Although spinel ferrite (MFe2O4, M = Zn, Ni, Mn, etc.) has been reported as a promising catalyst, its low photocatalytic activity under visible light greatly restricts its practical application. Spinel ferrite-based photocatalytic composites have exhibited improved efficiency for pollutant degradation, due to interface charge carrier mobility and structural modification. Meanwhile, due to its magnetism and stability, spinel ferrite composite can be easily recycled for long-term utilization, showing its high application potential. In this review, the recent advances in the construction and photocatalytic degradation of spinel ferrite composites are discussed, with an emphasis on the relationship between structural property and photocatalytic activity. In addition, to improve their photocatalytic application, the challenges, gaps and future research prospects are proposed.

  • The development of spinel ferrite-based photocatalysts was reviewed.

  • The heterojunction of spinel ferrite and other photocatalysts was reported.

  • The preparation processes of photocatalytic heterojunctions were summarized.

  • The mechanism of photocatalytic heterojunctions was illustrated and compared.

  • Future research suggestions were proposed.

Graphical Abstract

Graphical Abstract
Graphical Abstract

In recent years, the heavy consumption of organic compounds, such as organic dyes, phenols, and pharmaceuticals, has resulted in large amounts of debris in the natural aquatic environment, originating from industrial effluents (Shao et al. 2021). The increased discharge of organic pollutants has aroused considerable attention worldwide, due to their threat to human health (Rodriguez-Mozaz et al. 2015). This environmental issue has been considered a tough problem that urgently needs to be addressed since conventional treatment methods can hardly eliminate these pollutants due to their stable molecular structure (Agunbiade & Moodley 2016). Advanced oxidation processes have been reported as an effective route to eliminate these refractory compounds (Michael-Kordatou et al. 2018), and among various processes, photocatalysis has attracted large attention (Xing et al. 2018; Zhu et al. 2022). The main reason is its green and eco-friendly features: no requirement of fossil energy and chemical reagents (only solar energy), the conversion of toxic organic compounds into less toxic intermediates, and eventually inorganic substances (Nair et al. 2021).

Most reported photocatalysts are in powder form, which requires an additional process to collect them from water (Arora et al. 2021). The high cost of recycling photocatalysts greatly restricts its practical application potential. Because of this, spinel ferrite has been introduced to the photocatalytic system due to its magnetic property, which ensures high recycle performance via magnetic separation (Shah et al. 2022). However, its low photocatalytic activity under visible light greatly restricts its practical application.

The key factor of a photocatalyst is its band gap structure, which determines the wavelength of absorbing light (Acharya et al. 2022). The distance between the valence band (VB) and conduction band (CB) is defined as band gap energy (E, eV), which is closely related to the wavelength (λ, nm) of light (E = 1,240 eV nm/λ) (Ajeesha et al. 2021). Figure 1(a) presents the solar spectrum that illustrates the intensity of light reaching the Earth's surface, ranging from ultraviolet (UV), and visible light to infrared (IR) (Casbeer et al. 2012). UV merely accounts for 5% while visible light takes up 46% of entire solar energy, leaving the rest part corresponding to IR. Many reported photocatalysts have band gaps wider than 3.1 eV, which enables them to absorb a tiny portion of solar light (Melki et al. 2021). Thus, as for photocatalysts, it is essential to utilize visible light (visible solar energy). This requires the photocatalyst with band gap energy below 3.1 eV. One method is the fabrication of material with a narrow band gap, which enables the absorption to visible light. It is reported that spinel ferrite has a band gap value of around 2.0 eV, such as ZnFe2O4 (Boumaza et al. 2010), NiFe2O4 (Meinert & Reiss 2014) or MnFe2O4 (Mary Jacintha et al. 2015). However, two factors restrict its photocatalytic application. First, during irradiation, the recombination of photo-induced charge carriers is very high. This leads to rather low photo quantum yield and limited photocatalytic activity (Sonu et al. 2021). Second, spinel ferrite can hardly achieve photo-oxidation and photo-reduction simultaneously (Suresh et al. 2021), yet this is essential for the complete degradation of organic pollutants, as well as full absorption of visible light. In other words, the redox potential (vs. NHE) for the formation of reactive oxygen species is −0.33 V for (photo-reduction) (Liu et al. 2021) and +2.30 V for •OH (photo-oxidation) (Zhang et al. 2021), which requires the photocatalyst to have its VB more positive than +2.30 V while its CB potential is more negative than −0.33 V. The band structure of spinel ferrite can't fulfill this requirement. In fact, only a few wide band gap photocatalysts such as TiO2 and ZnO are qualified; however, they only respond to UV light.
Figure 1

(a) Sunlight spectrum (Casbeer et al. 2012); (b–e) band structures and charge carrier migration directions in the (b) Z-scheme, (c) type-I, (d) type-II, and (e) type-III heterojunction (Li et al. 2021); (f–h) demonstration of three types of spinel ferrite: (f) normal spinel (MgAl2O4), (g) inverse spinel (NiFe2O4) and (h) complex spinel (CuAl2O4) (Qin et al. 2021).

Figure 1

(a) Sunlight spectrum (Casbeer et al. 2012); (b–e) band structures and charge carrier migration directions in the (b) Z-scheme, (c) type-I, (d) type-II, and (e) type-III heterojunction (Li et al. 2021); (f–h) demonstration of three types of spinel ferrite: (f) normal spinel (MgAl2O4), (g) inverse spinel (NiFe2O4) and (h) complex spinel (CuAl2O4) (Qin et al. 2021).

Close modal

In order to overcome both restrictions, the construction of a photocatalytic composite with two or more semiconductors has been intensively studied, and the enhanced photocatalytic performance is ascribed to the appropriate band alignment. Figure 1(b)–1(e) presents four different band alignment strategies. Figure 1(c) presents type-I heterojunction (straddling-gap junction) (Jabbar et al. 2023), in which the photo-induced e and h+ from photocatalytic semiconductor II (PS II) all migrate to photocatalytic semiconductor I (PS I). This accumulates the recombination of charge carriers, leading to reduced photocatalytic activity. Figure 1(d) presents a type-II heterojunction (staggered-gap junction), in which photo-induced e and h+ migrate to relatively lower energy bands (Jiang et al. 2022). This hinders the recombination of charge carriers and improves photocatalytic activity, yet reduces the total redox ability since charge carriers end up gathering in bands with low energy potentials. Figure 1(e) presents a type-III heterojunction (broken-gap junction), in which photo-induced charge carriers stay in the original PS bands without interface migration (Li et al. 2022b). This makes no contribution to photocatalytic efficiency since there is no interaction and synergy between PS I and PS II.

Figure 1(b) presents a special case of heterojunction similar to staggered-gap junction (type-II, Figure 1(d)), that is, Z-scheme heterojunction (Liu et al. 2022b). In this scenario, e in PS II moves toward PS I, meanwhile, h+ in PS I moves toward PS II, until both charge carriers recombine, leaving e with high reductive potential at the CB of PS I and h+ with high oxidative potential at the VB of PS II. Z-scheme heterojunction preserves the high redox ability of charge carriers, which is beneficial to the complete degradation of organic pollutants. In conclusion, staggered-gap junction (type-II) and Z-scheme heterojunction are promising strategies for improving photocatalytic activity, especially Z-scheme photocatalytic heterojunction composites.

The general molecular formula of spinel ferrites is MFe2O4, where M stands for divalent ions, such as Ni2+, Zn2+, Mn2+ (Dasgupta et al. 2016). There are three types of spinel based on the difference in crystal structure: normal spinel, inverse spinel, and complex spinel (Zhao et al. 2017). As for normal spinel (Figure 1(f)), such as ZnFe2O4, Zn2+ and Fe3+ are located at tetrahedral and octahedral sites, respectively (Li et al. 2019). As for inverse spinel (Figure 1), such as NiFe2O4, Ni2+ and half of Fe3+ occupy octahedral sites, and the other half of Fe3+ occupies tetrahedral sites (Nawaz et al. 2020). As for complex spinel (Figure 1), such as MnFe2O4, Mn2+, and Fe3+ randomly occupy tetrahedral and octahedral sites, and 20% of Mn2+ ions occupy octahedral sites and 80% of Mn2+ ions occupy at tetrahedral sites (Kefeni et al. 2017).

The keyword analysis of reported scientific literature works helps to describe topic(s) in a specific research area. As for all published papers, the authors generally set a list of keywords to describe the main focus of their work, as well as the essential concepts. Sometimes editors and reviewers also added more keywords based on the corresponding research field(s), which ends up with hundreds of keywords related to a certain research field (Padilla et al. 2018). VOSviewer software provides the option to choose keywords from all sources, including authors and publishers.

As for spinel ferrite, the Web of Science core collection database included 4,027 papers published over the past 5 years (from 2018 to 2022). By processing these data via VOSviewer, the network visualization map (Figure 2) was obtained. The map was divided into six clusters, separated by various colors. The keywords in the same cluster have closer links. The node size of a certain keyword reflects the use count of that keyword, and the line weight reflects the co-occurrence between two keywords.
Figure 2

The keyword occurrence network visualization map in the field of spinel ferrite.

Figure 2

The keyword occurrence network visualization map in the field of spinel ferrite.

Close modal

The terms ‘synthesis’ and ‘structural’ are the most used keywords. Both keywords are highly related to the physicochemical properties, which affect its photocatalytic property. Thus, in this review, the connections between the synthesis method, structural property and photocatalytic activity are discussed.

In recent decades, nano-sized spinel ferrites have been intensively studied, especially their catalytic application in the environmental remediation field (Li et al. 2004). Compared with bulk materials (large-sized), nanoparticles exhibit superior catalytic performance, optical properties, and chemical stability (Du et al. 2016). These advantages make nano-sized spinel ferrite a suitable catalytic material for practical application (Rostami et al. 2013). Especially, nanoscale spinel ferrite exhibits superparamagnetic properties, which enables spinel ferrite-based composite to be easily recycled via external magnet (Nadimi et al. 2019). However, the disadvantages of pristine spinel ferrite restrict its catalytic activity: high agglomeration and rapid charge carrier recombination (Zhu et al. 2019). To address these problems, a great many types of research have been conducted on developing spinel ferrite-based composites with high photocatalytic activity (Chandrasekaran et al. 2018; Qin et al. 2021). This paper aims at providing a timely and systematical review of the design and photocatalytic degradation of spinel ferrite (ZnFe2O4, NiFe2O4 and MnFe2O4)-based composites, offering an inspiring and useful discussion on the relationship between structural property and photocatalytic activity, as well as future research suggestions.

Although spinel ferrite has been considered a promising catalyst, the low photocatalytic activity under visible light greatly restricts its practical application (Gebreslassie et al. 2019; Leonel et al. 2021). One of the reported methods to develop high-performance photocatalysts is the combination of photocatalysts with functional materials (Fouad et al. 2021). Carbon-based materials, such as graphene and graphitic carbon nitride (g-C3N4), are described as follows.

Spinel ferrite/graphene

As one of the forms of carbon, graphene presents a unique crystal structure, which endows it with different properties. In 2004, Novoselov et al. reported the two-dimensional morphology of graphene, as well as its astonishing electric field effect (Novoselov et al. 2004). In 2010, Geim and Novoselov were awarded the Nobel Prize in Physics, due to their outstanding contribution to the research field of graphene (Li et al. 2022a). Because of its ultrahigh tensile strength and specific surface area, abundant surface functional groups, excellent electronic and thermal conductivity, and superior chemical and thermal stability, graphene has been intensively studied in the fields of electronics, electric batteries, semiconductor and composite (Yu et al. 2020). In recent years, graphene has been used as the carrier of various photocatalysts (Dutta et al. 2019). In this section, the main preparation methods of spinel ferrite and its graphene-based composite are discussed, and the brief information of these papers is summarized in Table 1.

Table 1

Summarized information of spinel ferrite/graphene photocatalysts

PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4@graphene nanosheets Hydrothermal method Congo red; 15 mg L−1 300 W Xenon lamp, 2.0 W cm−2; 0.5 g L−1 88.66%/240 min Jiang et al. (2020)  
NiFe2O4@graphene oxide Sol–gel auto-combustion method Methylene blue; 0.04 mM 10 W UV lamp (λ = 254 nm); 0.5 g L−1; pH = 10 90.84%/150 min Bayantong et al. (2021)  
MnFe2O4/reduced graphene oxide Co-precipitation method Methylene blue; 10 mg L−1 UV lamp (λ = 365 nm, Intensity = 40 W); 0.3 g L−1 97.00%/60 min Mandal et al. (2020)  
PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4@graphene nanosheets Hydrothermal method Congo red; 15 mg L−1 300 W Xenon lamp, 2.0 W cm−2; 0.5 g L−1 88.66%/240 min Jiang et al. (2020)  
NiFe2O4@graphene oxide Sol–gel auto-combustion method Methylene blue; 0.04 mM 10 W UV lamp (λ = 254 nm); 0.5 g L−1; pH = 10 90.84%/150 min Bayantong et al. (2021)  
MnFe2O4/reduced graphene oxide Co-precipitation method Methylene blue; 10 mg L−1 UV lamp (λ = 365 nm, Intensity = 40 W); 0.3 g L−1 97.00%/60 min Mandal et al. (2020)  

The first one is the hydrothermal method, which uses water as medium and requires high temperature (100–300 °C) at high pressure (1–30 MPa) in a confined container to produce nanocrystals (Soufi et al. 2021). This is currently the most widely used preparation method. At these extreme conditions, all precursors (metal ions) in water acquire high energy, which greatly accelerates the crystallization process (Narang & Pubby 2021).

Jiang et al. prepared ZnFe2O4 supported on graphene nanosheets (ZnFe2O4@GNs) via the hydrothermal method (Figure 3(a)), with a crystallite size of 30 nm (Jiang et al. 2020). ZnFe2O4@GN exhibited a higher removal rate of the dye Congo red under simulated sunlight, compared with pristine ZnFe2O4. The SEM image of graphene (Figure 3(b)) showed its nano-sheet structure, while the image of ZnFe2O4@GNs (Figure 3(c)) exhibited the dispersed distribution of ZnFe2O4 nanoparticles on the surface of graphene. In other words, during the fabrication period, graphene hindered the agglomeration of ZnFe2O4 nanoparticles, which was a negative effect leading to the low specific surface area. This resulted in enhanced adsorption ability toward aqueous pollutants (Figure 3(e)). The second function of graphene is its wide absorption range and high absorption intensity toward visible light (Figure 3(d)), which greatly enhances the light absorption ability of binary composite. The third function of graphene is its high stability. After four cycling tests, the photodegradation efficiency of pristine ZnFe2O4 dropped dramatically, yet the composite still exhibited good performance. The combination of graphene did not affect the magnetic recycling process (Figure 3(g) and 3(h)). The fourth function of graphene is prolonging the lifetime of photo-induced charge carriers, due to its good electronic conductivity. Figure 3(i) depicts the photocatalytic mechanism of binary composite, implying its enhanced adsorption ability and charge carrier separation efficiency. In conclusion, the above four functions of graphene greatly improved the photocatalytic performance of ZnFe2O4. During the hydrothermal period, the following factors affect the structural property of obtained semiconductor: the heating rate, temperature, and reaction time (Nhlapo et al. 2021). Sometimes, organic solvents also act as reaction media instead of water, and this route is called the solvothermal method (Manohar et al. 2021).
Figure 3

(a) Schematic illustration for the ZnFe2O4@GNs hydrothermal preparation route; (b) SEM image of graphene nanosheets (GNs); (c) SEM image of ZnFe2O4@GNs; (d) UV-visible light absorption spectra of various catalysts; (e) adsorption comparison of Congo red using various catalysts; (f) the recycle test performance for four successive turns; (g and h) before and after the magnetic recovery; (i) possible mechanism of decolorization of CR over ZnFe2O4@GNs under simulated solar light (Jiang et al. 2020).

Figure 3

(a) Schematic illustration for the ZnFe2O4@GNs hydrothermal preparation route; (b) SEM image of graphene nanosheets (GNs); (c) SEM image of ZnFe2O4@GNs; (d) UV-visible light absorption spectra of various catalysts; (e) adsorption comparison of Congo red using various catalysts; (f) the recycle test performance for four successive turns; (g and h) before and after the magnetic recovery; (i) possible mechanism of decolorization of CR over ZnFe2O4@GNs under simulated solar light (Jiang et al. 2020).

Close modal

Another preparation strategy is the sol–gel auto-combustion method, which also uses metal ions as precursors. During the preparation period, metal salts are fully dissolved into water or ethanol by vigorous stirring, under alkaline conditions (Bhandare et al. 2020). After several hours, the obtained gel is heated (dehydrated, 80–90 °C) and calcinated at 450–800 °C (Bhandare et al. 2020).

Luna et al. immobilized NiFe2O4 nanoparticles onto graphene oxide (GO) via this method, denoted as NiFe2O4@GO, which exhibited superior photocatalytic degradation toward dye methylene blue compared with pure NiFe2O4 (Bayantong et al. 2021). This result was also ascribed to the excellent electric conductivity and adsorption ability of GO. As one derivative of graphene, GO also had four functions to enhance the catalytic activity of spinel ferrite. However, this composite only exhibited photocatalytic activity under UV irradiation, only a tiny part of sunlight energy. The substrate GO cannot alter the band structure of NiFe2O4, and thus cannot extend its light absorption range. This greatly restricted the practical application of NiFe2O4@GO. It is suggested that visible-light-driven component should be introduced to extend the light response range of NiFe2O4. The key factor during sol–gel auto-combustion is the calcination temperature, which affects the particle size and crystallinity (Khalid et al. 2021).

The third preparation strategy is the co-precipitation method, which utilizes metal precipitation as the precursor. The precipitation is formed by mixing two or more metal ions in a solution. The precipitation is then calcinated to obtain spinel ferrite (Rabi et al. 2021).

Bidisha et al. decorated MnFe2O4 onto reduced GO (MnFe2O4/rGO) via this method (Mandal et al. 2020). The sphere-like MnFe2O4 nanoparticles were well-dispersed onto rGO nanosheets with reduced agglomeration, which improved the surface condition of MnFe2O4/rGO. MnFe2O4/rGO presented higher photodegradation efficiency toward methylene blue, much better than that of bare MnFe2O4. As another derivative of graphene, rGO also exhibited four functions to enhance the catalytic activity of spinel ferrite. The limitation of this work is also the utilization of UV light, which restricted its practical application. Various factors affect the structural properties (particle size and shape) of spinel ferrite during the co-precipitation process: salt precursor, solution medium, temperature, pH and extra surfactant (Haneef et al. 2021).

Different preparation methods have unique advantages and disadvantages. As for the hydrothermal method, due to the extreme conditions, the obtained product often exhibits controlled particle size, morphology and nanocrystal dispersion. However, this method also has its shortcomings, such as relatively low output amount and safety of production equipment (Zhu et al. 2021). As for the sol–gel auto-combustion method, the product often has good uniformity and purity; however, the fabrication conditions are highly uncontrollable, and unwanted byproducts are formed (Khalid et al. 2021). As for the co-precipitation route, it has been considered a facile and cost-effective method for spinel ferrite fabrication, however, currently, the obtained products exhibit poor crystallinity (Rabi et al. 2021). This method has great potential for the development of large-scale production, once this problem can be addressed (Soylak et al. 2021).

Although graphene and its derivatives have many functions to improve the photocatalytic performance of spinel ferrite, they can't change its light response range, in other words, NiFe2O4 or MnFe2O4 still can't be activated by visible light after immobilized onto these substrates. These spinel ferrites should combine other semiconductors and form a heterojunction composite to extend their light absorption range and realize high solar light utilization.

Spinel ferrite/g-C3N4

Wang et al. reported for the first time that graphitic carbon nitride (g-C3N4) exhibited visible-light-driven photocatalytic activity (Wang et al. 2009). Due to its fascinating properties, g-C3N4 is a promising n-type semiconductor, with abandgap of 2.7 eV (Balakrishnan & Chinthala 2022). Different from other carbon nitride compounds, g-C3N4 exhibits a unique delocalized conjugate molecular structure, which is composed of stacking carbon nitride layers interconnected via amines (Fu et al. 2018). The unique two-dimensional structure, as well as the strong bonding between C and N atoms, result in excellent electronic conductivity, and high chemical and thermal stability (Ismael 2020). However, its practical application is restricted due to low photocatalytic performance, owing to its rapid electron–hole pair recombination, low specific surface area and low adsorption ability (Mishra et al. 2019; Truong et al. 2022). Moreover, the long recovery operation of g-C3N4 from water also hinders its commercial application potential (Zhao et al. 2021b). Recently, spinel ferrite/g-C3N4 heterojunctions show excellent solar-to-chemical energy conversion rates (Das & Chowdhury 2021). These composites exhibit interesting properties: unique structural properties, extended light absorption range, enhance charge carrier mobility and high redox capability, as well as facile magnetic recycling ability (Keerthana et al. 2022). All these greatly improve the photodegradation performance. The micro-structures of these composites are discussed in this section, such as type-II heterojunction, p–n junction and S-scheme structure. The brief information of these papers is summarized in Table 2.

Table 2

Summarized information of spinel ferrite/g-C3N4 photocatalysts

PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4/g-C3N4 Solvothermal method Methylene blue, 10 mg L−1; Rhodamine B, 10 mg L−1; Tetracycline hydrochloride, 10 mg L−1300 W Xenon lamp with UV filter as visible light source, 0.3 g L−1 Methylene blue, 98.00%/120 min; Rhodamine B, 100%/120 min; Tetracycline hydrochloride, 95.00%/210 min Wu et al. (2018)  
MnFe2O4/g-C3N4 Calcination method Rhodamine B, 30 mg L−1 Sunlight irradiation; 0.4 g L−1 97.20%/90 min Xie et al. (2022)  
NiFe2O4/g-C3N4 Hydrothermal method Tetracycline, 20 mg L−1 30 W LED lamp (400 nm < λ < 760 nm) as visible light source; 0.1 g L−1; pH = 5 78.00%/120 min Lu et al. (2023)  
ZnFe2O4/reduced graphene oxide/g-C3N4 Solvothermal method Malachite green, 10−515 W white LED, 418–700 nm; 0.5 g L−1 63.00%/150 min Tsvetkov et al. (2020)  
g-C3N4/MnFe2O4/graphene Solvothermal method Metronidazole, 20 mg L−1; Amoxicillin, 20 mg L−1; Tetracycline, 20 mg L−1; Ciprofloxacin, 10 mg L−1300 W Xe lamp with a 400 nm cutoff filter; 0.01 mol L−1 persulfate; 1.0 g L−1 Metronidazole, 94.50%/60 min (0.0337 min−1); Amoxicillin, (0.017 min−1); Tetracycline, 91.50%/60 min (0.027 min−1); Ciprofloxacin, (0.043 min−1Wang et al. (2017)  
PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4/g-C3N4 Solvothermal method Methylene blue, 10 mg L−1; Rhodamine B, 10 mg L−1; Tetracycline hydrochloride, 10 mg L−1300 W Xenon lamp with UV filter as visible light source, 0.3 g L−1 Methylene blue, 98.00%/120 min; Rhodamine B, 100%/120 min; Tetracycline hydrochloride, 95.00%/210 min Wu et al. (2018)  
MnFe2O4/g-C3N4 Calcination method Rhodamine B, 30 mg L−1 Sunlight irradiation; 0.4 g L−1 97.20%/90 min Xie et al. (2022)  
NiFe2O4/g-C3N4 Hydrothermal method Tetracycline, 20 mg L−1 30 W LED lamp (400 nm < λ < 760 nm) as visible light source; 0.1 g L−1; pH = 5 78.00%/120 min Lu et al. (2023)  
ZnFe2O4/reduced graphene oxide/g-C3N4 Solvothermal method Malachite green, 10−515 W white LED, 418–700 nm; 0.5 g L−1 63.00%/150 min Tsvetkov et al. (2020)  
g-C3N4/MnFe2O4/graphene Solvothermal method Metronidazole, 20 mg L−1; Amoxicillin, 20 mg L−1; Tetracycline, 20 mg L−1; Ciprofloxacin, 10 mg L−1300 W Xe lamp with a 400 nm cutoff filter; 0.01 mol L−1 persulfate; 1.0 g L−1 Metronidazole, 94.50%/60 min (0.0337 min−1); Amoxicillin, (0.017 min−1); Tetracycline, 91.50%/60 min (0.027 min−1); Ciprofloxacin, (0.043 min−1Wang et al. (2017)  

Wu et al. prepared hierarchical ZnFe2O4/g-C3N4 heterojunction by solvothermal method (Wu et al. 2018). Typical microspheres were formed by ZnFe2O4 nanoparticles, and their diameter was limited due to the confined space effect of g-C3N4. Compared with pure ZnFe2O4, ZnFe2O4/g-C3N4 showed promoted photodegradation performance toward organic dyes under visible light. The composite was reported as a type-II heterojunction. The CB edge of g-C3N4 was more negative than that of ZnFe2O4, while the VB edge of ZnFe2O4 was more positive than that of g-C3N4. After irradiation, the photo-induced e migrated from g-C3N4 to ZnFe2O4, and the photo-induced h+ moved in the opposite direction. This migration promoted charge carrier separation, thus prolonging the lifetime and enhancing photocatalytic performance. Above all, the construction of heterojunction should follow the energy band matching principle, as well as close contact between components (Huang et al. 2018). However, ZnFe2O4/g-C3N4 composite exhibited reduced redox ability, due to the less positive VB position and less negative CB position. As for ZnFe2O4/g-C3N4, despite its enhanced charge carrier mobility, further, development is needed due to its poor redox ability.

Different from ZnFe2O4, NiFe2O4 and MnFe2O4 are p-type semiconductors (Jiang et al. 2021; Agboola et al. 2022), thus the micro-structure properties of NiFe2O4/g-C3N4 and MnFe2O4/g-C3N4 should be attributed as p–n junctions (Kong et al. 2022). When a p–n junction is built, an internal electric field is formed at the interface region due to electron (from an n-type semiconductor) and hole (from a p-type semiconductor) diffusion. Similar to type-II heterojunction, during light irradiation, electrons move to less negative CB while holes move to less positive VB due to the internal electric field, resulting in prolonged charge carrier lifetime and promoted photocatalytic activity. Xie et al. prepared MnFe2O4/g-C3N4 and evaluated the photocatalytic activity by Rhodamine B photodegradation (Xie et al. 2022). The composite with 30 wt% MnFe2O4 exhibited the highest photocatalytic activity under visible light. The reusability tests proved that, after five cycles, the photodegradation rate slightly dropped, implying its excellent stability and convenience in recovery. The interface contact between MnFe2O4 and g-C3N4, and the formation of an internal electric field greatly enhanced charge carrier mobility due to their energy band positions. The p–n junctions exhibit enhanced photocatalytic activity as well as excellent recyclability and stability, proving their high potential to be applied in wastewater treatment.

Recently, another heterojunction structure, S-scheme heterojunction was reported. Generally, this type of heterojunction is built between a semiconductor with a higher positive VB position (oxidizing part) and the other with a higher negative CB position (reducing part) (Sharma et al. 2022; Sun et al. 2022). One typical example is the composite g-C3N4/NiFe2O4 (CN/NFO), reported by Lu et al. (Lu et al. 2023), with the illustration of the photodegradation mechanism (Figure 4) toward tetracycline (TC) under visible light. As for this composite, NFO was the reducing semiconductor and CN was the oxidizing semiconductor. After contact, electrons migrated spontaneously from CN to NFO until their Fermi levels reached equilibrium, which resulted in the formation of internal electric field at the interface (Guo et al. 2017). When irradiated, photo-induced e in CB of NFO tended to combine with h+ in VB of CN, and thus enhanced the transition of photo-excited e from VB to CB. In conclusion, this heterojunction presented effective separation of charge carriers with high redox ability (Fang et al. 2022). The TC removal efficiency was further improved by adding H2O2, due to the photo-Fenton synergistic effect (Palanivel et al. 2021; Liu et al. 2022a), which facilitated the conversion from Fe3+ to Fe2+ and thus generated more •OH. Compared with p–n junction and type-II heterojunction, S-scheme structure not only reduced charge carrier recombination, but also promoted redox ability, presenting excellent photodegradation efficiency (Moradi et al. 2022). Thus, S-scheme can be considered as a promising route to design and fabricate high-performance photocatalysts.
Figure 4

S-scheme heterojunction mechanism about the charge carrier transfer between g-C3N4 (CN) and NiFe2O4 (NFO) (Lu et al. 2023).

Figure 4

S-scheme heterojunction mechanism about the charge carrier transfer between g-C3N4 (CN) and NiFe2O4 (NFO) (Lu et al. 2023).

Close modal

Due to the excellent electron conductivity, graphene can also be introduced to g-C3N4 to improve its photocatalytic performance. Up to now, plenty of papers on g-C3N4/graphene have been published, however, the combination of g-C3N4/graphene and spinel ferrite has seldom been reported. It is believed that the combination of heterojunction and graphene can greatly enhance photocatalytic efficiency (Hafeez et al. 2023).

In 2020, Tsvetkov et al. reported the ternary ZnFe2O4/rGO/g-C3N4 nanocomposite (Tsvetkov et al. 2020), prepared by the solvothermal method. During the photodegradation process, rGO (reduced GO) acted as an electron mediator, and efficiently separated photo-induced charge carriers (e/h+), it also enhanced the adsorption ability to target pollutants. Meanwhile, ZnFe2O4 and g-C3N4 combined as type-II heterojunctions, which also reduced charge carrier recombination. These factors greatly improved the overall photodegradation efficiency. In conclusion, the introduction of the functional substrates such as graphene can further improve the performance of type-II heterojunction.

Wang et al. reported the fabrication of g-C3N4/MnFe2O4/graphene (C3N4@MnFe2O4-G) composite (Wang et al. 2017). The ternary composite exhibited improved catalytic, optical and absorption ability, compared with single or binary sample. The catalytic activity was evaluated by photo-Fenton degradation of metronidazole, amoxicillin, TC and ciprofloxacin with persulfate under visible light, the one with mass ratio of 1:2 (g-C3N4 and MnFe2O4-G) was the optimal catalyst. The mechanism is illustrated in Figure 5. The intense contact and band alignment between g-C3N4 and MnFe2O4 led to efficient charge carrier mobility across the interface, and the inner electric field in the p–n junction provided a driving force for charge carrier transfer. Besides, graphene acted as a high-speed charge channel to extend the lifetime of the charge carrier, and its high specific surface area and numerous adsorption/reaction sites also facilitated photocatalytic reaction. In addition, the introduction of persulfate (PS) further improved photodegradation performance, due to the synergy between PS and photocatalyst, including high response to visible light, large specific surface area, the self-redox cycles of Fe and Mn atoms in MnFe2O4 (PS activators) as well as the rapid production (Deng et al. 2016), easy separation and transportation of photo-induced e/h+ pairs. In conclusion, the combination of p–n junction and graphene greatly improved photodegradation performance, similar to the ternary ZnFe2O4/rGO/g-C3N4 composite. The addition of oxidant PS can further enhance photodegradation performance due to the synergy between ternary catalyst and PS. This ternary combination provides a new route to construct high-performance photocatalysts, presenting a promising photocatalyst fabrication strategy.
Figure 5

Mechanism for antibiotics photodegradation in the C3N4@MnFe2O4-G/PS system (Wang et al. 2017).

Figure 5

Mechanism for antibiotics photodegradation in the C3N4@MnFe2O4-G/PS system (Wang et al. 2017).

Close modal

Spinel ferrite/other carbon materials

Above all, if combined with g-C3N4 or graphene, spinel ferrite-based photocatalysts can effectively eliminate organic pollutants. However, the preparation of graphene or its derivatives is very sophisticated and expensive. In the following section, several cost-effective carbon materials are introduced as photocatalyst substrates (Chen et al. 2019). The brief information of these papers is summarized in Table 3.

Table 3

Summarized information of spinel ferrite/other carbon materials photocatalysts

PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
MnFe2O4/g-C3N4/porous carbon microspheres Hydrothermal method Methyl orange, 10 mg L−1 300 W Xenon lamp with a 400 nm cutoff filter as visible light source, 1.0 g L−1 99.30%/75 min Hu et al. (2021)  
multi-walled carbon nanotubes/MnFe2O4 Hydrothermal method Phenol, 5 mg L−1 11 W mercury germicidal-lamp wavelength of 254 nm; 0.2 g L−1 ≈22.50%/120 min Hazarika et al. (2018)  
ZnFe2O4/B, N-codoped biochar One-pot microwave-assisted pyrolysis method Tetracycline hydrochloride, 150 mg L−1 Xe lamp (500 mW cm−2); 1/3 g L−1 98.19%/120 min Peng et al. (2021)  
PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
MnFe2O4/g-C3N4/porous carbon microspheres Hydrothermal method Methyl orange, 10 mg L−1 300 W Xenon lamp with a 400 nm cutoff filter as visible light source, 1.0 g L−1 99.30%/75 min Hu et al. (2021)  
multi-walled carbon nanotubes/MnFe2O4 Hydrothermal method Phenol, 5 mg L−1 11 W mercury germicidal-lamp wavelength of 254 nm; 0.2 g L−1 ≈22.50%/120 min Hazarika et al. (2018)  
ZnFe2O4/B, N-codoped biochar One-pot microwave-assisted pyrolysis method Tetracycline hydrochloride, 150 mg L−1 Xe lamp (500 mW cm−2); 1/3 g L−1 98.19%/120 min Peng et al. (2021)  

Frist, carbon-based microsphere. Hu et al. immobilized MnFe2O4/g-C3N4 onto porous carbon (PC) microspheres (Hu et al. 2021), in which PC was made from glucose via hydrothermal method. As shown in Figure 6(a) and 6(b), MnFe2O4@PC/g-C3N4 (Mn@PC/g-C3N4) presented a spherical morphology with adiameter of 2–3 μm. Photodegradation of methyl orange under visible light showed that, in optimal Mn@PC/g-C3N4, the mass ratio of MnFe2O4@PC and g-C3N4 was 20%, and its methyl orange photodegradation rate was 6.2 times higher than that of pristine g-C3N4. This can be ascribed to the enhanced light responding capacity and light harvesting ability, as well as effective separation of charge carriers, due to the introduction of PC and MnFe2O4 (Figure 6(c)). This substrate can be utilized as an alternative to graphene or its derivatives since it also has similar functions. However, PC was obtained by hydrothermal method, which limited its large-scale production. Future research should be carried out to develop a simpler route for PC production.
Figure 6

(a and b) SEM images of Mn@PC/g-C3N4; (c) illustrated mechanism for photocatalytic degradation of MO by Mn@PC/g-C3N4 (Hu et al. 2021).

Figure 6

(a and b) SEM images of Mn@PC/g-C3N4; (c) illustrated mechanism for photocatalytic degradation of MO by Mn@PC/g-C3N4 (Hu et al. 2021).

Close modal

Second, multi-walled carbon nanotubes (MWCNTs). Hazarika et al. decorated MnFe2O4 nanoparticles onto MWCNTs (MWCNTs/MnFe2O4) via the hydrothermal method (Hazarika et al. 2018), with a particle size of 27–30 nm. The nanocomposites exhibited superior phenol photodegradation efficiency compared with pristine MnFe2O4, due to the inhibition of photo-induced e/h+ pair recombination by MWCNTs. However, the degradation experiments were carried out under UV light, which means MWCNTs/MnFe2O4 only responded to visible light. This greatly hinders its practical application since UV light is only a small proportion of the sunlight spectrum. The production cost for MWCNTs is still relatively high, thus it is suggested that much cheaper carbon materials with similar functions should be developed as a substrate of the photocatalyst.

The above-mentioned carbon materials have the same shortcoming: high preparation costs and sophisticated procedures. Recently, as a common and cheap carbon material, biochar has drawn great attention to improving the photocatalytic activity of semiconductors, as well as a simple production routes, by calcinating various agricultural wastes in an oxygen-limited condition (Fito et al. 2022). Its abundant functional groups and condensed aromatic ring structure not only improve adsorption ability, but also accelerate electron transfer during the photocatalytic process (Ye et al. 2019; Feng et al. 2021). Wang et al. reported that B, N-codoped biochar exhibited higher adsorption ability, and enhanced charge carrier transportation, compared with pristine biochar (Wang et al. 2021; Zhou et al. 2021). Peng et al. modified B, N-codoped biochar with ZnFe2O4 (ZnFe/BN-biochar, Figure 7(a)–7(d)) (Peng et al. 2021). This composite presented enhanced photodegradation efficiency toward TC hydrochloride (TCH), compared with a single component, due to the sufficient active sites at the junction interface, which were important for the adsorption-photocatalytic capacity toward TCH molecules. Moreover, the migration of charge carriers at the interface between ZnFe2O4 and biochar inhibited their recombination, which also improved photodegradation performance (Figure 7(e)). The optimal ZnFe/BN-biochar eliminated 98.19% of TCH in 120 min. However, after seven cycles, this value sharply dropped to 89.45%, implying its unsatisfactory stability. In conclusion, as a substrate, biochar also has a similar function to other carbon materials. It is suggested that, further improvement should be proposed to promote the stability of biochar-based photocatalysts, in other words, to overcome the disadvantages of biochar: unstable in alkaline solution and relatively low solidity.
Figure 7

(a and b) SEM and (c and d) TEM images of ZnFe/BN-biochar; (e) photocatalytic mechanism of ZnFe/BN-biochar (Peng et al. 2021).

Figure 7

(a and b) SEM and (c and d) TEM images of ZnFe/BN-biochar; (e) photocatalytic mechanism of ZnFe/BN-biochar (Peng et al. 2021).

Close modal

Above all, the photocatalyst composed of spinel ferrite and carbon material can effectively eliminate various organic pollutants; however, higher demands are proposed nowadays to meet the growing requirements for wastewater treatment. Thus, developing high-performance and easy-recyclable photocatalysts from low-cost materials has been a challenging and urgent task. It is suggested that researchers focus on the development of ternary photocatalytic composite, which is composed by spinel ferrite-based heterojunction and carbon material. Moreover, the development of cost-effective carbon materials, such as biochar, is another important research topic especially to improve the stability of the long-term photodegradation process.

The heterojunctions of spinel ferrite and Bi-based semiconductors have recently been extensively studied in recent years. Typical Bi-based semiconductors are: BiOX (X = Cl, Br, I), Bi2WO6, Bi2O2CO3, BiVO4, Bi2S3 and so on.

Spinel ferrite/BiOX

Due to the unique structure and excellent light absorption ability, Bi-based materials have become a hotspot in the research field of photocatalysis. Among various Bi-based materials, Sillén-type bismuth oxyhalides (BiOX, X = Cl, Br, I) have drawn great interest (Wang et al. 2020b). Due to its narrow bandgap, BiOX possesses a high absorption ability to visible light (Ye et al. 2014). Moreover, their two-dimensional layered structure also facilitates photocatalytic performance. However, several drawbacks restrict their practical application (Mengting et al. 2022), such as high charge carrier recombination, and catalyst recovery limitations. Until now, many methods have been proposed to overcome these problems (Hussain et al. 2022), and among them, the incorporation of spinel ferrite has been considered a promising strategy (Suresh et al. 2021), which not only facilitates photocatalytic performance but also enhances recyclability via magnetic recovery (Ma et al. 2021). This strategy endows BiOX with a high potential for wastewater treatment. The brief information of the following papers is summarized in Table 4.

Table 4

Summarized information of spinel ferrite/bismuth oxyhalide photocatalysts

PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4 nanofibers/(001) BiOCl nanosheets Electrospinning and solvothermal method Rhodamine B, 10 mg L−1 150 W xenon lamp equipped with a cutoff glass filter (>420 nm) as visible light source, 1.0 g L−1 97.00%/180 min Sun et al. (2018)  
NiFe2O4/N-doped BiOBr nanosheets Hydrothermal method Phenol, 10 mg L−1; K2Cr2O7 (Cr (VI)), 25 mg/L 105 W compact fluorescent lamp with intensity as 1.0 × 104 lx (visible light); 1.0 g L−1 Phenol, 95.90%/60 min; Cr (VI), 100%/60 min Sin et al. (2021)  
MnFe2O4/BiOBr Hydrothermal method 2,4-dichlorophenoxyacetic (2,4-D), 20 mg L−1; Rhodamine B, 20 mg L−1 105 W compact fluorescent lamp with intensity as 1.0 × 104 lx (visible light); 1.0 g L−1 2.4-D, 96.50%/80 min; Rhodamine B, 89.30%/80 min Sin et al. (2020)  
ZnFe2O4/BiOI Solvothermal method Acid orange 7, 20 mg L−1 400W halogen lamp; 1.0 g L−1 96.00%/180 min Yosefi et al. (2017)  
PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4 nanofibers/(001) BiOCl nanosheets Electrospinning and solvothermal method Rhodamine B, 10 mg L−1 150 W xenon lamp equipped with a cutoff glass filter (>420 nm) as visible light source, 1.0 g L−1 97.00%/180 min Sun et al. (2018)  
NiFe2O4/N-doped BiOBr nanosheets Hydrothermal method Phenol, 10 mg L−1; K2Cr2O7 (Cr (VI)), 25 mg/L 105 W compact fluorescent lamp with intensity as 1.0 × 104 lx (visible light); 1.0 g L−1 Phenol, 95.90%/60 min; Cr (VI), 100%/60 min Sin et al. (2021)  
MnFe2O4/BiOBr Hydrothermal method 2,4-dichlorophenoxyacetic (2,4-D), 20 mg L−1; Rhodamine B, 20 mg L−1 105 W compact fluorescent lamp with intensity as 1.0 × 104 lx (visible light); 1.0 g L−1 2.4-D, 96.50%/80 min; Rhodamine B, 89.30%/80 min Sin et al. (2020)  
ZnFe2O4/BiOI Solvothermal method Acid orange 7, 20 mg L−1 400W halogen lamp; 1.0 g L−1 96.00%/180 min Yosefi et al. (2017)  

All three BiOX (X = Cl, Br, I) are p-type semiconductors, thus ZnFe2O4/BiOX should be categorized as a p–n junction composite. Sun et al. prepared a hierarchical p–n junction of BiOCl (p-type) nanosheets and ZnFe2O4 (n-type) nanofibers (Sun et al. 2018), via electrospinning and solvothermal method. During the fabrication process, the density and loading amount of BiOCl nanosheets with exposed (001) facets were controlled by adjusting the concentration of the precursor (Sun et al.). Compared with ZnFe2O4 nanofibers, the p–n junction showed enhanced photodegradation performance under visible light. The exposed (001) facets of BiOCl enhanced the surface reaction during the photocatalytic process (Wang et al. 2015). The hierarchical structure was built based on ZnFe2O4 nanofibers (Figure 8(a)) and BiOCl nanosheets loaded onto the surface (Figure 8(b)). The nanofibers were produced via the electrospinning method, exhibiting superior morphology. The ZnFe2O4 nanoparticles prepared by the solvothermal method exhibited highly agglomerated morphology (Figure 8(c)), as well as the corresponding binary composite (ZnFe2O4/BiOCl, Figure 8(d)). In conclusion, this unique morphology of photocatalyst can greatly affect its photocatalytic activity by reducing nanoparticle agglomeration, providing a uniform electric field surface for charge separation (Figure 8(f)), and improving surface condition to accelerate pollutant adsorption and photodegradation (Figure 8(e)). However, electrospinning requires a series of highly sophisticated equipment, which increases the production cost and limits large-scale production potential.
Figure 8

SEM images of (a) ZnFe2O4 nanofibers, (b) p-BiOCl/n-ZnFe2O4-2 (BZ2), (c) ZnFe2O4 nanoparticles (NPs obtained by solvothermal method), and (d) p-BiOCl/n-ZnFe2O4-2 nanoparticles (BZ2 NPs) at low magnification and high magnification (inset); (e) photodegradation plots of Rhodamine B using different catalysts under visible light; and (f) photocurrent responses of (a) ZnFe2O4 nanoparticles, (b) ZnFe2O4 nanofibers, (c) p-BiOCl/n-ZnFe2O4-2 nanoparticles (BZ2 NPs), and (d) p-BiOCl/n-ZnFe2O4-2 (BZ2) (Sun et al. 2018).

Figure 8

SEM images of (a) ZnFe2O4 nanofibers, (b) p-BiOCl/n-ZnFe2O4-2 (BZ2), (c) ZnFe2O4 nanoparticles (NPs obtained by solvothermal method), and (d) p-BiOCl/n-ZnFe2O4-2 nanoparticles (BZ2 NPs) at low magnification and high magnification (inset); (e) photodegradation plots of Rhodamine B using different catalysts under visible light; and (f) photocurrent responses of (a) ZnFe2O4 nanoparticles, (b) ZnFe2O4 nanofibers, (c) p-BiOCl/n-ZnFe2O4-2 nanoparticles (BZ2 NPs), and (d) p-BiOCl/n-ZnFe2O4-2 (BZ2) (Sun et al. 2018).

Close modal
Sin et al. decorated NiFe2O4 nanoparticles on N-doped BiOBr nanosheets via the hydrothermal method (Sin et al. 2021). Compared with pristine BiOBr, N-doped BiOBr showed higher visible light absorption (Jiang et al. 2014). This composite greatly improved the simultaneous removal of phenol and Cr (VI) under visible light, compared with a single component. After 60 min of visible light irradiation, 95.9% phenol and 100% Cr (VI) were simultaneously removed. Quenching tests proved that, as for phenol degradation, •OH was the main reactive species, while e was the main radical during Cr (VI) reduction. This proved the photodegradation mechanism as the formation of Z-scheme heterojunction, not type-II heterojunction, as shown in Figure 9. After five successive runs, no obvious decrease in photocatalytic efficiency can be observed, implying the high recyclability of this composite. The combination of MnFe2O4 and BiOBr also exhibited promoted photodegradation efficiency due to the construction of the Z-scheme structure. The same research group also reported the decoration of MnFe2O4 nanoparticles onto BiOBr nanosheets by hydrothermal method (Sin et al. 2020), and applied in the degradation of 2,4-dichlorophenoxyacetic acid (2,4-D) and Rhodamine B under visible light. The photocatalytic mechanism was also attributed to the formation of Z-scheme heterojunction, based on quenching tests. After five consecutive uses, the composite showed no significant loss of photoactivity, which proved its excellent stability. Compared with type-II and p–n junctions, Z-scheme heterojunction exhibits enhanced redox affinities of excitons. The key factor of Z-scheme heterojunction is the charge transfer pathway at the interface between two components (Malefane et al. 2022). The interfacial band matching affects the construction of Z-scheme (Malefane et al. 2022). After the components contact each other, the electron flows from the component with a lower work function (component one) to the counterpart with a higher work function (component two) (Jia et al. 2023). This results in the balance of the Fermi level. By the impact of the internal electric field, the holes from component one and the electrons from component two flow to the interface for recombination. This leads to the construction of a Z-scheme structure with effective separation of photo-generated electrons and holes, which are accumulated at lower VB and higher CB positions, with high redox capability.
Figure 9

Possible charge carrier separation paths and photodegradation mechanism of N-doped BiOBr/NiFe2O4 composite (Sin et al. 2021).

Figure 9

Possible charge carrier separation paths and photodegradation mechanism of N-doped BiOBr/NiFe2O4 composite (Sin et al. 2021).

Close modal

Yosefi et al. synthesized flower-like p-BiOI/n-ZnFe2O4 junction via a solvothermal method (Yosefi et al. 2017). The composite showed higher photodegradation efficiency toward acid orange 7 under visible light, compared with pure ZnFe2O4 and BiOI. In the optimal composite, the mass ratio of BiOI/ZnFe2O4 was 80/20. The p–n junction facilitated the charge carrier separation and thus enhanced photocatalytic performance. This is similar to the above-mentioned p-BiOCl/n-ZnFe2O4. Xia et al. prepared flower-like NiFe2O4/BiOI (NFO/BOI) nanocomposites by solvothermal method (Xia et al. 2018). The photoactivity was evaluated by the degradation of organic dyes under visible light. The NiFe2O4/BiOI sample with 15 wt% NiFe2O4 exhibited the highest photodegradation performance. The quenching tests proved was the primary radical. The formation of type-II heterostructure improved the separation and restricted the recombination of electron–holes pairs. The composite showed no notable decrease in photoactivity after five recycles, implying its good stability. Based on the above literature works, it can be concluded that the coupling of BiOBr and NiFe2O4, or the coupling of BiOBr and MnFe2O4 is regarded as the optimal combination, compared with BiOCl, BiOI and other spinel ferrites. This is because of their appropriate band matching, leading to the construction of Z-scheme heterojunction. It is suggested that researchers should pay attention to both composites in future work, in order to develop high-performance photocatalysts for wastewater treatment.

Spinel ferrite/Aurivillius Bi-based compounds

Bi2WO6 is often regarded the simplest member of the Aurivillius family with one perovskite layer in its molecular structure (Tachibana 2015), its excellent visible light response ability makes itself a good candidate for photocatalytic purposes. However, its high charge carrier recombination greatly reduced its photocatalytic activity, thus greatly restricting its practical application potential. The coupling of Bi2WO6 and other semiconductors lead to the formation of composites with varied morphologies, and has been considered an effective strategy to build high-performance photocatalysts. The brief information of the following papers is summarized in Table 5.

Table 5

Summarized information of spinel ferrite/Aurivillius Bi-based material photocatalysts

PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4/Bi2WO6 Solvothermal method Tetracycline hydrochloride, 50 mg L−1 500 W Xe lamp (>420 nm), 1.0 g L−1 96.85%/90 min Zhong et al. (2017)  
NiFe2O4 nanoplates/Bi2WO6 nanoflakes Calcination and hydrothermal method Tetracycline, 10 ppm; Methylene blue, 10 ppm 100-W solar simulator; 0.3 g L−1 Tetracycline, 96.81%/96 min; Methylene blue, 99.16%/60 min Koutavarapu et al. (2021)  
ZnFe2O4/Bi2O2CO3 Hydrothermal method Rhodamine B, 5 mg L−1 500 W xenon lamp (simulant sunlight); 0.5 g L−1 ≈71.00%/180 min Liu et al. (2018)  
PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4/Bi2WO6 Solvothermal method Tetracycline hydrochloride, 50 mg L−1 500 W Xe lamp (>420 nm), 1.0 g L−1 96.85%/90 min Zhong et al. (2017)  
NiFe2O4 nanoplates/Bi2WO6 nanoflakes Calcination and hydrothermal method Tetracycline, 10 ppm; Methylene blue, 10 ppm 100-W solar simulator; 0.3 g L−1 Tetracycline, 96.81%/96 min; Methylene blue, 99.16%/60 min Koutavarapu et al. (2021)  
ZnFe2O4/Bi2O2CO3 Hydrothermal method Rhodamine B, 5 mg L−1 500 W xenon lamp (simulant sunlight); 0.5 g L−1 ≈71.00%/180 min Liu et al. (2018)  

Zhong et al. synthesized Bi2WO6/ZnFe2O4 composite via a two-step solvothermal method (Zhong et al. 2017). The combination of ZnFe2O4 greatly enhanced the adsorption and photodegradation ability of Bi2WO6, and endowed the catalyst with the magnetic recyclable property. The composite with 0.15 wt% of ZnFe2O4 presented the highest photodegradation efficiency toward TC hydrochloride (TCH) under visible light, with aremoval percentage of 96.85% in 90 min. The enhanced photoactivity was ascribed to the effective separation of photo-generated electron–hole pairs at the interface. After five recycling tests, the TCH removal rate dropped to 81.52%, which was attributed to the catalyst loss during recycling processes. The photocatalytic mechanism of Bi2WO6/ZnFe2O4 was attributed to atype-II heterojunction.

Koutavarapu et al. prepared 2D NiFe2O4 nanoplates/2D Bi2WO6 nanoflakes heterojunction via a combined calcination and hydrothermal method (Koutavarapu et al. 2021). The photodegradation toward TC and methylene blue indicated that the composite with 20 wt% of Bi2WO6 exhibited the highest photoactivity. Two factors led to the enhanced photoactivity compared with pure component: first, the unique morphology of NiFe2O4/Bi2WO6 nanocomposite, as shown in Figure 10(c). The Bi2WO6 (Figure 10(b)) nanoflakes inserted over the surface of NiFe2O4 nanoplates (Figure 10(a)), which not only facilitated light absorption but also enhanced charge carrier separation. This also resulted in higher specific surface area and more active sites, which facilitated mass transfer during photodegradation. Second, Z-scheme mechanism (Figure 10(d)) was proposed based on quenching test results, that and •OH radicals were the critical active species during photodegradation. This greatly hindered the recombination of photo-excited e/h+ pairs, and improved photodegradation efficiency. The composite maintained high photoactivity after four cycles, suggesting itself promising to be applied in wastewater treatment. In conclusion, the combination of NiFe2O4 and Bi2WO6 is considered the optimal option, for the coupling of spinel ferrite and Bi2WO6. Its Z-scheme structure exhibited outstanding charge separation performance, while its unique morphology further improved adsorption and photodegradation efficiency. Thus, this composite is considered promising for wastewater treatment.
Figure 10

SEM images of (a) NiFe2O4 nanoplates, (b) Bi2WO6 nanoflakes, and (c) NiFe2O4/Bi2WO6 composite; (d) proposed Z-scheme mechanism about photodegradation of TC and MB in NiFe2O4/Bi2WO6 composite (Koutavarapu et al. 2021).

Figure 10

SEM images of (a) NiFe2O4 nanoplates, (b) Bi2WO6 nanoflakes, and (c) NiFe2O4/Bi2WO6 composite; (d) proposed Z-scheme mechanism about photodegradation of TC and MB in NiFe2O4/Bi2WO6 composite (Koutavarapu et al. 2021).

Close modal
Bi2O2CO3 is another member of the Aurivillius family (Zu et al. 2021). Liu et al. prepared Bi2O2CO3/ZnFe2O4 composite via a two-step hydrothermal method (Liu et al. 2018), and used it in dye degradation under simulated sunlight. Bi2O2CO3/ZnFe2O4 composite showed enhanced photoactivity compared with bare ZnFe2O4 and Bi2O2CO3. This was ascribed to the Z-scheme reaction mechanism, which not only extended the light response region but also greatly facilitated interfacial charge carrier mobility (Figure 11). Moreover, Bi2O2CO3/ZnFe2O4 composite also presented excellent stable and recycling properties, implying its great potential for long-term practical use. In conclusion, the enhanced photodegradation performance of this composite was ascribed to the Z-scheme structure via proper band matching, implying its superior potential compared to other heterojunction composites. As for one specific spinel ferrite, it is suggested to find asuitable counterpart to form a Z-scheme composite.
Figure 11

Proposed photodegradation mechanism of Bi2O2CO3/ZnFe2O4 heterojunction (Liu et al. 2018).

Figure 11

Proposed photodegradation mechanism of Bi2O2CO3/ZnFe2O4 heterojunction (Liu et al. 2018).

Close modal

Spinel ferrite/other Bi-based materials

Except for BiOX and Aurivillius Bi-based compounds, other Bi-based photocatalysts, such as BiVO4 and Bi2S3, have also attracted attention. The photocatalytic materials based on these materials and spinel ferrites have been developed. The brief information of the following papers is summarized in Table 6.

Table 6

Summarized information of spinel ferrite/other Bi-based materials photocatalysts

PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4/BiVO4 Co-precipitation method Methylene blue, 15 mg L−1 500 W Halogen lamp (visible light), 2.0 g L−1 99.0%/300 min Xu & Song (2017)  
ZnFe2O4/BiVO4 Sol–gel auto-combustion and calcination method Methyl orange, 10−5 mol/L a light filter (420 nm) was added to a light source (500 W halogen tungsten lamp); 1.5 g L−1 64.15%/120 min Aiqiong et al. (2021)  
MnFe2O4/BiVO4 Hydrothermal method Tetracycline, 10 ppm 30 W Duhalled LED used as visible light; 0.25 g L−1 ≈92.00%/120 min Dieu Cam et al. (2021)  
ZnFe2O4/Bi2S3 Hydrothermal method Tetracycline, 10 mg L−1; Cr (VI), 10 mg L−1 300 W Xe lamp used as visible light; 0.3 g L−1 Tetracycline, 91.60%/120 min; Cr (VI), 96.70%/120 min Yan et al. (2023)  
PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4/BiVO4 Co-precipitation method Methylene blue, 15 mg L−1 500 W Halogen lamp (visible light), 2.0 g L−1 99.0%/300 min Xu & Song (2017)  
ZnFe2O4/BiVO4 Sol–gel auto-combustion and calcination method Methyl orange, 10−5 mol/L a light filter (420 nm) was added to a light source (500 W halogen tungsten lamp); 1.5 g L−1 64.15%/120 min Aiqiong et al. (2021)  
MnFe2O4/BiVO4 Hydrothermal method Tetracycline, 10 ppm 30 W Duhalled LED used as visible light; 0.25 g L−1 ≈92.00%/120 min Dieu Cam et al. (2021)  
ZnFe2O4/Bi2S3 Hydrothermal method Tetracycline, 10 mg L−1; Cr (VI), 10 mg L−1 300 W Xe lamp used as visible light; 0.3 g L−1 Tetracycline, 91.60%/120 min; Cr (VI), 96.70%/120 min Yan et al. (2023)  

Xu et al. prepared ZnFe2O4/BiVO4 via the one-step co-precipitation method (Xu & Song 2017), and used it for dye photodegradation under visible light. The introduction of ZnFe2O4 greatly enhanced visible light absorption of the composite, due to the narrow band gap. Besides, photo-excited e/h+ were effectively separated due to the formation of type-II heterojunction. Ma et al. also fabricated ZnFe2O4/BiVO4 composite (Aiqiong et al. 2021), using the sol–gel auto-combustion and calcination method. This material presented excellent dye degradation under visible light, which was also ascribed to the formation of type-II heterojunction, due to its enhancement to visible light absorption and charge carrier mobility. Cam et al. decorated MnFe2O4 on BiVO4 via the hydrothermal method (Dieu Cam et al. 2021), and applied the composite in TC degradation under visible light. As for the optimal composite, the molar ratio of MnFe2O4: BiVO4 was 30%. The quenching tests indicated that h+, •OH and all played an important role during photodegradation. Based on this, the enhanced photoactivity was ascribed to the formation of Z-scheme heterojunction (Figure 12), which allowed photo-induced e on the CB of BiVO4 quickly moved to the VB of MnFe2O4 and combined with h+, thus greatly hindering the charge carrier combination in each component. This composite also exhibited good stability after five recycle tests, proving itself capable for long-term processes. In conclusion, compared with other spinel ferrites, MnFe2O4 is considered as the optimal material to be coupled with BiVO4, since the micro-structure of this composite was attributed to Z-scheme heterojunction, exhibiting superior photocatalytic activity.
Figure 12

Proposed charge carrier separation and TC photodegradation mechanism using MnFe2O4/BiVO4 heterojunction (Dieu Cam et al. 2021).

Figure 12

Proposed charge carrier separation and TC photodegradation mechanism using MnFe2O4/BiVO4 heterojunction (Dieu Cam et al. 2021).

Close modal
Yan et al. prepared ZnFe2O4/Bi2S3 high-low junction via the hydrothermal method (Yan et al. 2023), and used it in TC degradation and Cr (VI) reduction under visible light. ZnFe2O4/Bi2S3 with 12% of ZnFe2O4 content presented the best photoactivity, with 91.6% TC degradation and 96.7% Cr (VI) reduction in 2 h. Since the band edges of Bi2S3 are located between those of ZnFe2O4, a high-low junction was formed after their contact (Li et al. 2022c), as shown in Figure 13. The photo-induced h+ in the VB of ZnFe2O4 moved to the VB of Bi2S3 due to the effect of the internal electric field, thus the photo-induced e in the CB of ZnFe2O4 and Bi2S3, and the h+ in the VB of Bi2S3 participated in the photocatalytic reaction (Yang 2021). The h+ and e reacted with nearby O2, H2O and •OH and generated and •OH, and quenching tests proved that h+, and •OH were the radicals during the photocatalytic reaction. In conclusion, the high-low junction between ZnFe2O4/Bi2S3, despite its enhanced charge separation, was not comparable to the Z-scheme structure, due to its reduced redox ability (holes moved to a less positive position). In future research on photocatalyst development, it is suggested that the Z-scheme structure is still the mainstream strategy to build high performance composites.
Figure 13

Enhanced charge carrier transfer driven by internal electric field during a photocatalytic process of ZnFe2O4/Bi2S3 (ZFO/BS) (Yan et al. 2023).

Figure 13

Enhanced charge carrier transfer driven by internal electric field during a photocatalytic process of ZnFe2O4/Bi2S3 (ZFO/BS) (Yan et al. 2023).

Close modal

Above all, the photocatalysts derived from spinel ferrite and Bi-based materials have been applied in various organic pollutant degradation, which all exhibited excellent photoactivity and recyclability. Future research work should focus on the proper energy band coupling between bismuth semiconductor and spinel ferrite, in order to build a Z-scheme structure for superior photocatalytic activity. As for current knowledge, Bi2O2CO3/ZnFe2O4, Bi2WO6/NiFe2O4 and BiVO4/MnFe2O4 are typical examples. Other issues should also be considered in future work: the catalyst amount during photodegradation should be further reduced through the modification and optimization of the photocatalyst's structure and physicochemical properties. Moreover, the stability and recyclability of photocatalysts should be further improved.

TiO2 has long been studied as a green semiconductor, especially in the aspect of photocatalytic degradation, due to its advantages such as abundance, low cost, nontoxicity and chemical stability (Nur et al. 2022). However, the wide band gap of pure TiO2 (3.2 eV) greatly limits its light absorption range (Li et al. 2022d), only responding to UV light, which accounted for 4% of solar energy. Besides, other disadvantages, such as rapid charge carrier recombination, low recyclability and activity regulation, also restrict its practical application (Mohd Adnan et al. 2019). To overcome all these issues and design visible-light-driven photocatalysts, the coupling of TiO2 and spinel ferrite has been proven effective and promising. The brief information of the following papers is summarized in Table 7.

Table 7

Summarized information of spinel ferrite/TiO2 photocatalysts

PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4/TiO2 Hydrothermal method Humic acid, 10 mg L−1; Florfeniol, 10 mg L−1; Tetracyclines, 10 mg L−1; Bisphenol A, 10 mg L−1 300 W Xe lamp (visible light), 0.2 g L−1 (0.6 g L−1 for Bisphenol A degradation) Humic acid, 0.01766min−1; Florfeniol, 0.01504 min−1; Tetracyclines, 0.0166 min−1; Bisphenol A, 0.01564 min−1 Zeng et al. (2022)  
MnFe2O4@ reduced graphene oxide @TiO2 Hydrothermal and calcination method Ofloxacin, 20 mg L−1 a solar simulator equipped with halogenide high-pressure lamp (1,000 W/m2); 0.5 g L−1; pH = 5.4 8.56 × 10−3 min−1 Firtina-Ertis & Kerkez-Kuyumcu (2022)  
PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4/TiO2 Hydrothermal method Humic acid, 10 mg L−1; Florfeniol, 10 mg L−1; Tetracyclines, 10 mg L−1; Bisphenol A, 10 mg L−1 300 W Xe lamp (visible light), 0.2 g L−1 (0.6 g L−1 for Bisphenol A degradation) Humic acid, 0.01766min−1; Florfeniol, 0.01504 min−1; Tetracyclines, 0.0166 min−1; Bisphenol A, 0.01564 min−1 Zeng et al. (2022)  
MnFe2O4@ reduced graphene oxide @TiO2 Hydrothermal and calcination method Ofloxacin, 20 mg L−1 a solar simulator equipped with halogenide high-pressure lamp (1,000 W/m2); 0.5 g L−1; pH = 5.4 8.56 × 10−3 min−1 Firtina-Ertis & Kerkez-Kuyumcu (2022)  

In 2022, Zeng et al. prepared TiO2/ZnFe2O4 heterojunction via a one-step hydrothermal method (Zeng et al. 2022). It was observed that TiO2 nanosheets grew on the main body of ZnFe2O4 nanorods. The heterojunction possessed higher photocatalytic performance toward hydrogen production and contaminants degradation (humic acid, florfenicol, tetracyclines, and bisphenol A), compared with single component. The composite with a molar ratio of 1:4 exhibited the highest activity, and also manifest good stability. This high performance was ascribed to the formation of type-II heterojunction, leading to the enhancement of visible light absorption and improved photo-induced charge separation at the interface. However, different opinions were proposed to explain the photocatalytic mechanism of TiO2/ZnFe2O4. Rong et al. prepared TiO2/ZnFe2O4 composite via the solvothermal-calcination method (Rong et al. 2019), and used it in N2 photo-fixation under visible light. TiO2/ZnFe2O4 presented a higher NH3 production rate than pure TiO2 and ZnFe2O4. The Quenching tests implied that the enhanced photoactivity was attributed to the formation of Z-scheme heterojunction (Figure 14, model II), not model I, due to the detection of •OH radical. After five recycle tests, TiO2/ZnFe2O4 remained high stability. The different band structures between these literature works can be explained as follows: Zeng et al. prepared TiO2/ZnFe2O4 heterojunction via the hydrothermal method, using ethanediol–water mixed solvent as media. The obtained composite showed its unique morphology: TiO2 nanosheets grew on the main body of ZnFe2O4 nanorods. However, Rong et al. prepared this composite via the solvothermal-calcination method. During the solvothermal process, ethylene glycol was used as media. Other preparation factors such as temperature and reaction time are also different from each other. Thus, the obtained TiO2 and NiFe2O4 from both papers had different energy band structures, such as different band gap values, leading to different band alignment (via band matching) and heterojunction structures.
Figure 14

(a) Illustration of two possible charge carrier transfer paths at the interface of TiO2/ZnFe2O4 composite and (b) the mechanism of N2 photo-fixation using Z-scheme TiO2/ZnFe2O4 composite (Rong et al. 2019).

Figure 14

(a) Illustration of two possible charge carrier transfer paths at the interface of TiO2/ZnFe2O4 composite and (b) the mechanism of N2 photo-fixation using Z-scheme TiO2/ZnFe2O4 composite (Rong et al. 2019).

Close modal

Wang et al. prepared TiO2/NiFe2O4 heterojunction via the hydrothermal method and used it to detect sub-ppm trimethylamine with the aid of visible light (Wang et al. 2022). Trimethylamine (TMA) is a tertiary amine compound, responsible for the unpleasant smell of decomposing fish, thus it is an effective indicator of seafood freshness (Zhao et al. 2021a). TiO2/NiFe2O4 sensor exhibited enhanced gas-sensing performance, due to the formation of p–n heterojunction, which enhanced charge flow between two components. This work also extended the application potential of TiO2/NiFe2O4 heterojunction. Moreover, the photocatalytic activity of the TiO2/NiFe2O4 composite can be altered after TiO2 was doped. Kuyumcu et al. prepared TiO2/NiFe2O4 by a complex assisted vapor thermal method (Firtina-Ertis & Kerkez-Kuyumcu 2022), and coupled Ag+ by wet-impregnation. This composite was used in photocatalytic hydrogen production, and the sample with 12 wt% of NiFe2O4 and 0.5 wt% of Ag+ presented the best photoactivity. •OH played a vital role during this process, as well as . Based on this, S-scheme heterojunction was proposed to interpret the photocatalytic mechanism (Fu et al. 2019). There was an internal electric field from NiFe2O4 to TiO2, the photo-induced e on the CB of TiO2 combined with photo-induced h+ on the VB of NiFe2O4. The h+ on the VB of TiO2 reacted with the methanol via Ag+ and generated CO2, while the e on the CB of NiFe2O4 combined with H+ and generated H2. As long as proper band alignment between components, S-scheme heterojunction can be built between p-type and n-type semiconductors, or between two n-type semiconductors, or two p-type semiconductors (Naderi et al. 2023). This junction exhibits promoted redox ability similar to the Z-scheme, so it can be seen as a promising route to develop a highly efficient photocatalytic composite. The introduction of doping further enhanced photodegradation efficiency by prolonging charge carrier lifetime, providing an extra strategy to enhance photocatalytic application potential.

Gad-Allah et al. fabricated a core double-shell MnFe2O4@rGO@TiO2 composite via a successive hydrothermal and calcination method (Abdel-Wahed et al. 2020). The composite exhibited superior photodegradation of ofloxacin under solar light, compared with single component. This work also revealed that MnFe2O4@rGO@TiO2 of 50-mg rGO (calcined at 400 °C for 2 h) exhibited the highest photodegradation rate at pH = 5.4 of water polluted with ofloxacin. MnFe2O4 acted as recombination center due to its energy band position, thus leading to less efficient photoactivity, however, as an interlayer between MnFe2O4 and TiO2, rGO attracted the photo-induced e from CB of TiO2 and prolonged its lifetime to enhance the overall photoactivity. This ternary composite conserved its photoactivity after six consecutive runs, proving itself stable for long-term practical application. In conclusion, although the combination of MnFe2O4@TiO2was attributed as type-II heterojunction, the substrate rGO acted as interlayer and thus hindered charge carrier recombination, promoting overall photocatalytic efficiency. It is suggested that, heterojunction components should be loaded onto functional material to further improve the entire photodegradation performance, for example, carbon-based materials.

Above all, the coupling of spinel ferrite with TiO2 not only improved photocatalytic performance, but also endowed the magnetic recyclable ability. However, there are many types of junction structures as for photocatalytic mechanisms. Thus, it is suggested that more research work should be done to investigate the impact of fabrication methods and conditions on the band alignment of spinel ferrite/TiO2 composites. Meanwhile, the doping and substrate loading strategies are also important, and related research is needed in future research work.

As one of the extensively studied photocatalysts, ZnO has attracted considerable interest due to its low cost, nontoxicity and high active properties (Goktas & Goktas 2021). However, pure ZnO can only be stimulated by UV light, due to its wide band gap (Hullavarad et al. 2009). This greatly lowers its response to sunlight, since UV light merely accounts for 4% of the sunlight spectrum. Besides, another disadvantage of ZnO is its low stability, since it can be affected by photo-corrosion (Taylor et al. 2019). Both factors greatly restrict its practical application as a photocatalyst. Thus, researchers have been developing various strategies to modify ZnO to improve its quantum efficiency, improving the photocatalytic activity and stability (Tian et al. 2012).

One of the effective methods is the combination of ZnO with other semiconductors (Goktas & Goktas 2021). Kuang et al. synthesized an octahedral-like ZnO/ZnFe2O4 composite via the solvothermal method (Kuang et al. 2019), and evaluated its photoactivity via dye photodegradation. The sample with a molar ratio of 3:1 presented the highest photodegradation performance, 82.7 and 91.2% after 120 min of UV-visible light and 140 min of visible light, respectively. Compared with ZnO and ZnFe2O4, the heterojunction exhibited higher photocatalytic performance, due to the synergetic effect of mesoporous structure, effective charge carrier separation at the interface, which improved light response ability, adsorption and degradation ability toward organic dye. this composite also exhibited good stability, no obvious decrease in photoactivity can be detected after four cycles. Choudhary et al. also reported the photodegradation using ZnO/ZnFe2O4 composite (Choudhary et al. 2022), prepared via the co-precipitation method. The superior photodegradation efficiency of ZnO/ZnFe2O4 was ascribed to extended light absorption range, and suppressed charge carrier recombination due to heterostructure. They also reported the outstandingly stable property of ZnO/ZnFe2O4. However, due to the band alignment, the reported composites from both papers were attributed to type-II heterojunctions, in which electrons moved to a less negative position while holes moved to a less positive position, leading to reduced redox ability.

Munir et al. reported the fabrication of ZnO/NiFe2O4 composite via the ultrasonication method (Munir et al. 2021), which exhibited improved photodegradation performance of various dyes under solar light irradiation. They also attributed the enhanced results to the formation of type-II heterojunction (Figure 15(a)), which reduced the recombination of photo-excited charge carriers. Garg et al. further introduced g-C3N4 to ZnO/NiFe2O4 (Garg et al. 2022). The ternary g-C3N4/ZnO/NiFe2O4 was prepared via the sonication–calcination method. The photoactivity was examined by photodegradation toward fluoroquinolone antibiotics: levofloxacin, ciprofloxacin and ofloxacin. It was observed that, the introduction of NiFe2O4 to g-C3N4/ZnO greatly enhanced photodegradation performance, which was ascribed to the formation of dual Z-scheme heterojunction (Figure 15(b)), based on quenching tests. As a result, the ternary catalyst presented amended visible light absorption ability, and diminished photo-generated charge carrier recombination. Moreover, the ternary composite remained intact after five cycles, both its crystalline nature and morphology. In conclusion, type-II heterojunction can be transformed into a Z-scheme structure by introducing another semiconductor with appropriate band alignment, building a dual Z-scheme photocatalytic system. It is another novel strategy to design high-performance photocatalytic composite.
Figure 15

Proposed mechanism of photodegradation using (a) NiFe2O4/ZnO heterojunction (Munir et al. 2021) and (b) traditional type-II route and direct Z-scheme junction of g-C3N4/ZnO/NiFe2O4 composite (Garg et al. 2022).

Figure 15

Proposed mechanism of photodegradation using (a) NiFe2O4/ZnO heterojunction (Munir et al. 2021) and (b) traditional type-II route and direct Z-scheme junction of g-C3N4/ZnO/NiFe2O4 composite (Garg et al. 2022).

Close modal

Boutra et al. combined tannic acid (TA, a carbon material) with ZnO/MnFe2O4 via a two-step solvothermal method (Boutra et al. 2020). The ternary catalyst presented higher dye photodegradation performance under visible light. Both the narrow band gap of MnFe2O4 and the electron transfer ability of TA enhanced the photodegradation performance. The ternary composite still remained high photodegradation efficiency after five cycles, proving its high stability and reusability. In conclusion, the introduction of a third material such as TA can promote photodegradation performance, which is similar to the functions of the above-mentioned carbon materials.

The brief information of the above papers is summarized in Table 8. Above all, the introduction of spinel ferrite affects ZnO in several aspects: first, tuning the band gap of ZnO; second, enhancing the photocatalytic activity; third, improving the stability and recyclability. However, as to its practical application potential, the visible light response range and photocatalytic activity of ZnO-based composite should be further extended, such as the construction of a Z-scheme junction via third-party component addition. Thus, to develop novel photocatalysts with high visible-light absorption ability, high quantum efficiency and stability, is still a major research hotspot in the field of photocatalysis.

Table 8

Summarized information of spinel ferrite/ZnO photocatalysts

PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4/ZnO Solvothermal method followed by thermal treatment Methylene blue, 10 mg L−1 UV-vis (350 ≤ λ ≤ 780 nm) or visible light (λ ≥ 420 nm) generated by a 300W Xe lamp, 1.0 g L−1 91.20% after 120 min of UV-vis; 82.70% after140 min of visible light Kuang et al. (2019)  
ZnFe2O4/ZnO Co-precipitation method Methylene blue (10 μM); Malachite green (10 μM); Methyl orange (10 μM); Rhodamine B (10 μM) Sunlight; 1.0 g L−1 Methylene blue: 90.30%/24 min; Malachite green: 93.10%/24 min; Methyl orange: 28.10%/24 min; Rhodamine B: 57.2%/24 min Choudhary et al. (2022)  
NiFe2O4/ZnO Ultrasonication method Methyl orange (10 mg L−1); Methyl blue (10 mg L−1); Crystal violet (10 mg L−1Sunlight; 0.6 g L−1 Methyl orange: 49.2%/40 min; Methylene blue: 44.40%/40 min; Crystal violet: 41.30%/40 min Munir et al. (2021
NiFe2O4/ZnO/g-C3N4 Sonication–calcination method Levofloxacin, 30 mg L−1; Ciprofloxacin, 10 mg L−1; Ofloxacin, 15 mg L−1 400 W Hg lamp as visible light source with light intensity near the surface of solution to be 51.2 mW/cm2; 0.5 g L−1 Levofloxacin: 94.00%/90 min; Ciprofloxacin: 80.00%/90 min; Ofloxacin: 85.00%/90 min Garg et al. (2022
MnFe2O4/ZnO/tannic acid Solvothermal method Congo Red, 16 mg L−1 128 W Xenon lamp (visible light); 0.2 g L−1 84.20%/90 min Boutra et al. (2020
PhotocatalystPreparation strategyTarget pollutantPhotodegradation conditionsDegradation percentage/reaction timeRef
ZnFe2O4/ZnO Solvothermal method followed by thermal treatment Methylene blue, 10 mg L−1 UV-vis (350 ≤ λ ≤ 780 nm) or visible light (λ ≥ 420 nm) generated by a 300W Xe lamp, 1.0 g L−1 91.20% after 120 min of UV-vis; 82.70% after140 min of visible light Kuang et al. (2019)  
ZnFe2O4/ZnO Co-precipitation method Methylene blue (10 μM); Malachite green (10 μM); Methyl orange (10 μM); Rhodamine B (10 μM) Sunlight; 1.0 g L−1 Methylene blue: 90.30%/24 min; Malachite green: 93.10%/24 min; Methyl orange: 28.10%/24 min; Rhodamine B: 57.2%/24 min Choudhary et al. (2022)  
NiFe2O4/ZnO Ultrasonication method Methyl orange (10 mg L−1); Methyl blue (10 mg L−1); Crystal violet (10 mg L−1Sunlight; 0.6 g L−1 Methyl orange: 49.2%/40 min; Methylene blue: 44.40%/40 min; Crystal violet: 41.30%/40 min Munir et al. (2021
NiFe2O4/ZnO/g-C3N4 Sonication–calcination method Levofloxacin, 30 mg L−1; Ciprofloxacin, 10 mg L−1; Ofloxacin, 15 mg L−1 400 W Hg lamp as visible light source with light intensity near the surface of solution to be 51.2 mW/cm2; 0.5 g L−1 Levofloxacin: 94.00%/90 min; Ciprofloxacin: 80.00%/90 min; Ofloxacin: 85.00%/90 min Garg et al. (2022
MnFe2O4/ZnO/tannic acid Solvothermal method Congo Red, 16 mg L−1 128 W Xenon lamp (visible light); 0.2 g L−1 84.20%/90 min Boutra et al. (2020

Recently, quantum dots (QDs) have been intensively studied due to their high specific surface area, low cost, numerous active sites, water insolubility, and excellent thermal stability (Sharma et al. 2019). Thanks to the unique quantum confinement effect derived from ultra-small size (2–10 nm), the accumulated electrons in QDs result in an enhanced light absorption range (Wang et al. 2020a). The combination of semiconductor and QDs has been reported as a cost-effective strategy to build photocatalytic heterojunction, which exhibits enhanced photocatalytic activity due to effective charge carrier separation (Yuan et al. 2021). In this section, some typical QDs are introduced as coupling semiconductor nanoparticles: ZnS, ZnO, Cu–In–S, and Ag–In–S. Although currently there have been no reports on the combination of these QDs with spinel ferrite, it is suggested that this combination is promising for the development of high performance photocatalysts.

Liu et al. reported a direct Z-scheme ZnS(QD)/Fe2O3(QD)/rGO ternary composite prepared via the hydrothermal method (Liu et al. 2020). This photocatalytic composite exhibited a strong redox ability (Figure 16(a) and 16(b)), 96.45% of dye was degraded within 40 min under UV light, much higher than pristine ZnS(QD) or Fe2O3(QD). However, the composite showed low efficiency under visible light (Figure 16(c)), since ZnS QD had a wide band gap and thus cannot be activated by visible light. From this viewpoint, it is suggested that further improvement is needed to transform ZnS(QD)-based composite into a visible-light-driven photocatalyst.
Figure 16

Proposed mechanism of the charge transfer route of ZnS(QD)/Fe2O3(QD)/rGO under (a, b) UV light and (c) visible light (Liu et al. 2020).

Figure 16

Proposed mechanism of the charge transfer route of ZnS(QD)/Fe2O3(QD)/rGO under (a, b) UV light and (c) visible light (Liu et al. 2020).

Close modal

Ikram et al. reported the photoelectrochemical conversion of ZnO(QD)/α-Fe2O3 thin films (Ikram et al. 2015). This composite showed 5.5 fold enhancement in photocurrent density under sunlight. α-Fe2O3 acted as solar energy harnessing material while ZnO QDs promoted charge carrier separation and transportation, since photo-induced holes can be trapped in the oxygen vacancy state, thus hindering the recombination of charge carriers. In conclusion, due to its wide band gap, ZnO(QD) exhibited similar optical properties to that of ZnS(QD), thus more work is suggested to be done to transform ZnO(QD)-based composite into a visible-light-driven photocatalyst.

Cu–In–S (CIS) has been reported as a spectral sensitizer, absorbing light across the entire visible light region (Yue et al. 2018). It can also inject electrons into a wide band gap semiconductor (Yue et al. 2018). Based on this, Raevskaya et al. reported a TiO2/CIS@ZnS photoanode for photoelectrochemical solar cells (Raevskaya et al. 2016), and the optimal cell exhibited the average conversion efficiency of 8.15%, under the irradiation of a Xe lamp (30 mW cm−2). This cell also showed excellent stability. CIS@ZnS was used as a light harvester, presenting enhanced light conversion efficiency compared with CIS, since ZnS suppressed the recombination of charge carriers. In conclusion, the visible light absorption ability of CIS is much better than that of ZnS or ZnO, thus it can be considered as a promising route to combine CIS(QD) with spinel ferrite to build high-performance photocatalyst under the condition of appropriate band alignment.

Shi et al. reported the Ag–In–S QDs for photocatalytic CO2 reduction to syngas under visible light (Shi et al. 2021). The Ag to In molar ratio affected the activity and selectivity by adjusting the band gap structure and charge carrier lifetime due to structural defects. The addition of Co(bpy)32+ (bpy = 2′2-bipyridine) can enhance the conversion of CO2 to CO as well as promote the photo-stability of Ag–In–S QDs. In conclusion, the excellent visible-light-driven catalytic activity of Ag–In–S QDs proved itself a good option to be combined with spinel ferrite for the development of a high-performance photocatalyst. The adjustable band gap structure of Ag–In–S QDs can be a flexible feature to couple Ag–In–S QDs with spinel ferrite with varied band positions to realize proper band alignment.

Due to the excellent photocatalytic activity, stability and magnetic property, spinel ferrite-based composites have been intensively studied in pollutant degradation applications. The related research findings present excellent removal performance of organic pollutants, offering an effective strategy for wastewater treatment, and proving spinel ferrite-based materials as a promising candidate for industrial scale applications. This paper mainly concludes the construction and photodegradation application of spinel ferrite-based materials: spinel ferrite/carbon material, spinel ferrite/Bi-based materials, spinel ferrite/TiO2 and spinel ferrite/ZnO, in which ZnFe2O4, NiFe2O4 or MnFe2O4 are chosen as spinel ferrites. The review compared three widely used preparation routes: hydrothermal (and solvothermal), co-precipitation and sol–gel auto-combustion methods. Among these, co-precipitation is promising for large-scale production, yet it still has certain drawbacks. This review also discussed the relationship between structural property and photocatalytic activity. Out of various junction structures, Z-scheme and S-scheme can realize both high photocatalytic activity and redox capability, and their loading onto function materials can further improve photodegradation performance, thus all these are considered key topics for future research. Moreover, there is a lack of research on pollutant degradation in real water bodies. All these aspects imply that, as for the practical application of spinel ferrite-based materials, there is still a long way to go, since a myriad of problems need to be fixed, which requires more systematic research work in the future.

The authors sincerely thank the financial support given from the National Natural Science Foundation of China (41977205).

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

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