Exploring the mechanism of ZrO2 structure features on H2O2 activation in Zr–Fe bimetallic catalyst
Graphical Abstract
Introduction
Hydroxyl radicals (HO•) with high oxidation ability (E0 = 2.73 V) and strong electrophilic addition properties, are one of the most powerful oxidizing agents, which have a significant effect on the removal of refractory organics in wastewater treatment [1], [2], [3]. Activation of H2O2 by transition metals is an effective way to generate HO• [4], [5], [6]. Among them, the Fenton reaction catalyzed by Fe(II) is considered to be the most economical and effective choice for HO• generation [7], [8], [9]. However, the traditional Fenton process still faces bottlenecks, such as narrow working pH range and secondary pollution caused by iron sludge, which need to be further improved [10], [11], [12]. In recent years, a large number of researches have been devoted to the development of heterogeneous Fenton processes. But, the cycling rate between Fe(II) and Fe(III) (k = 0.02 M−1 s−1) in the Haber-Weiss process is much lower than that of Fe(II) and H2O2 (k = 76 M−1 s−1), which still limits the generation of HO• [13], [14].
The bimetallic catalytic system can realize the rapid Fe(III) reduction by coordinating the spontaneous electron transfer process inside the catalyst, without external energy supply [15], [16]. In addition to the activation of H2O2 by low valence transition metals such as Cu(I), Co(I) and Mn(II), the thermodynamic spontaneous process based on the energy difference between redox potentials can also accelerate Fe(III) reduction, thus promoting the formation of HO• in the bimetallic catalysts systems [17], [18]. However, the dissolution of heavy metals in this type of bimetallic catalysts can reach several milligrams per liter [19], [20], [21]. And this will not only threaten the safety of water quality, but also increase the cost of subsequent treatment.
Good biocompatibility and stability of zirconium make it can be used in the synthesis of environment-friendly bimetallic catalysts [22]. Since Zr does not possess the characteristics of variable valence state similar to Cu, Mn and Co etc., which has unsaturated 3d orbital, ZrO2 is only used as a stable carrier to enhance the dispersion of iron oxides in heterogeneous Fenton processes [23], [24]. The dispersing effect and low dissolution rate of ZrO2 enable the Zr-Fe bimetallic catalyst to efficiently activate H2O2 while avoiding the problem of secondary pollution caused by the dissolution of heavy metals [25]. Nevertheless, Zr with fully occupied 3d orbital may also realize the rapid electron transfer inside the catalyst through d0 surface electron transfer process [26]. Besides, direct electron supply can also achieve the reduction of H2O2, thereby generating active oxygen species [27], [28]. It is inferred that Zr might be able to activate H2O2 through the surface electron transfer.
To our knowledge, the activation of H2O2 is an interface reaction on the iron site in heterogeneous Fenton processes [29], [30]. And the density functional theory (DFT) calculations show that the interface energies at different crystal planes of iron oxide are different [31], [32]. It means that the association of H2O2 on the iron surface will be affected by the exposed crystal faces of the catalyst. But there are few basic researches on the structure features of Zr-Fe bimetallic catalysts. Therefore, the synergistic effect between Zr-Fe bimetals has not been fully understood.
Herein, amorphous-ZrO2 (a-ZrO2) and monoclinic-ZrO2 (c-ZrO2) were prepared and used as the components of Zr-Fe bimetals to explore the different structure features of zirconium oxides in heterogeneous Fenton processes. This study reveals the relationship between Zr-Fe bimetals structure features and H2O2 activation, and provides a new insight into strengthening the synergistic effect between bimetals. In addition, ZrO2 has a stable structure, and zirconium, as an environment-friendly metal, can also effectively avoid potential secondary pollution, which further expands the application of heterogeneous Fenton catalysts in the field of environment remediation.
Section snippets
Chemicals
Unless otherwise specified, all chemicals used in this study were of analytical grade without further purification. Ferric chloride (FeCl3), zirconium chloride (ZrCl4), bisphenol A (BPA), terephthalic acid (TA), etc. were purchased from Aladdin Industrial Corporation. And H2O2 (30 wt%) were obtained from Sinopharm chemical regent Co., Ltd. All experimental solutions and suspensions were prepared in ultrapure deionized water (18.25 MΩ cm).
Synthesis of catalysts
Solutions of FeCl3 (1.0 mol L−1, 10 mL) and ZrCl4
Structural analysis of catalysts
As can be seen from high resolution TEM images, the pristine amorphous ZrO2 (a-Zr) presents a stacked block morphology, while the monoclinic ZrO2 (c-Zr) obtained after calcination is particle of about 10–20 nm (Fig. S2). The calcined iron oxide nanoparticles are mainly α-Fe2O3 (c-Fe) (Fig. 1a), and the long-range order of the particle structure has been improved. This is mainly caused by the rearrangement of atoms in the crystal structure induced by high temperature [40]. On the other hand,
Conclusion
In view of the secondary pollution caused by the dissolution of heavy metals during H2O2 activation by traditional bimetallic catalysts, we prepared an environment-friendly Zr–Fe bimetallic catalyst in this work. However, the mechanism of the effect of Zr–Fe bimetal structure on H2O2 activation is still ambiguous. Therefore, the influence of the structure features of ZrO2 on the activation of H2O2 by Fe2O3 was also explored in this work. The surface hydroxyl of the amorphous ZrO2 in the Zr–Fe
CRediT authorship contribution statement
Yue Yin: Conceptualization, Investigation, Formal analysis, Writing – original draft & editing. Ruolin Lv: Investigation, Methodology. Xiaoyang Li: Formal analysis. Lu Lv: Investigation. Weiming Zhang: Conceptualization, Supervision, Resources, Validation, Writing – review & editing.
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
This study was financially supported by National Key Research and Development Program of China (Grant No. 2017YFE0107200).
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