Open Access Article
Hoai Linh Phamab,
Van Dang Nguyen
*c,
Van Khien Nguyenc,
Thi Hong Phong Lea,
Ngoc Bach Taa,
Do Chung Phamd,
Quoc Toan Trane and
Van Thanh Dang
*f
aInstitute of Materials Science, Vietnam Academy of Science and Technology, Hanoi, Vietnam
bGraduate University of Science and Technology, Vietnam Academy of Science and Technology, Hanoi, Vietnam
cDepartment of Physics and Technology, TNU-University of Sciences, Thai Nguyen, Vietnam. E-mail: dangnv@tnus.edu.vn
dDepartment of Physics, Hanoi National University of Education, 136 Xuan Thuy Road, Cau Giay District, Hanoi, 100000, Vietnam
eDepartment of Chemistry, Thai Nguyen University of Education, Vietnam
fTNU – University of Medicine and Pharmacy, Vietnam. E-mail: thanhdv@tnmc.edu
First published on 24th June 2021
Magnetically separable core/shell Fe3O4/ZnO heteronanostructures (MSCSFZ) were synthesized by a facile approach, and their application for enhanced solar photodegradation of RhB was studied. The formation mechanism of MSCSFZ was proposed, in which Fe3O4 nanoparticles served as a template for supporting and anchoring the ZnO crystal layer as the shells. The morphology of MSCSFZ can be varied from spherical to rice seed-like structures, and the bandgap was able to be narrowed down to 2.78 eV by controlling the core–shell ratios. As a result, the MSCSFZ exhibited excellent visible-light photocatalytic activity for degradation of rhodamine B (RhB) in aqueous solution as compared to the controlled ZnO nanoparticles. Moreover, MSCSFZ could be easily detached from RhB solution and maintained its performance after 4 cycles of usage. This work provides new insights for the design of high-efficient core/shell recyclable photocatalysts with visible light photocatalytic performance.
Over the years, a wide range of single semiconductors were used for photocatalytic technology.7 However, recently, a various type of heterogeneous photocatalysis composed by two or more semiconductors were rapidly developed to overcome draw-backs of single semiconductors as: enhancing visible photocatalytic activity with suitable band edges and improving photo-generated charge carrier separation; easy collecting in the solution.5,7–9 An alternative to benchmark TiO2, ZnO is also an well-known photocatalyst for degradation of organic pollution in aqueous media because of its higher electron mobility, longer lifetime of charge carriers, and especially in low cost and environmental friendliness.10,11 Besides, the structure–morphology of ZnO can be easily varied by wet-chemistry strategy to obtain the well-defined structures for photocatalytic and sensing applications. Although ZnO has been widely served as an efficient and low-cost photocatalyst in water remediation, however, there are some problems needed to be solved, such as (i) the fast photogenerated electron–hole recombination and (ii) the large bandgap energy of 3.37 eV, resulting in low efficiency of solar radiation absorption (from 3% to 5%); subsequently, the photocatalytic activity is unsatisfactory for the applications in industry.12
To overcome these limitations, recent efforts have been focused on modifying the electronic band structure of ZnO by doping transition/noble metals or combining ZnO with other materials to form a hybrid photocatalyst system such as low bandgap semiconductors and magnetic nanomaterials.13–15 Currently, the synthesis of heterogeneous structures between ZnO and magnetic nanomaterials has gained some interest in the field.16–18 The combination of ZnO and several spinel ferrite nanomaterials has created a new hybrid material that is capable to enhance the visible light photocatalytic efficiency and advantageous in recovery and reusability.19–22 Typically, nanoscale materials have a primary bottleneck in recovery and reuse since they are in particulate form in solution, which hinders the outstanding performance in practical industrial environment. The nanocomposites of photocatalysts with magnetic-based materials allows detaching the nanocomposites from aqueous treatment solution by simply applying an external magnetic fields. Various metal magnetic oxides, such as FeO, Fe2O3, Fe3O4 or ferrites of MFe2O4 (M = Co, Mn, Ni) are widely used for incorporating with ZnO to form the magnetically recoverable photocatalysis.23 Among the magnetic-based materials, Fe3O4 possesses the highest saturation magnetization (theoretical value of 93 emu g−1 at room temperature), superior adsorption of heavy metals, as well as the excellent ability to decompose organic pollutants.24,25 The combination of Fe3O4 and ZnO will formed a heterojuntion in which electrons and holes of two materials can be transfer to others based on the energy band position. These lead to an effective separation of photogenerated charge carrier and, in some cases, extends absorption of visible-region light.4,5,8 It is expected that the core/shell structured Fe3O4/ZnO at the nanoscale not only exhibits good magnetic separability, but also suppresses the charge carrier recombination, and achieving a narrow bandgap of ZnO for reaching visible-light-driven photocatalysis. So far, there has been much literature on fabrication of core/shell nanostructured Fe3O4/ZnO for photocatalytic applications. However, to the best of our knowledge, the previous works mainly reported on the effective degradation of organic pollutants under ultraviolet irradiation, while the visible light-driven photocatalytic performance of core/shell nanostructure is still in its fancy. Additionally, the ratio between Fe
:
Zn in hybridization is believed to tune the overall bandgap and thus enhance the photocatalytic performance. Nonetheless, there is a gap knowledge in this field due to the lack of synthesis control over Fe
:
Zn ratio. Therefore, it is imperative to comprehensively study on the effects of Fe3O4/ZnO ratio as a core/shell heterostructures for photocatalytic degradation of organic pollutants under the visible light irradiation.
In this work, we reported a facile approach to synthesize core/shell nanostructured Fe3O4/ZnO magnetic photocatalyst with tunable band gap for photodegradation of rhodamine B (RhB) under sunlight irradiation. The material properties were characterized by using SEM, TEM, UV-Vis, XRD, and Raman. By controlling the Fe
:
Zn molar ratio, different morphologies of Fe3O4/ZnO were achieved. The Fe3O4/ZnO heterostructures with the optimal core/shell Fe
:
Zn ratio showed excellent visible light photo-degradation activity of RhB. The reusability and recovery have also been demonstrated after four cycles.
:
2 were dissolved in a beaker containing 30 mL of EG–CA solution (2.56 g of CA) under vigorous stirring within 1 hour. The beaker was further added by dropwise NH4OH solution (3 M) at 90 °C until the reaction was completed (black color). The MNPs were washed with deionized (DI) water by a magnet and re-dispersed in 100 mL of EG–CA solution by sonication.
:
Zn molar ratios were prepared as 1
:
5, 1
:
10, and 1
:
20. During synthesis, the amount of Fe3O4 NPs was fixed, while the amount of ZnO varied by changing the concentration of zinc precursor. The core/shell samples with Fe
:
Zn molar ratios of 1
:
5; 1
:
10; 1
:
20 were named as Fe3O4/ZnO 1
:
5; Fe3O4/ZnO 1
:
10 and Fe3O4
:
ZnO 1
:
20, respectively.
![]() | (1) |
:
Zn molar ratios (1
:
5, 1
:
10; and 1
:
20), and ZnO samples. Obviously, the diffraction peaks of Fe3O4 NPs were observed at 2θ of 18.32°, 30.14°, 35,5°, 43.15°, 53.54°, 57.07° corresponding to the (111), (220), (311), (400), (422), (511) planes of the inverse cubic spinel structure of Fe3O4 crystal, which are well-matched with JCPDS 71-6336. The strong diffraction peaks centered at 2θ of 32.77°, 34.44°, 36.26°, 47.55°. 56.6°, 62.88°, 66.38°, 67.96°, 69.09° are indexed to (100), (002), (101), (102), (110), (103), (200), (112), (201) planes of the hexagonal wurtzite structure of ZnO crystalline (JCPDS, 71-6424). For the CSFZ, the diffraction peaks were mainly attributed to the hexagonal wurtzite structure of the ZnO phase, while the small and broad peaks observed at 2θ of 30.1°, 35.6°, and 43.2°, corresponding to the (220), (311), and (400) planes of the inverse cubic spinel structure of Fe3O4, respectively. The appearance of the characteristic peaks of both Fe3O4 and ZnO crystalline in the XRD patterns of CSFZ samples confirmed for the successful formation of Fe3O4 and ZnO heterostructure. A closer observation of the XRD patterns in the 2θ range of 28°–46° showed that the characteristic peaks of Fe3O4 phase in the heterostructure samples shifted toward smaller 2θ angles as compared with that of the original one (Fig. 1b), while the diffraction peaks of the ZnO shell were still unchanged. According to Bragg's law, the shift in diffraction peaks to lower 2θ can be related to the increase in lattice strain, implying the significant expansion of the Fe3O4 crystal distance in the heterostructure samples. This is due to the hybridization of core/shell at the interface as a result of the formation of core/shell structure that ZnO shell was grown on the surface of Fe3O4 core.26 The average crystallite size was performed by X'pert Highscore Plus and shown in Table 1. The calculated results are in good agreement with the above mentioned findings.
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| Fig. 1 XRD diffraction of (a) the as-prepared samples; (b) the enlarged XRD patterns of samples with 2θ angle in the range of 28–45°. | ||
| Samples | d220 (Fe3O4) | DXRD (nm) | Morphology | DFESEM (nm) | |
|---|---|---|---|---|---|
| Fe3O4 core | ZnO shell | ||||
| Fe3O4 | 2,95 164 |
12.8 | — | Spherical | 15.8 |
Fe3O4/ZnO 1 : 5 |
2,96 648 |
10.86 | 19.8 | Nearly spherical | 39 |
Fe3O4/ZnO 1 : 10 |
2,97 249 |
10.34 | 20.1 | Rice seed-like | W: 42; L: 96 |
Fe3O4/ZnO 1 : 20 |
2,97 513 |
11.6 | 22.03 | Rice seed-like, rods | W: 40; L: 139 |
| ZnO | — | 36.49 | Nearly spherical | 87 | |
The FE-SEM was used to investigate the morphological features of all samples. As shown in Fig. 2a, the pristine Fe3O4 NPs display a uniform spherical shape with an average size of 15.8 nm, thus making them well-dispersed in the EG–CA solution. After being covered by the ZnO shell, the morphology and size of CSFZ (Fig. 2b–d) changed drastically compared to the pristine Fe3O4 NPs. At Fe/Zn ratio of 1
:
5, the core/shell heterostructure retained nearly spherical morphology with a wide size distribution, and the average particle size was estimated to be 39.8 nm. As increasing the Fe
:
Zn ratios up to 1
:
10 and 1
:
20, the morphology changes from spherical shape of core/shell structure to rice seed-like structure (Fig. 2c and d). The rice seed-like shaped nanostructures with an average size of 42 nm in diameter and 6 nm in lengths were observed for the Fe3O4/ZnO 1
:
10 sample. For the Fe3O4/ZnO 1
:
20 samples, the formation of the nano rod-like structure of CSFZ was seen with average lengths of 139 nm. It should be noted that all samples were synthesized in the same experimental conditions with the same amount of Fe3O4 core, meanwhile the ZnO shell content varied by adjusting zinc precursor concentration. Thus, the structural evolution of the CSFZ is assigned for the formation of ZnO shell, suggesting the Zn content is crucial for designing the desirable structure. As comparison for ZnO NPs, they displayed a spherical shape with an average diameter size of 87 nm, which is larger than Fe3O4 NPs (Fig. 2e). To further analyze the elemental composition, EDS analysis was carried out on the Fe3O4/ZnO 1
:
5 and Fe3O4/ZnO 1
:
20 samples (Fig. 2f). The results revealed that the core/shell nanostructured Fe3O4/ZnO included O, Fe, and Zn elements, in which the atomic ratio of Zn to Fe in the EDS spectrum of Fe3O4/ZnO 1
:
20 sample was higher than that of Fe3O4/ZnO 1
:
5 sample. It confirmed that the Fe3O4/ZnO heterostructures with controlled core–shell ratio was successfully synthesized by the proposed method.
To gain further insight into the evolution of CSFZ, HR-TEM images of samples with Fe
:
Zn molar ratio of 1
:
5, 1
:
10 and 1
:
20 were shown in Fig. 3. TEM images shows the features of the core–shell structure formation, in which Fe3O4 core is dark and ZnO shell is light (different brightness). From HR-TEM images, different lattice fringes were observed in the center and the edge region of a particle, suggesting the existence of a crystalline core/shell structure. The lattice spacing of the core and shell correspond to (311) and (222) plane of Fe3O4 crystal, and (200) and (102) of ZnO crystal. In addition, the selected area electron diffraction (SAED) images presented the ring patterns of the polycrystalline sample with the lattice spacing of 4.81, 2.98 and 2.53 Å, corresponding to the Fe3O4 (111), (220), Fe3O4 (311) reflections, respectively. The lattice spacing of ZnO (002) is also expected to 2.61 Å. These results suggested that the core/shell Fe3O4/ZnO were well formed in spherical shape at a low Fe
:
Zn ratio, meanwhile, the ZnO peculates tended to link together to form rice-like or nanorod structures at relatively high Fe
:
Zn ratios. The mechanism for the structural formation of core/shell Fe3O4/ZnO heterostructure is proposed as follows: during reaction at second step of sol–gel process, Zn2+ ions absorbed on the surface of Fe3O4 nanoparticles under the linking of surface connecting agents (DEG and EG–CA) and growth as ZnO crystal shell to form the Fe3O4/ZnO core–shell particles. When increasing the ZnO shell ratio, the more amount of Zn2+ ions continue growth on surface of Fe3O4 NPs and tended to link together to form nanorod structures.
To gain in-depth understanding about the chemical bonding and vibration, the FTIR analysis of prepared samples was carried out. Fig. 4 presents the FTIR spectra of Fe3O4 NPs, ZnO NPs and CSFZ with different Fe
:
Zn molar ratio of 1
:
5, 1
:
10, and 1
:
20. The stretching vibration modes on the FTIR spectra were generally categorized into three wavenumber regions. (i) The stretching vibration modes observed in the wavenumber region from 400 to 900 cm−1 correspond to metal–oxygen bonds, which could confirm metal oxide formation. For the pristine Fe3O4 and ZnO NPs, the bands located at 628–584 and 534–450 cm−1 were ascribed to Fe–O bond and Zn–O bond, respectively.27,28 Next, the region with wavenumber from 1000 to 1700 cm−1, the absorption band centered at 1625 cm−1 was attributed to the bending vibration of O–H bond, which is belongs to H2O molecules presented in samples. Moreover, the stretching vibrations of the intermediates or residual products, for instance, CH3COO… can be found at 1524, 1419, and 1362 cm−1.20,29 Last, the absorption bands obtained in the region from 2000 to 3700 cm−1 were related to the O–H stretching vibration (3385 cm−1) and C–O stretching modes (2358–2337 cm−1) due to the existence of undesired CO2 in the sample during measurements.30 Focusing on the low wavenumber region, as shown in Fig. 4b, the absorption peaks assigned to Fe–O bonds and Zn–O bonds in core/shell samples shifted to lower wavenumbers compared with those of pure Fe3O4 and ZnO NPs. The peak shift revealed that the successful introduction of ZnO NPs on surface of Fe3O4 NPs to form a core/shell structure, thus requiring the higher energy and resulting in the change of bond length and energy. In addition, a new absorption mode was found at 692 cm−1 in core/shell samples, which is associated to the incorporation Fe into the Zn–O lattice due to the hybridization of Fe3O4 core and ZnO shell at the core–shell interface and similar to previous scholarly publications.31–33 In terms of peak intensity located at 692 cm−1, the core/shell Fe3O4/ZnO 1
:
5 exhibited the strongest and sharpest among these compared samples, which further confirms the better core/shell formation at a low precursor Fe
:
Zn ratio. To verify this unique feature, we employed Raman spectra and their results are shown in Fig. 5. The peaks observed at 99.6, 338 and 439 cm−1 were assigned to the E2 (low) mode, A1 (TO) mode E2 (high) mode of ZnO NPs, which is consistent with the previous study.34 The broad peak centered at 664 cm−1 was attributed to A1g mode corresponding to the symmetric stretch of oxygen atoms along Fe–O bonds in Fe3O4 NPs. It is well-known that E2 (high) and E2 (low) modes in ZnO NPs corresponded to the vibrations of oxygen atoms and Zn sub-lattice, respectively.35 Evidence by the previous work of Morozov et al., the alter in Raman peak intensity of E2 (high) and E2 (low) related to the defects on the ZnO side of the interface.35 Karamat et al. revealed that the intensity of the E2 (low) mode decreased due to phonon vibrations of the existence of Fe dopant.36 Thus, the decreasing of the intensity of E2 (high) and E2 (low) mode observed in Raman spectra of core/shell heteronanostructures confirm again the hybridization of Fe3O4 core and ZnO shell with the Fe ions incorporated in the ZnO crystal lattice at the interface of core–shell. Taken the above discussion, it is strongly confirmed that core/shell nanostructured Fe3O4/ZnO was successfully prepared.
![]() | ||
| Fig. 4 (a) FTIR spectrums of as-prepared samples and (b) the enlarged spectra with wavenumber in the range of 800 cm−1 to 400 cm−1. | ||
![]() | ||
Fig. 5 Raman spectra of Fe3O4 nanoparticles and Fe3O4/ZnO heterostructures with different Fe : Zn molar ratio. | ||
To further study the surface composition of CSFZ, XPS measurement was conducted for Fe3O4/ZnO 1
:
5 sample and shown in Fig. 6. From XPS survey spectra of 1–5 sample in Fig. 6a, it can be found that the C, O, Fe and Zn elements coexisted in the sample and the intensity of peak represents for the ZnO phase (Zn 2p) is much larger than that for the Fe3O4 phase (Fe 2p), revealing the formation of the Fe3O4/ZnO core–shell nanostructure with the elemental signals from the ZnO shell are much stronger than those from the deeper core of Fe3O4 in the sample. The high-resolution Fe 2p spectrum (Fig. 6b) shows main peak at 710.64 eV which could be attributed to Fe 2p3/2 of Fe2+ spcies, two other main peaks at 724.2 eV and 713.08 eV were correspond to Fe 2p1/2 and Fe 2p3/2 of Fe3+ species.37 There is a satellite peak observed at 717.79 eV, confirming the presence of high crystalline Fe3O4 in the samples.38 As shown in the high resolution Zn 2p spectrum (Fig. 6c), two main peak of ZnO centered at 1021.58 eV and 1044.58 eV corresponding to Zn 2p3/2 and Zn 2p1/2, suggesting the existence of ZnO.39 Interestingly, a strong satellite structure was observed in both of Fe 2p and Zn 2p. The reason for the increasing intensity of satellite peaks is most likely due to the defects found in core–shell systems resulting from the interaction between Fe3O4 core and ZnO shell. The incorporation of Fe ion or Zn ion at interfaces creates a greater defect density would increase conductivity within the particle, which in turn, could boosting shake-up processes that lead to a strong satellite structure,34 confirming the hybridization between Fe3O4 and ZnO phase in the heterostructures. Additionally, O1s spectrum (Fig. 6d) can be fitted by the Gaussian function with the coincidence of 3 peaks distributed at binding energy of 529.7 eV, 532.26 eV, and 533.75 eV which able to assigned respectively, to metal–O bonds (Fe–O bonds, Zn–O bonds); oxygen defects and oxygen adsorbed on the surface of samples including O2, hydroxyl (OH−) and carbonate (CO23−) groups (O2−).40,41
![]() | ||
Fig. 6 (a) XPS survey spectra and (b) high-resolution XPS spectra of Zn 2p for Fe3O4/ZnO 1 : 5 samples; (c) high-resolution XPS spectra of Fe 2p and (d) O1s for Fe3O4/ZnO 1 : 5 sample. | ||
![]() | ||
Fig. 7 (a) (a) UV-Vis spectra and (b) PL spectra of Fe3O4 NPs, Fe3O4/ZnO heterostructures with different Fe : Zn molar ratio: 1 : 5; 1 : 10; 1 : 20. | ||
For further understanding optical properties of the core–shell heterostructures, bandgap values and the possible charge transfer mechanism were explored. The band gap (Eg) was estimated by employing the Kubelka–Munk equation.49 Fig. 8 show the curves of (F(R∞)hv)2 versus (hv) of ZnO NPs and core/shell Fe3O4/ZnO 1
:
5, 1
:
10 and 1
:
20. The band gap of samples was obtained by extrapolating the linear portion of the (F(R∞)hν)2 versus (hν) curve to F(R∞) = 0. The bandgap of Fe3O4/ZnO 1
:
5 is 2.75 eV, which is lower than those of Fe3O4/ZnO-1
:
20 (2.85 eV) Fe3O4/ZnO 1
:
10 samples (2.81 eV), ZnO NPs (3.26 eV) and Fe3O4 (1.81 eV). The decreasing in band gap energy of CSFZ with increasing Fe3O4 core ratio indicated that the visible light adsorption greatly enhanced, which is benefit for the high-efficiency in visible light-driven photocatalytic performance.46 This is explained that the unique small core/shell heterostructure and their coupling between Fe3O4 and ZnO. Based on the calculated bandgap values of Fe3O4 and ZnO samples, the band edge positions of the valence band (EVB) and conduction band (ECB) potentials of Fe3O4 core nanoparticles and ZnO shell were estimated by the empirical formula:50
![]() | (2) |
![]() | (3) |
:
5 samples was fast and outperformed over the Fe3O4/ZnO 1
:
10, Fe3O4/ZnO 1
:
20 samples and ZnO NPs. The Fe3O4/ZnO 1
:
5 exhibited the highest RhB removal efficiency at 150 min under the sunlight irradiation. Moreover, without photocatalyst, RhB self-degradation under solar light irradiation can be neglected. The enhanced photocatalytic properties in core–shell heterostructures can be governed by two main physicochemical features: (i) low recombination rate of photogenerated charges compared with the charge transfer rate to the surface-bound redox reactions; and (ii) low bandgap energy is provided the material with the ability to absorb a wide range of light in the visible region. As shown in Fig. 11, after reaching the adsorption/desorption equilibrium, the adsorption capacity toward the organic pollutant of all samples was not significantly different. This result implied that the enhanced photocatalytic performance of the core–shell Fe3O4/ZnO samples was affected by the remaining two factors. The recombination behaviors of the photogenerated electron–hole pairs in the core–shell Fe3O4/ZnO samples were characterized by PL spectra. As shown in Fig. 7b, the PL emission intensity of core/shell samples significantly decreased with increasing Fe3O4 core ratio, the weakest PL emission was found in Fe3O4/ZnO 1
:
5 sample. These results reveal that Fe3O4/ZnO 1
:
5 sample is more effective in improving charge carrier transfer and separation than those of Fe3O4/ZnO 1
:
10 and 1
:
20 because the PL emission intensity is proportional to the photo-induced electron–hole recombination rate.50,52 It can be explained that the recombination of photogenerated charge carriers in core–shell samples was effectively suppressed by coupling of Fe3O4 core and ZnO shell with the presence of the impurities of Fe ions incorporated to ZnO lattice at the interface region. According to the work done by Liu et al., the incorporation of Pt2+ ions into α-Fe2O3 photocatalyst induced the formation of Schottky barrier at the interface between two phase of the nanocomposites that can effectively improve charge carrier separation and hinder carrier recombination.50 As mentioned in the FTIR results, the addition of Fe ions into the ZnO lattice in Fe3O4/ZnO 1
:
5 sample is larger than that in Fe3O4/ZnO 1
:
10 and 1
:
20 samples, which produce more capturing sites to facilitate the separation efficiency of photogenerated carriers. The energy level of the conduction band of ZnO was higher than the Fermi level of Fe3O4, and photogenerated electrons in the conduction band of ZnO were quickly transferred from ZnO shells to the core.53 Thus, the buffer region acted as a reservoir for the photoelectrons and extended the lifetime of the photogenerated charges due to the reduction of Fe+3 to Fe+2.21,54 Thus, the enhanced photocatalytic activity can be achieved in the core–shell Fe3O4/ZnO nanocomposite, especially in the sample with a core–shell ratio of 1
:
5.
![]() | ||
Fig. 10 Absorption spectra of the RhB solution as a function of sunlight irradiation time in the presence of Fe3O4/ZnO heterostructures with different Fe : Zn molar ratio (1 : 5; 1 : 10 and 1 : 20). | ||
It is well known that the photocatalytic process to degrade organic pollutants involved three reactions: (i) generating electrons and hole at conduction band and valence band of photocatalyst by light absorption; (ii) electrons and hole move to the surface of photocatalyst and take reaction with O2 and H2O absorbed on photocatalyst's surface to create reactive species; (iii) reactive species will degrade organic pollutants through strong oxidation and reduction reaction.
As shown in Fig. 9, it can be seen that the potential of conduction band of ZnO is more negative than the O2/O2%− potential (−0.33 eV vs. NHE). Thus, photogenerated electrons can react with O2 in the solution to generate O2−. Additionally, photoinduced h+ also can react with H2O or hydroxyl group on the surface of photocatalyst to produce ˙OH because the position of valance band potential for ZnO is larger than the standard redox potential of OH (2.7 eV vs. NHE). According to recently reports by Han et al., O2−. ˙OH and h+ were found as the main oxidizing species for the photocatalytic process of the ZnO-based composites.55,56
:
5 and 1
:
20) measured at 300 K. The saturation magnetization values for Fe3O4 NPs, Fe3O4/ZnO 1
:
5, and Fe3O4/ZnO 1
:
20 were 61, 17.4, and 5.2 emu g−1, respectively, which is still comparable to the reported values in the ref. 16, 19 and 53. The reduction of saturation magnetization in core/shell samples was due to the non-magnetic phase of ZnO shell. Interestingly, Fe3O4/ZnO 1
:
5 could be effortlessly separated and detached from solutions containing RhB by applying an external magnetic field (inset in Fig. 12a). Reusability is an essential feature of composites for organic pollutant photodegradation in practice. The recycling and sustainability of Fe3O4/ZnO 1
:
5 were further evaluated with four continuous cycles (Fig. 12b). For each cycle, the photocatalyst in solution was rapidly separated by a magnet with surface magnetic field strength of 4 kOe. The solar light photocatalytic activities of sample remained good after four recycles. These results showed that core/shell Fe3O4/ZnO heteronanostructure could be an excellent candidate for practical wastewater treatment.
:
5. In comparison with ZnO NPs, the core–shell nanocomposites showed the higher sunlight photocatalytic activity. Efficient sunlight harvesting and reduced photogenerated electron–hole recombination rate should be the main factors to enhance the sunlight photocatalytic performance of Fe3O4/ZnO nanocomposites. Our results revealed that core–shell Fe3O4/ZnO heterostructure with Fe
:
Zn molar ratio is 1
:
5 showed an excellent sunlight photocatalytic performance, efficient magnetic separation, and recyclability during four cycles. Therefore, this photocatalysts can be excellent candidate for visible-light-driven photocatalysis applications.
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