers. A thin shell of approximate 5 nm was observed at the outmost layer which may be due to the oxidation of Fe/Cu catalysts exposure to trace oxygen. Such a unique feature represents a

Catalytic performance of Fe/Cu for DCP degradation

The catalytic performances of the Fe/Cu catalysts with varying stoichiometric ratios have been evaluated and compared for DCP degradation with PS. The results clearly show that there is negligible degradation of DCP by PS in the absence of catalysts, indicating that the direct DCP degradation by PS cannot occur, in line with previous studies (Zhong et al., 2015; Liang et al., 2013b). Meanwhile, the direct degradation of DCP by Fe/Cu, Cu, or Fe nanoparticles alone appears neglect (Figure S3),

Identification of the important Cu and Fe species in Fe/Cu

It is evident that the “co-existence” of Cu and Fe elements with PS can remarkably enhance the reaction rate and extent of DCP degradation as shown in our work (Figure 2a – b), while it is puzzling which species/forms of these elements determine the enhanced DCP degradation. In particular, a few studies have shown that the presence of dissolved Fe (II) ions with/without CuO also has synergistic effects on oxidation of organic pollutants (Zhang et al., 2017; Gupta and Gupta, 1981). Hence, we

Decomposition of persulfate and the stoichiometric efficiency

The decomposition of PS without DCP by the catalysts with different stoichiometric ratios were further examined to evaluate their efficiencies in generating ⦁OH/ SO4- radicals. As shown in Fig. 4a, there is neglect decomposition of PS without adding catalysts, explaining the reason for little DCP degradation by PS alone (Fig. 2a). Interestingly, the decomposition of PS by different catalysts is in an order of Fe° (∼ 79.5%) > Fe/Cu(0.1) (∼ 77.0%) > Fe/Cu(0.2) (∼ 60.9%) >> Fe/Cu(0.4) (∼ 50.0%) >

Radical identification and reaction mechanisms

To identify whether and how much the potential radical species (e.g. SO4- and ⦁OH) can be responsible for the DCP degradation, two typical radical scavengers (MeOH and TBA) were used to quench SO4- and ⦁OH that may be generated from SO4-(Zhu et al., 2018); TBA has a preferential reaction with ⦁OH radical compared with SO4- (kTBA/⦁OH = (3.8–7.6) × 108 M−1 s−1; (kTBA/SO4-= (4.0–9.1) × 105 M−1 s−1) (Zhang et al., 2013; Anipsitakis and Dionysiou, 2004), while MeOH has relatively comparable

Mineralization of DCP and possible reaction pathways

The exploration of mineralization of DCP and its intermediates during the reactions can further assist the understanding of the performance of Fe/Cu for destructing organic pollutants and its mechanisms. Figure S11 illustrates the DCP changes as TOC contents in reaction systems during DCP degradation (C/Co) from 1 to ∼ 0, showing that the relative TOC content (C/Co) in the reaction system rapidly declines from 1 to ∼ 0.25, and finally reaches 80% removal of TOC. The results suggest a high

Conclusions

The present study inspects into the stoichiometric efficiency of zero-valent bimetallic Fe/Cu catalysts towards activating PS and therefore efficiency for the decomposition of DCP under varying conditions. The Fe/Cu catalysts with different Fe/Cu ratios exhibit a unique wire-like core/shell structure, and likely with an oxide layer of Cu2O with increasing the Cu contents. The increase of Cu ratio in Fe/Cu significantly enhances the decomposition of DCP by the catalytic process, indicating the

CRediT authorship contribution statement

Liping Fang: Conceptualization, Investigation, Visualization, Writing - original draft. Kai Liu: Investigation. Fangbai Li: Supervision, Conceptualization, Writing - review & editing, Funding acquisition. Wenbin Zeng: Investigation. Zebin Hong: Investigation. Ling Xu: Investigation. Qiantao Shi: Writing - review & editing. Yibing Ma: Writing - review & editing.

Declaration of Competing Interest

The authors declare there is no conflict of interest.

Acknowledgments

This work was financially supported by the National Natural Science Foundation of China (21876161; 41420104007), and the National Key Research and Development Project of China (No. 2018YFF0213403), Guangdong Academy of Sciences’ Project (2019GDASYL-0102006; 2019GDASYL-0301002; 2018GDASCX-0501)

References (61)

  • X. Guan et al.

    The limitations of applying zero-valent iron technology in contaminants sequestration and the corresponding countermeasures: the development in zero-valent iron technology in the last two decades (1994–2014)

    Water Res.

    (2015)
  • F. He et al.

    Hydrodechlorination of trichloroethene using stabilized Fe-Pd nanoparticles: Reaction mechanism and effects of stabilizers, catalysts and reaction conditions

    Appl. Catal. B

    (2008)
  • N. Hiroyoshi et al.

    Synergistic effect of cupric and ferrous ions on active-passive behavior in anodic dissolution of chalcopyrite in sulfuric acid solutions

    Hydrometallurgy

    (2004)
  • K.C. Huang et al.

    Kinetics of heat-assisted persulfate oxidation of methyl tert-butyl ether (MTBE)

    Chemosphere

    (2002)
  • Q. Ji et al.

    Enhanced reactivity of microscale Fe/Cu bimetallic particles (mFe/Cu) with persulfate (PS) for p-nitrophenol (PNP) removal in aqueous solution

    Chemosphere.

    (2017)
  • G. Kresse

    Ab initio molecular dynamics for liquid metals

    J. Non-Cryst. Solids.

    (1995)
  • H. Kusic et al.

    Modeling of iron activated persulfate oxidation treating reactive azo dye in water matrix

    Chem. Eng. J.

    (2011)
  • R. Li et al.

    Heterogeneous Fenton oxidation of 2,4-dichlorophenol using iron-based nanoparticles and persulfate system

    Chem. Eng. J.

    (2015)
  • C. Liang et al.

    pH dependence of persulfate activation by EDTA/Fe(III) for degradation of trichloroethylene

    J. Contam. Hydrol.

    (2009)
  • L. Liang et al.

    Kinetics and mechanisms of pH-dependent selenite removal by zero valent iron

    Water Res.

    (2013)
  • H. Liang et al.

    Oxidative degradation of p-chloroaniline by copper oxidate activated persulfate

    Chem. Eng. J.

    (2013)
  • C. Liu et al.

    Oxidative degradation of propachlor by ferrous and copper ion activated persulfate

    Sci. Total Environ.

    (2012)
  • K. Liu et al.

    Simultaneous removal of Cd(II) and As(III) by graphene-like biochar-supported zero-valent iron from irrigation waters under aerobic conditions: synergistic effects and mechanisms

    J. Hazard. Mater.

    (2020)
  • Q. Ma et al.

    Synthesis of magnetic CuO/MnFe2O4 nanocompisite and its high activity for degradation of levofloxacin by activation of persulfate

    Chem. Eng. J.

    (2019)
  • J. Shi et al.

    Fe@Fe2O3 core-shell nanowires enhanced Fenton oxidation by accelerating the Fe(III)/Fe(II) cycles

    Water Res.

    (2014)
  • D. Xia et al.

    Activation of persulfates by natural magnetic pyrrhotite for water disinfection: Efficiency, mechanisms, and stability

    Water Res.

    (2017)
  • X. Xiong et al.

    Activating persulfate by Fe0 coupling with weak magnetic field: performance and mechanism

    Water Res.

    (2014)
  • C. Xu et al.

    Enhanced reduction of organic pollutants by Fe/Cu@Pd ternary metallic nanoparticles under aerobic conditions: batch and membrane reactor studies

    Chem. Eng. J.

    (2019)
  • H.Y. Yu et al.

    Cadmium availability in rice paddy fields from a mining area: the effects of soil properties highlighting iron fractions and pH value

    Environ. Pollut.

    (2016)
  • Y. Zhang et al.

    Synergistic effect of ferrous ion and copper oxide on the oxidative degradation of aqueous acetaminophen at acid conditions: a mechanism investigation

    Chem. Eng. J.

    (2017)
  • Cited by (73)

    View all citing articles on Scopus
    View full text