Physical properties and photocatalytic activities of the well-defined morphological BiVO4 photocatalysts.
\r\n\t
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Currently, he is an Associate Professor at Physics Department, Kasetsart University, Thailand. He is a specialist in the development of smart sensors and intelligent systems for food, agricultural and environmental applications. He has received over twenty-eight research awards such as TRF–OHEC–SCOPUS Young Researcher Award in physical science, Invention Award from National Research Council of Thailand, Highest Citation Award for the young researcher, etc. He has served as a reviewer, guest editor, and associate editor for several scientific journals. He is Top 2% World Ranking of Scientists in Electrical & Electronic Engineering in 2020 and 2021 ranked by the Stanford University researcher team. He has published several dozens of articles in reputed journals, proceedings, book chapters, patents, and copyrights. His research interests cover the topics of modern Nanoscience and Nanotechnology research ranging from theoretical modeling of nanomaterials to fabrication of intelligent nanodevices such as DFTB, hybrid gas sensors, electronic nose, chemical sensors, electrochemical sensors, printed sensors, flexible electronics, IoT systems, intelligent food and agricultural sensors, and smart devices.",institutionString:"Kasetsart University",position:null,outsideEditionCount:0,totalCites:0,totalAuthoredChapters:"2",totalChapterViews:"0",totalEditedBooks:"2",institution:{name:"Kasetsart University",institutionURL:null,country:{name:"Thailand"}}}],coeditorOne:null,coeditorTwo:null,coeditorThree:null,coeditorFour:null,coeditorFive:null,topics:[{id:"14",title:"Materials Science",slug:"materials-science"}],chapters:null,productType:{id:"1",title:"Edited Volume",chapterContentType:"chapter",authoredCaption:"Edited by"},personalPublishingAssistant:{id:"453623",firstName:"Silvia",lastName:"Sabo",middleName:null,title:"Mrs.",imageUrl:"https://mts.intechopen.com/storage/users/453623/images/20396_n.jpg",email:"silvia@intechopen.com",biography:null}},relatedBooks:[{type:"book",id:"8398",title:"2D Materials",subtitle:null,isOpenForSubmission:!1,hash:"974977d9d7e76f2f4c93470c844f4cd5",slug:"2d-materials",bookSignature:"Chatchawal Wongchoosuk and Yotsarayuth Seekaew",coverURL:"https://cdn.intechopen.com/books/images_new/8398.jpg",editedByType:"Edited by",editors:[{id:"34521",title:"Associate Prof.",name:"Chatchawal",surname:"Wongchoosuk",slug:"chatchawal-wongchoosuk",fullName:"Chatchawal Wongchoosuk"}],productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"6391",title:"Intelligent System",subtitle:null,isOpenForSubmission:!1,hash:"e66e8d52ef62125a9f741ce0610d6899",slug:"intelligent-system",bookSignature:"Chatchawal Wongchoosuk",coverURL:"https://cdn.intechopen.com/books/images_new/6391.jpg",editedByType:"Edited by",editors:[{id:"34521",title:"Associate Prof.",name:"Chatchawal",surname:"Wongchoosuk",slug:"chatchawal-wongchoosuk",fullName:"Chatchawal Wongchoosuk"}],productType:{id:"1",chapterContentType:"chapter",authoredCaption:"Edited by"}},{type:"book",id:"6320",title:"Advances in Glass Science and Technology",subtitle:null,isOpenForSubmission:!1,hash:"6d0a32a0cf9806bccd04101a8b6e1b95",slug:"advances-in-glass-science-and-technology",bookSignature:"Vincenzo M. 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In particular, various industrial processes and human activities contaminate the global water supply, which is a serious problem for living beings. During the past decades, great efforts have been made on the degradation of organic wastewater pollutants. The visible-light-driven photocatalysis attracts much attention, since such a photocatalytic process can directly convert organic pollutants (e.g., methylene blue (MB), methyl orange (MO), rhodamine B (RhB), phenol, and etc.) to harmless products (CO2 and H2O) under sunlight irradiation.
\nThe organic dye models (MB, MO, and RhB) in textile and other industrial effluents have become one series of the major environmental contaminants, which have serious implications on the environment and human health [2]. Meanwhile, phenol is a widely used chemical and present in a great variety of emitted waste effluents. Organic dyes and phenol degrade slowly in the environment and are extremely toxic, carcinogenic, teratogenic, and refractory in nature [3]. Therefore, tremendous efforts have been made to fabricate high-efficiency photocatalysts for the control of wastewater pollution.
\nAs one of the earliest studied
Semiconductor is a kind of materials with electrical conductivity between conductor (such as metals) and insulator (such as ceramics). The unique electronic property of a semiconductor is characterized by its valence band (VB) and conduction band (CB). The VB of a semiconductor is formed by the interaction of the highest occupied molecular orbital (HOMO), while the CB is formed by the interaction of the lowest unoccupied molecular orbital (LUMO). There is no electron state between the top of the VB and the bottom of CB. The energy range between CB and VB is called forbidden bandgap (also called bandgap energy), which is usually denoted as
As shown in reaction 1, the photocatalytic reaction initiates from the generation of electron−hole pairs upon light irradiation. When a semiconductor photocatalyst absorbs photons with energy equal to or greater than its
These photogenerated electron−hole pairs may further be involved in the following three possible processes [9]: (i) successfully migrating to the surface of semiconductor, (ii) being captured by the defect sites in bulk and/or on the surface region of semiconductor, and (iii) recombining and releasing the energy in the form of heat or photon. The last two processes are generally viewed as deactivation processes because the photogenerated electrons and holes do not contribute to the photocatalytic reactions. Only the photogenerated charges that reach to the surface of semiconductor can be available for photocatalytic reactions. The defect sites in the bulk and on the surface of semiconductor may serve as the recombination centers for the photogenerated electrons and holes, which would decrease the efficiency of the photocatalytic reaction.
\nIt is well known that the photocatalytic activity of a semiconductor depends strongly upon three factors: adsorption behavior, photoresponsive region, and separation efficiency of electron–hole pairs [10]. The adsorption behavior can usually be enhanced by improving the surface areas of catalysts. In this aspect, how to extend the photoresponsive region and improve the separation efficiency of electron–hole pairs are important factors on the photocatalytic performance of a semiconductor [11]. The way to extend the photoresponsive region of a semiconductor photocatalyst is mainly the doping of nonmetals or transition metals, which can also improve the separation efficiency of electron–hole pairs and increase the oxidation power of photogenerated carriers [12, 13]. In general, noble metals (e.g., Ag, Pt, Au, and Pd) have been used as electron acceptors to separate the photoinduced hole–electron pairs and promote the interfacial charge transfer processes [14].
\nGenerally speaking, physicochemical properties of a material may be quite different depending on its crystal phase structure. The phase structure of BiVO4 is one of the important factors determining its photocatalytic performance [15]. BiVO4 has mainly three polymorphs in nature, including zircon–tetragonal, scheelite–tetragonal, and scheelite–monoclinic. The zircon–tetragonal phase can be formed via a low-temperature (100°C) synthesis route, whereas the scheelite-monoclinic phase can be generated using a high-temperature (400–600°C) synthesis method [16]. Moreover, the phase transformation between the scheelite monoclinic and the scheelite tetragonal can occur reversibly at 255°C [17]. It has been confirmed that the sheelite monoclinic structure of BiVO4 is the most photocatalytically active under visible-light irradiation. The greater reactivity can be associated with the energy band structure since monoclinic and tetragonal BiVO4 have bandgap energies of 2.4 and 2.9 eV, respectively. [8, 18, 19] Though BiVO4 has better photocatalytic performance, various strategies have been proposed to further improve its activity. In addition to the crystal structure, the photocatalytic property also strongly depends upon the morphology of BiVO4 [20]. Different morphological semiconductor photocatalysts have been prepared by many researchers. Efficient charge separation is the most important factor that determines the photocatalytic performance [9]. Furthermore, creation of heterjunction [21] and porous structure [22] as well as doping of element(s) [23] and using of support [24] are also effective strategies for improving charge separation efficiency.
\nAs one of new photocatalysts, monoclinic BiVO4 (
Photocatalyst | \nCrystal structure | \nSurface area (m2/g) | \nReaction condition | \nDegradation efficiency and light illumination time | \nReferences | \n|
---|---|---|---|---|---|---|
Sphere-like BiVO4 | \nMonoclinic | \n1.75 | \n− | \nVisible light, 80 mL RhB (0.01 mmol/L), 0.1 g sample | \n100% and 20 min | \n[2] | \n
\n | Monoclinic | \n− | \n− | \nUV light, RhB | \n84.1% and 2.5 h | \n[6] | \n
\n | Monoclinic | \n8.4 | \n2.45 | \nVisible light, 200 mL MO (0.01 mmol/L), 0.1 g sample | \n84% and 2 h | \n[22] | \n
\n | Monoclinic | \n10 | \n2.37 | \nSunlight, 50 mL phenol (25 mg/L), 0.3 mL H2O2, 0.1 g sample | \n100% and 1.5 h | \n[29] | \n
\n | Monoclinic | \n2.62 | \n2.48 | \nVisible light, 100 mL RhB (0.01 mmol/L), 0.08 g sample | \n97.7% and 6 h | \n[30] | \n
\n | Monoclinic | \n− | \n2.5 | \nVisible light, 100 mL RhB, 0.01 g sample | \n80% and 50 min | \n[31] | \n
\n | Tetragonal | \n− | \n2.81 | \nSunlight, 100 mL MB (5 mg/L), 0.1 g sample | \n90% and 5 h | \n[32] | \n
\n | Monoclinic | \n24.4 | \n2.50 | \nBlue light, 50 mL MB (0.01 mmol/L), 0.005 g sample | \n100% and 5 h | \n[33] | \n
\n | Monoclinic | \n85.4 | \n2.38 | \nVisible light, 20 mL MB (20 mg/L), 0.02 g sample | \n63% and 2 h | \n[34] | \n
\n | Monoclinic | \n0.7 | \n2.42 | \nVisible light, 100 mL MB (0.01 mmol/L), 0.01 g sample | \n90% and 3 h | \n[35] | \n
Flower-like BiVO4 | \nMonoclinic | \n0.9 | \n2.3 | \nVisible light, MB (10 mg/L), 1 g/L sample | \n60% and 2 h | \n[28] | \n
\n | Monoclinic | \n61.6 | \n2.14 | \nVisible light, 20 mL MB (20 mg/L), 0.02 g sample | \n75% and 2 h | \n[34] | \n
\n | Monoclinic | \n− | \n2.46 | \nSunlight, 100 mL MO (10 mg/L), 0.5 g sample | \n58% and 4 h | \n[36] | \n
\n | Monoclinic | \n1.6 | \n2.45 | \nSunlight, 200 mL RhB (5 mg/L), 0.1 g sample | \n62% and 10 h | \n[37] | \n
\n | Monoclinic | \n2.1 | \n2.52 | \nVisible light, 100 mL MO (0.01 mmol/L), 0.1 g sample | \n60% and 4 h | \n[38] | \n
Rod-like BiVO4 | \nMonoclinic | \n3.5 | \n2.46 | \nSunlight, 200 mL RhB (10 mg/L), 0.2 g sample | \n98.3% and 8 h | \n[27] | \n
\n | Monoclinic | \n4.3 | \n2.26 | \nVisible light, 100 mL MB (0.01 mmol/L), 0.01 g sample | \n90% and 2 h | \n[35] | \n
\n | Monoclinic | \n3.8 | \n2.47 | \nVisible light, 100 mL MO (0.01 mmol/L), 0.1 g sample | \n87% and 4 h | \n[38] | \n
\n | Monoclinic/tetragonal | \n− | \n2.46 | \nVisible light, 100 mL RhB (10 mg/L), 0.04 g sample | \n39.5% and 2.5 h | \n[39] | \n
\n | Monoclinic | \n− | \n2.45 | \nVisible light, 100 mL RhB (0.01 mmol/L), 0.2 g sample | \n96% and 50 min | \n[40] | \n
Peanut-like BiVO4 | \nMonoclinic | \n10.3 | \n2.4 | \nSunlight, 200 mL RhB (5 mg/L), 0.1 g sample | \n61% and 10 h | \n[37] | \n
\n | Monoclinic | \n0.54 | \n2.4 | \nSolar light, 100 mL crystalviolet (0.02 mmol/L), 0.05 g sample | \n98% and 1 h | \n[41] | \n
\n | Monoclinic | \n33.9 | \n2.44 | \nVisible light, 100 mL MB (10 mg/L), 0.1 g sample | \n95% and 225 min | \n[42] | \n
\n | Monoclinic | \n5.4 | \n2.35 | \nUV–Vis light, 100 mL MB (10 ppm), 1 g/L sample | \n40% and 2 h | \n[43] | \n
Polyhedron- like BiVO4 | \nMonoclinic | \n0.9 | \n2.34 | \nVisible light, 100 mL MB (0.01 mmol/L), 0.01 g sample | \n90% and 2 h | \n[35] | \n
\n | Monoclinic | \n3.97 | \n2.25 | \nVisible light, 50 mL RhB (0.015 mmol/L), 0.1 g sample | \n60% and 10 h | \n[44] | \n
\n | Monoclinic | \n− | \n2.35 | \nVisible light, 30 mL MB (5 mg/L), 0.1 g sample | \n81.6% and 160 min | \n[45] | \n
\n | Monoclinic | \n0.4 | \n2.35 | \nVisible light, alachlor (50 mg/L), 1 g/L sample | \n97% and 6 h | \n[46] | \n
Olive-like BiVO4 | \nMonoclinic | \n0.91 | \n2.40 | \nSunlight, 50 mL MB (10 mg/L), 0.1 g sample | \n18% and 3.5 h | \n[26] | \n
\n | Monoclinic | \n4.6 | \n2.40 | \nSunlight, 200 mL RhB (5 mg/L), 0.1 g sample | \n97% and 10 h | \n[37] | \n
\n | Monoclinic | \n− | \n2.50 | \nVisible light, 100 mL RhB (10 mg/L), 0.04 g sample | \n50.5% and 2.5 h | \n[39] | \n
\n | Monoclinic | \n− | \n2.45 | \nVisible light, 100 mL MB (10 mg/L), 0.1 g sample | \n67% and 225 min | \n[42] | \n
Microtube-like BiVO4 | \nMonoclinic | \n6.6 | \n2.33 | \nVisible light, 100 mL MB (0.01 mmol/L), 0.01 g sample | \n90% and 3 h | \n[35] | \n
\n | Monoclinic | \n− | \n2.36 | \nVisible light, 100 mL RhB (0.01 mmol/L), 0.5 mmol sample | \n96% and 3 h | \n[47] | \n
\n | Monoclinic | \n0.3 | \n2.36 | \nVisible light, MO (20 mg/L), 0.01 g sample | \n95% and 3 h | \n[48] | \n
\n | Monoclinic | \n3.46 | \n2.48 | \nVisible light, 100 mL RhB (0.01 mmol/L), 0.2 g sample | \n100% and 5 h | \n[49] | \n
Dumbbell-like BiVO4 | \nMonoclinic | \n4.6 | \n2.43 | \nVisible light, 200 mL RhB (5 mg/L), 0.1 g sample | \n89% and 10 h | \n[37] | \n
\n | Monoclinic | \n− | \n2.51 | \nVisible light, 600 mL RhB (0.01 mmol/L), 0.3 g sample | \n90% and 4.5 h | \n[50] | \n
\n | Monoclinic | \n9.87 | \n2.25 | \nSunlight, 100 mL ofloxacin (20 mg/L), 0.1 g sample | \n80.8% and 1 h | \n[51] | \n
\n | Monoclinic | \n53.6 | \n2.42 | \nVisible light, 100 mL RhB (0.01 mmol/L), 0.1 g sample | \n100% and 1 h | \n[52] | \n
Needle-like BiVO4 | \nMonoclinic | \n− | \n− | \nSunlight, 200 mL RhB (5 mg/L), 0.1 g sample | \n40% and 10 h | \n[37] | \n
\n | Monoclinic | \n2.0 | \n2.41 | \nUV–Vis light, MB (10 ppm), 1 g/L sample | \n60% and 2 h | \n[43] | \n
\n | Monoclinic | \n17.63 | \n2.42 | \nVisible light, 100 mL MB (10 mg/L), 0.005 g sample | \n81% and 200 min | \n[53] | \n
\n | Monoclinic | \n1.6 | \n2.38 | \nUV–Vis light, MB (10 ppm), 1 g/L sample | \n66% and 3 h | \n[54] | \n
Dendrite-like BiVO4 | \nMonoclinic/tetragonal | \n1.88 | \n2.52 | \nVisible light, 100 mL MB (20 mg/L), 0.1 g sample | \n95% and 3 h | \n[16] | \n
Butterfly-like BiVO4 | \nMonoclinic | \n1.22 | \n2.34 | \nSunlight, 50 mL MB (10 mg/L), 0.1 g sample | \n74.8% and 3.5 h | \n[26] | \n
Nanosheet-like BiVO4 | \nMonoclinic | \n− | \n3.3 | \nVisible light, 100 mL RhB, 0.01 g sample | \n50% and 50 min | \n[31] | \n
Leaf-like BiVO4 | \nMonoclinic | \n3.0 | \n2.34 | \nVisible light, 100 mL MB (0.01 mmol/L), 0.01 g sample | \n100% and 3 h | \n[35] | \n
Cuboid-like BiVO4 | \nMonoclinic | \n− | \n2.39 | \nSunlight, 100 mL MO (10 mg/L), 0.5 g sample | \n36% and 4 h | \n[36] | \n
Star-like BiVO4 | \nMonoclinic | \n− | \n2.44 | \nVisible light, 100 mL MB (10 mg/L), 0.1 g sample | \n76% and 225 min | \n[42] | \n
Bone-like BiVO4 | \nMonoclinic | \n10.32 | \n2.36 | \nVisible light, 100 mL MB (0.01 mmol/L), 0.005 g sample | \n61% and 200 min | \n[53] | \n
Physical properties and photocatalytic activities of the well-defined morphological BiVO4 photocatalysts.
Among different morphologies of BiVO4, microspherical or nanospherical BiVO4 particles are mostly reported. For example, Kunduz et al. [29] reported the preparation of monoclinic bismuth vanadate catalysts by hydrothermal method at different pH values and the removal of phenol from wastewater under natural sunlight illumination. Homogenous and spherical BiVO4 (particle size = 40–90 nm) was formed at pH = 2 (Figure 1d), the bandgap energy of the BiVO4 sample calculated from the absorption edge was 2.37 eV. This BiVO4 sample showed a high phenol conversion (100%) within 90 min of natural sunlight illumination, which was related to the morphology of BiVO4 (surface area = 10 m2/g).
\n(a−g, i, j) SEM and (h) TEM images of sphere-like BiVO4: (a) [
An one-pot template-free hydrothermal method was developed for the fabrication of BiVO4 microspheres with a tetragonal–monoclinic heterophasic structure [30]. The average diameter, bandgap energy, and BET surface area of the as-prepared BiVO4 microspheres were 4–6 μm, 2.48 eV, and 2.62 m2/g, respectively. The BiVO4 microspheres exhibited the highest photocatalytic activity with ca. Ninety-eight percentage degradation of RhB, remarkably superior to the pure monoclinic–scheelite BiVO4 and tetragonal–zircon BiVO4. The enhanced photocatalytic performance was attributed to the more effective separation of photogenerated carriers generated in the heterophasic BiVO4. Based on free radical scavenging and N2/O2-purging experiments, the degradation of RhB was believed to be driven mainly by the participation of •O2− and a lesser extent by the participation of holes and •OH.
\nSun et al. [31] prepared monoclinic scheelite BiVO4 hollow spheres (diameter = 3000–4000 nm) using a simple hydrothermal method with urea as guiding surfactant. It is observed that the RhB removal efficiency of BiVO4 hollow spheres was more than 80% after 50 min of visible-light irradiation without adding any H2O2. The superior activity of the
Monoclinic BiVO4 crystals with a particle size of 400–700 nm and a surface area of 1.75 m2/g were synthesized with the assistance of cetyltrimethylammonium bromide (CTAB) [2]. The given RhB solution (100 mL, 10−5 M) was completely degraded within 20 min of visible-light irradiation, which was due to the addition of CTAB during the catalyst fabrication process.
\nMany other researchers also reported various kinds of spherical BiVO4 crystallites (Table 1). For example, Ma et al. [32] prepared BiVO4 microspheres by a hydrothermal method in the presence of ethylenediamine tetraacetic acid (EDTA) for the removal of MB under sunlight illumination. Jiang et al. [22] reported porous spherical BiVO4 using urea as pH adjustor and polyvinyl pyrrolidone (PVP) as surfactant for MO degradation. Castillo et al. [33] studied flame-assisted synthesis of nanoscale spherical BiVO4 for the degradation of MB under visible-light illumination. These spherical BiVO4 samples exhibited good photocatalytic activities for the degradation of organic dyes under visible-light irradiation.
\nA flower-like morphology is usually composed of nanorods or nanosheets. Flower-like particles not only look beautiful, but also show good photocatalytic performance. Fan et al. [34] prepared monoclinic BiVO4 with a flower-like morphology via a simple hydrothermal route by adjusting the amount of surfactant (PVP K30). The photocatalytic efficiency for the decolorization of MB aqueous solution could reach 75% in 2 h of visible-light irradiation. The UV-visible diffuse reflectance absorption spectra reveal that this BiVO4 sample showed excellent absorption of visible light in the region of up to 600 nm, and the
SEM images of flower-like BiVO4: (a) [
An
\nFigure 3 shows the scanning electron microscopic (SEM) images of the rod-like BiVO4 samples. Hu et al. [27] reported the controlled fabrication of monoclinic BiVO4 with a rod-like structure and investigated the effect of calcination temperature on the sunlight-driven photocatalytic degradation of RhB. It is found that the sample calcined at 300°C exhibited a superior photocatalytic activity: RhB at an initial concentration of RhB lower than 10 mg/L could be completely decolorized after 6 h of sunlight irradiation. The bandgap energy and BET surface area of the rod-like BiVO4 photocatalyst were 2.46 eV and 3.5 m2/g, respectively. It can be observed from the SEM images (Figure 3) that the sample obtained after calcination at 300°C was composed of dispersive and short rod-like nanocrystals, thus displaying higher BET surface area, which would enhance the adsorption ability and hence improve the photocatalytic performance. Dai and coworkers [35] prepared monoclinic BiVO4 single crystallites with different morphologies using the triblock copolymer P123-assisted hydrothermal strategy with bismuth nitrate and ammonium metavanadate as metal source and various bases as pH adjustor. The rod-like BiVO4 sample was obtained at pH = 6 using NH3–H2O as pH adjustor. This sample displayed a higher surface area (3.2 m2/g) and a lower bandgap energy (2.26 eV). The rod-like BiVO4 sample showed excellent visible-light-driven photocatalytic activity for MB degradation in an aqueous solution under visible light irradiation: 90% degradation was achieved within 2 h of reaction. The unusually high visible-light-driven catalytic performance of monoclinically crystallized rod-like BiVO4 single crystallite was associated with its higher surface area and surface oxygen defect concentrations as well as the unique particle morphology.
\nSEM images of rod-like BiVO4: (a) [
Chen et al. [41] synthesized
SEM images of peanut-like BiVO4: (a) [
The physical properties and photocatalytic activities of the related polyhedral BiVO4 samples are summarized in Table 1. For example, Han et al. [44] reported the synthesis of monodispersed octahedral
SEM images of polyhedron-like BiVO4: (a) [
The physical properties and photocatalytic activities of several kinds of olive-like BiVO4 samples are listed in Table 1. Adopting the facile pH-dictated solvothermal route with the aid of either NH3–H2O or NaOH, Dong et al. [37] controllably synthesized the uniform monoclinic scheelite BiVO4 with hierarchical structures. As the pH value was adjusted to 6.26 using NaOH as the pH controller, the olive-like BiVO4 crystallites (bandgap energy = 2.40 eV) was generated. The olive-like BiVO4 sample showed a RhB degradation efficiency of 97% after 10 h of sunlight irradiation. It should be noted that this sample did not have a high surface area (4.6 m2/g) in comparison with other samples (surface area = 6.3–11.1 m2/g) obtained at different pH values. Apparently, the enhanced photocatalytic performance was not related to the surface area and aspect ratios of the fabricated photocatalysts, but to the unique morphological configurations. Lei et al. [39] synthesized olive-like BiVO4 using a hydrothermal strategy at pH = 3.0. As seen from the SEM images (Figure 6c), the sizes of the BiVO4 particles were predominantly 1.8–2.9 μm in length and 1.1–1.8 μm in diameter. The olive-like BiVO4 photocatalyst with a bandgap energy of 2.5 eV showed the highest photocatalytic activity, which could photocatalytically degrade 50.5% RhB after 150 min of visible-light illumination. The synergic effect of monoclinic phase and particle size contributed to the high photocatalytic efficiency of the olive-like BiVO4 photocatalyst.
\nSEM images of olive-like BiVO4: (a) [
Dai and coworkers [38] fabricated the BiVO4 samples with a monoclinic scheelite-type structure and various morphologies via an alcoho-hydrothermal route with Bi(NO3)3 and NH4VO3 as precursor and sodium hdroxide as pH adjustor in the absence or presence of triblock copolymer P123. It is realized that the pH of the precursor solution and the surfactant greatly affected the particle shape and architecture of BiVO4. Porous BiVO4 particles with spherical, flower-like, and sheet-like shapes were obtained in the presence of P123 at a reaction temperature of 180°C and a pH of 2, 7, or 10, respectively. A rod-like BiVO4 was generated at reaction temperature = 180°C and pH = 2. The four BiVO4 samples possessed a surface area of 1.4–3.8 m2/g and a bandgap energy of 2.47–2.54 eV. The difference in morphology of the BiVO4 particles gave rise to discrepancies in surface area, surface oxygen deficiency density, and (040) crystal face exposure. The rod-like BiVO4 sample that possessed the largest surface area, the highest surface oxygen deficiency density, the highest (040) crystal face exposure, and the lowest bandgap energy performed the best for MO degradation under visible-light irradiation. It is concluded that the particle morphology could influence the photocatalytic activity of BiVO4 and the rod-like shape was favorable for the improvement in photocatalytic activity.
\nThe physical properties and photocatalytic activities of tubular BiVO4 samples reported in the literature are summarized in Table 1. Single-crystalline monoclinic BiVO4 microtubes with a side length of 800 nm and a wall thickness of 100 nm (Figure 7b) were synthesized by a facile reflux method at 80°C [47]. The results of optical absorption experiments reveal that in addition to the UV light region, the BiVO4 microtubes also had a strong absorption in the visible-light region and the bandgap energy was estimated to be 2.36 eV. The RhB photodegradation over the BiVO4 microtubes was up to 96% after 3 h of visible-light irradiation, which could be associated with its distinctive morphology.
\nSEM images of microtube-like BiVO4: (a) [
Lu et al. [50] reported the controllable synthesis of dumbbell-like BiVO4 with a hierarchical nanostructure (Figure 8b) and a bandgap energy of 2.51 eV by employing a simple hydrothermal process. The photocatalytic degradation of RhB over the dumbbell-like BiVO4 sample was up to 90% within 4.5 h of visible-light irradiation, which was much higher than the P25 sample under the same reaction conditions. The good visible-light-driven photocatalytic efficiency was related to the exposed crystal planes, which could not only provide more active sites for the photocatalytic reaction but also effectively promote the separation efficiency of the electron–hole pairs. The physical properties and photocatalytic activities of several kinds of dumbbell-like BiVO4 samples reported in the literature are summarized in Table 1.
\nSEM images of dumbbell-like BiVO4: (a) [
The physical properties and photocatalytic activities of the typical needle-like BiVO4 samples are summarized in Table 1. For example, Obregón et al. [43] prepared monoclinic BiVO4 with different morphologies by a surfactant-free hydrothermal method through adjusting the pH value, precipitating agent type, hydrothermal temperature, and treatment time. The needle-like particles (Figure 9b) obtained with hydrothermal treatment at 100°C and NH4OH as pH controlling agent showed the best efficiency (50–60% after 2 h of UV-visible-light irradiation) for MB photodegradation. The surface areas of the samples obtained with hydrothermal treatment time of 2, 8, and 20 h were 30.2, 2.7, and 1.6 m2/g, respectively. It should be noted that the slight diminution in surface area had no clear effect on the photocatalytic performance of the sample. Therefore, the best performance was not associated with the surface area, but strongly affected by the crystallite size and morphology.
\nSEM images of needle-like BiVO4: (a) [
In addition to the well-morphological BiVO4 samples described above, there are some kinds of BiVO4 samples with other morphologies (Figure 10) that have been prepared. Most of them perform well in the photocatalytic degradation of organic dyes (Table 1).
\nSEM images of BiVO4 with various morphologies: (a) [
Most of the monoclinic BiVO4 samples obtained using the above methods are bulk materials and are low in surface area (<4 m2/g) [55, 56], which is unfavorable for photocatalytic applications. The reasons are as follows: (i) the amount of surface active sites is intimately related to the surface area [57, 58] and (ii) a porous architecture can increase the ability to capture incident light and the transfer of reactant and product molecules [59]. Therefore, it is of significance to controllably prepare BiVO4 photocatalysts that are porous in structure and high in surface area. The physical properties and photocatalytic activities of typical porous BiVO4 samples are summarized in Table 2.
\nPhotocatalyst | \nCrystal structure | \nCrystallite size (nm) | \nSurface area (m2/g) | \nReaction condition | \nDegradation efficiency and light illumination time | \nReferences | \n|
---|---|---|---|---|---|---|---|
3DOM BiVO4 | \nMonoclinic | \n185 | \n23.6 | \n2.50 | \nVisible light, 200 mL phenol (0.1 mmol/L), 0.2 g sample | \n94% and 3 h | \n[3] | \n
Mesoporous BiVO4 | \nMonoclinic | \n− | \n8.4 | \n2.45 | \nVisible light, 200 mL MO (0.01 mmol/L), 0.1 g sample | \n84% and 2 h | \n[22] | \n
Ordered mesoporous BiVO4 | \nMonoclinic | \n3.5 | \n59 | \n2.20 | \nVisible light, 80 mL MB (10 ppm), 0.08 g sample | \n85% and 3h | \n[57] | \n
Mesoporous BiVO4 | \nMonoclinic | \n− | \n11.8 | \n2.38 | \nVisible light, 200 mL phenol (0.2 mmol/L), 0.2 g sample | \n91% and 4 h | \n[60] | \n
Mesoporous BiVO4 | \nMonoclinic | \n2.2 | \n7.2 | \n2.38 | \nSunlight, 200 mL RhB (0.02 mmol/L), 0.2 g sample | \n100% and 1 h | \n[61] | \n
3DOM InVO4 | \nMonoclinic | \n130−140 | \n52.3 | \n2.50 | \nVisible light, 100 mL MB (10 mg/L), 0.1 g sample | \n98% and 1 h | \n[62] | \n
15 wt% CrO | \nMonoclinic | \n155−165 | \n45 | \n2.10 | \nVisible light, 100 mL RhB (15 mg/L), 0.1 g sample | \n99% and 200 min | \n[63] | \n
0.08 wt% Au/3DOM InVO4–BiVO4 | \nMonoclinic | \n22.3 | \n25.1 | \n2.54 | \nVisible light, 100 mL RhB (15 mg/L), 0.1 g sample | \n100% and 50 min | \n[64] | \n
0.08 wt% Au/3DOM InVO4–BiVO4 | \nMonoclinic | \n22.3 | \n25.1 | \n2.54 | \nVisible light, 100 mL MB (20 mg/L), 0.1 g sample | \n100% and 90 min | \n[64] | \n
0.08 wt% Au/3DOM InVO4–BiVO4 | \nMonoclinic | \n22.3 | \n25.1 | \n2.54 | \nVisible light, 100 mL RhB (15 mg/L) + MB (20 mg/L), 0.1 g sample | \n100% and 120 min | \n[64] | \n
0.17 wt% Pd/10 wt% AgBr/BiVO4 | \nMonoclinic | \n29.8 | \n12.9 | \n2.49 | \nVisible light, 100 mL 4-chlorophenol (15 mg/L), 0.05 g sample | \n100% and 2.5 h | \n[65] | \n
Physical properties and photocatalytic activities of the porous BiVO4 photocatalysts.
By adopting an alcoho-hydrothermal method with Bi(NO3)3 and NH4VO3 as precursor, sodium hydroxide as pH adjustor, ethanol and ethylene glycol as solvent, and dodecylamine, oleylamine, or oleic acid as surfactant, Dai and coworkers [59] prepared the BiVO4 materials with various shapes and/or mesoporous architectures. Photocatalytic activities of the as-derived samples were measured for phenol degradation in the presence of H2O2 under visible-light illumination, and effect of phenol concentration on photocatalytic performance was also probed. The authors pointed out that the surfactant and pH exerted a significant impact on particle morphology and crystal phase structure of BiVO4. Monoclinic BiVO4 samples with a porous olive-like shape could be fabricated with dodecylamine, oleylamine, or oleic acid as surfactant at a pH of 1.5 or 3.0 and a reaction temperature of 100°C. Short-rod-like monoclinic BiVO4 and porous sheet-layered spherical orthorhombic Bi4V2O11 were generated with dodecylamine as surfactant at reaction temperature = 100°C and pH = 7.0 and 11.0, respectively. Among all of the as-prepared BiVO4 samples, the porous sample with an olive-like morphology and a surface area of 12.7 m2/g (derived with dodecylamine and at pH = 1.5) exhibited the best visible-light-driven photocatalytic performance for phenol degradation (96% phenol was removed within 4 h of visible-light illumination).
\nJiang et al. [60] prepared monoclinic BiVO4 single crystallites with a porous octapod-like morphology using the P123-assisted hydrothermal method with bismuth nitrate and ammonium metavanadate as metal source and various bases as pH adjustor. The BiVO4 with a surface area of 11.8 m2/g and a bandgap energy of 2.38 eV showed excellent photocatalytic activities for the degradation of MB and phenol. Near 100 and 91% degradation of MB and phenol were achieved within 2 and 4 h of visible-light irradiation, respectively. The authors concluded that the high visible-light-driven catalytic performance of the porous octapod-like BiVO4 single crystallites was associated with the higher surface area, porous structure, and lower bandgap energy.
\nPeanut-shaped porous monoclinic BiVO4 with high yield was prepared using a simple template-free solvothermal method [61]. The pore size of the sample was 2.2 nm. Compared to the BiVO4 sample obtained hydrothermally, the porous BiVO4 sample exhibited a higher photocatalytic activity for the degradation of RhB and maintained high catalytic efficiency in the repeated recycles of the H2O2-containing system. Nearly, complete degradation of RhB was observed after 1 h of sunlight irradiation. It is noteworthy that the bandgap energy (2.38 eV) of the porous BiVO4 sample was higher than that (2.28 eV) of the nonporous BiVO4 sample, but the surface area (7.3 m2/g) of the former was considerably higher than that (2.1 m2/g) of the latter.
\nLi et al. [57] prepared ordered mesoporous monoclinic BiVO4 using mesoporous silica (KIT-6) as template. The mesoporous BiVO4 sample had a surface area of 59 m2/g and a pore size of 3.5 nm. The mesoporous BiVO4 exhibited a superior visible-light-driven photocatalytic activity for the degradation of MB. The degradation rate over the mesoporous BiVO4 sample was twice as active as the conventional BiVO4 sample, and 85% MB could be degraded after 3 h of visible-light illumination. The mesoporous BiVO4 sample possessed a large surface area, an ordered structure, and a small crystal size, thus resulting in excellent visible-light photocatalytic activity. The most attractive feature of the mesoporous BiVO4 semiconductor with a bandgap energy of 2.20 eV was its excellent visible-light response ability.
\nLiu et al. [3] prepared three-dimensionally ordered macroporous (3DOM) bismuth vanadates with a monoclinic crystal structure and high surface areas (18–24 m2/g) using ascorbic acid-assisted poly(methyl methacrylate) (PMMA)-templating strategy. The average macropore size and wall thicknesses of the BiVO4 samples were in the ranges of 160–185 and 24–70 nm, respectively. The photocatalytic performance of the porous BiVO4 samples was evaluated for the degradation of phenol in the presence of a small amount of H2O2 under visible-light illumination. The results showed that the conversion of phenol could reach 94% at an initial phenol concentration of 0.1 mmol/L after 3 h of visible-light irradiation. However, only 51% phenol was degraded over the bulk BiVO4 sample. The authors concluded that the excellent photocatalytic activity of 3DOM BiVO4 was associated with the high-quality 3DOM-structured BiVO4 that has a high surface area and a surface oxygen vacancy density.
\nWang et al. [62] reported the 3DOM-structured monoclinic InVO4 with high surface areas (35–52 m2/g) using the citric acid-, tartaric acid-, or ascorbic acid-assisted PMMA-templating strategy. From the SEM images, among the as-obtained samples, the InVO4 sample derived with PMMA in the presence of ascorbic acid showed the best quality in 3DOM architecture and a bandgap energy of 2.50 eV, with the macropore and nanovoid (on the skeletons) sizes being in the ranges of 130–160 and of 2–10 nm, respectively. Ninety-eight percentage MB was removed over the ascorbic acid-derived sample within 1 h of visible-light illumination. It is concluded that the excellent photocatalytic activity of this sample was related to its higher surface area and surface oxygen vacancy density and lower bandgap energy as well as the better quality of 3DOM structure.
\nDai and coworker [63] loaded certain amounts of chromia on the surface of 3DOM InVO4 to obtain the
Ji et al. [64] prepared the 3DOM InVO4–BiVO4 (InBi-3D) and its supported noble metal (
Dai and coworkers [65] prepared 3DOM BiVO4 (3D-BiV), AgBr/3D-BiV, and
Up to now, many investigations have been made to improve the photocatalytic performance of visible-light-responsive BiVO4 by doping heteroatoms that can efficiently avoid the charge recombination via trapping both electrons and holes. The co-doping with both cations and anions can also extend the visible-light absorption spectrum of BiVO4.
\nYin et al. [66] reported the one-step fabrication of high-performance C-doped BiVO4 photocatalyst with hierarchical structures under visible-light irradiation. The sample calcined at 400°C with a carbon content of 1.5 wt% showed the best photocatalytic MB degradation efficiency (100% degradation after 1 h of visible-light irradiation), which was 6.3 times higher than that over the pure BiVO4 sample (18% degradation after 1 h of visible-light irradiation). The XRD result showed that 1.5 wt% C-BiVO4 had a smaller crystalline size (18.7 nm) in comparison with pure BiVO4 (28.5 nm). Moreover, the bandgap energy of 1.5 wt% C-BiVO4 was about 2.39 eV, which was smaller than that (2.46 eV) of pure BiVO4. The photocatalytic performance was enhanced by C-doping because it improved the efficient separation and transfer of the photogenerated electrons and holes, as evidenced by the results of electron paramagnetic resonance (EPR) measurements.
\nTan et al. [67] fabricated a N-doped monoclinic BiVO4 photocatalyst via a facile microwave hydrothermal route using NaN3 as nitrogen source. The photocatalytic performance of the samples was evaluated by the decolorization of RhB under the simulated sunlight irradiation. After 4 h of the simulated sunlight irradiation, the degradation efficiencies over the pure BiVO4 and N-doped BiVO4 samples were 48 and 97%, respectively, indicating that N-doped BiVO4 was twice as active as pure BiVO4. The bandgap energy (2.0 eV) of N-doped BiVO4 was narrower than that (2.2 eV) of pure BiVO4, whereas the surface area (1.34 m2/g) of the former was close to that (0.21 m2/g) of the latter. The enhancement in photocatalytic activity could be attributable to the small particle size, narrow bandgap, and most importantly, the existence of multi-atomic BiVO4 centers and surface oxygen vacancies, which improved the mobility of charge carriers and inhibited the recombination of charge carriers.
\nF-doped BiVO4 particles were synthesized through a simple two-step hydrothermal process [68]. The XRD results demonstrated that the presence of F− ions did not change the phase structure of monoclinic BiVO4. F-doped BiVO4 was consisted of relatively uniform spheres with a diameter of 2–4 μm, and the bandgap energy was 2.39 eV. When the BiVO4/NaF molar ratio was 1: 0.9, the derived F-doped BiVO4 sample exhibited the highest photocatalytic MB degradation activity (99% MB was degraded after 3 h of visible-light irradiation). The appropriate amount of F– ions introduced into the BiVO4 crystal lattice might effectively restrain the recombination of photogenerated electron–hole pairs, thus facilitating the improvement in photocatalytic activity.
\nJiang et al. [69] prepared fluoride-doped BiVO4 with the different F/Bi molar ratios using the hydrothermal strategy with the hydrothermally derived BiVO4 as precursor and NH4F as fluoride source. All of the samples were of single-phase monoclinic scheelite structure. The doping of fluorine did not induce any alteration in crystal structure but changed the morphology of the sample particles. Compared to the undoped BiVO4 sample, the fluoride-doped BiVO4 samples showed higher oxygen adspecies concentration. When the F/Bi molar ratio was 0.29, the BiVO4 sample with a surface area of 14.6 m2/g and a bandgap energy of 2.42 eV performed the best for the degradation of phenol, giving a 97% phenol degradation efficiency within 2 h of visible-light irradiation. The authors concluded that the excellent photocatalytic performance of fluoride-doped BiVO4 was associated with its higher surface area and adsorbed oxygen species concentration, stronger optical absorbance performance, and lower bandgap energy.
\nOther anions (e.g., S and B) were also doped into the BiVO4 lattice (Table 3). For example, Guo et al. [70] found that S-doped BiVO4 was superior to pure BiVO4 in photocatalyzing the degradation of MB under visible-light irradiation, since an appropriate amount of S2− ions could improve the separation efficiency of photogenerated electron–hole pairs and hinder their recombination.
\nPhotocatalyst | \nCrystal structure | \nCrystallite size (nm) | \nSurface area (m2/g) | \nReaction condition | \nDegradation efficiency and light illumination time | \nReferences | \n|
---|---|---|---|---|---|---|---|
0.5 wt% C–BiVO4 | \nMonoclinic | \n35.7 | \n1.18 | \n− | \nVisible light, 200 mL phenol (5 mg/L), 0.2 g sample | \n88.7% and 5 h | \n[79] | \n
4 mol% B–BiVO4 | \nMonoclinic | \n23.0 | \n4.17 | \n2.34 | \nVisible light, 50 mL MO (15 mg/L), 0.01 g sample | \n96% and 50 min | \n[80] | \n
F–BiVO4 (F/Bi molar ratio = 0.29) | \nMonoclinic | \n− | \n14.6 | \n2.42 | \nVisible light, 200 mL phenol (0.2 mmol/L), 0.2 g sample | \n97% and 2 h | \n[69] | \n
0.17 wt% S–BiVO4 | \nMonoclinic | \n29.01 | \n3.18 | \n2.44 | \nVisible light, 100 mL MB (10 mg/L), 0.1 g sample | \n100% and 25 min | \n[70] | \n
0.08 wt% S–BiVO4 | \nMonoclinic | \n− | \n9.9 | \n2.40 | \nVisible light, 100 mL MB (0.005 mmol/L), 0.01 g sample | \n95% and 2 h | \n[71] | \n
1.40 wt% FeO | \nMonoclinic | \n− | \n5.1 | \n2.39 | \nVisible light, 100 mL MB (0.01 mmol/L), 0.01 g sample | \n100% and 90 min | \n[72] | \n
N–BiVO4 (N : Bi molar ratio = 0.2) | \nMonoclinic | \n49.8 | \n3.03 | \n2.23 | \nVisible light, 50 mL MO (10 mg/L), 0.01 g sample | \n85% and 50 min | \n[81] | \n
1% wt% Cu-BiVO4 | \nMonoclinic | \n39.78 | \n15.37 | \n1.90 | \nUV light, 90 mL MB (50 mg/L), 0.15 g sample | \n96% and 2 h | \n[82] | \n
2 mol% Mo-BiVO4 | \nMonoclinic | \n− | \n0.1 | \n2.39 | \nVisible light, MB (16 ppm), 0.1 g sample | \n100% and 1.5 h | \n[78] | \n
1.08 wt% Er-BiVO4 | \nMonoclinic | \n− | \n4.39 | \n2.11 | \nVisible light, 100 mL MO (10 mg/L), 0.2 g sample | \n99.4% and 3 h | \n[83] | \n
8 mol% Yb-BiVO4 | \nTetragonal | \n− | \n11.02 | \n2.9 | \nSunlight, 50 mL RhB (5 mg/L), 0.05 g sample | \n98% and 2 h | \n[84] | \n
3 mol% Yb/0.75 mol% Er-BiVO4 | \nMonoclinic/tetragonal | \n− | \n4 | \n2.35/2.68 | \nUV–vis–NIR light, 150 mL MB (10 ppm), 1 g/L sample | \n100% and 1 h | \n[77] | \n
0.8 wt% Eu/4 wt% B-BiVO4 | \nMonoclinic | \n44.89 | \n4.61 | \n2.28 | \nVisible light, 50 mL MO (15 mg/L), 0.015 g sample | \n90% and 50 min | \n[76] | \n
Physical properties and photocatalytic activities of the heteroatom-doped BiVO4 photocatalysts.
Employing a dodecylamine-assisted alcohol-hydrothermal method in the absence and presence of thiourea or Na2S, Zhao et al. [71] synthesized the sulfur-doped BiVO4 samples. The S-doped samples possessed a monoclinic scheelite structure and a surface area of 8.4–9.9 m2/g, and the bandgap energies of the S-doped BiVO4 samples were narrower than that of pure BiVO4. The S-doped BiVO4 sample with a S content of 0.78 wt% showed the best photocatalytic performance for the degradation of MB and formaldehyde. The photodegradation efficiency of MB was 92% within 2.5 h of visible-light illumination, but only 45% MB was degraded over pure BiVO4 under the same conditions. It is believed that a higher adsorbed oxygen species concentration and a lower bandgap energy were responsible for the excellent photocatalytic activity of the 0.78 wt% S-BiVO4 sample. These authors also investigated the porous olive-like morphological S-doped bismuth vanadate-supported iron oxide (
Cation doping is another approach to enhance the photocatalytic degradation efficiency of BiVO4, including transition metal doping and rare-earth doping (Table 3). For example, Li et al. [73] prepared Cu-doped monoclinic BiVO4 by a facile hydrothermal method and used the degradation of RhB to evaluate their photocatalytic activities. 1 wt% Cu-BiVO4 showed the best degradation performance: 95% of RhB was degraded within 80 min of visible-light irradiation, whereas pure BiVO4 can only degrade 60% of RhB within the same time. The bandgap energy of 1 wt% Cu-BiVO4 was 2.55 eV, resulting in the photoabsorption ability of the 1 wt% Cu-BiVO4 sample slightly stronger than undoped BiVO4 (bandgap energy = 2.57 eV). The amount of oxygen vacancies increased in the copper-doped samples. Possible factors that significantly enhance photocatalytic performance could be as follows: (i) Cu2+ substituted partial V5+ ions with lower oxidation state, generating a certain amount of oxygen vacancies; (ii) the generated oxygen vacancies can capture the electrons to suppress recombination of the photoinduced carriers; and (iii) the photoinduced carriers freely diffuse to the active sites on the surface of the photocatalyst where oxidation of organic species takes place.
\nZhou et al. [74] prepared a series of visible-light-sensitive monoclinic Co-BiVO4 photocatalysts by the heteronuclear complexing method with diethylenetriamine pentaacetic acid (DTPA) as chelating agent. The bandgap was narrowed by doping cobalt. The bandgap energies of the Co-doped BiVO4 samples at cobalt molar content of 0 and 1–10 wt% were 2.44 and 2.39–2.43 eV, respectively. The photocatalytic activity of Co-BiVO4 was studied by the decolorization of MB. The 5 wt% Co-BiVO4 sample exhibited the highest photocatalytic activity with a 85% of MB removal (65% of MB removal by pure BiVO4) within 5 h of visible-light irradiation. There was no significant loss of photocatalytic activity in three successive runs (each lasted for 6 h). Therefore, Co-BiVO4 was photocatalytically stable and resistant to photocorrosion during the photocatalytic degradation of organic dyes.
\nObregón et al. [75] synthesized Er-BiVO4 by means of a microwave-assisted hydrothermal method and examined the photodegradation of MB under sunlike excitation. The Er-doped BiVO4 sample showed a mixed phase of monoclinic and tetragonal structures. The optimal MB conversion was achieved over the sample with 0.75 atom% of erbium, over which the complete MB degradation was reached after 40 min of light illumination. The reaction rate obtained over this photocatalyst was 20 times higher than that over the undoped BiVO4 sample. Two clear absorption edges in the diffuse reflectance spectra of the sample appeared, and the corresponding bandgap energies were ca. 2.4 and 2.8 eV, which were associated with the monoclinic and tetragonal phases, respectively. In order to understand the role of erbium doping in the luminescent properties of the sample, the photoluminescence spectra upon 523 and 655 nm excitations were studied. Upon 655 nm excitation, the up-converted emission of the 0.75 atom% Er-BiVO4 sample was almost suppressed in the 400–600 nm range. Therefore, the dramatic improvement in photocatalytic activity induced by Er3+ doping could correlate to a co-operative process involving the electronic and luminescence mechanism. This sensitization mechanism could improve the photon efficiency of the photocatalytic process, and the formation of a monoclinic–tetragonal heterostructure could also be responsible for a more effective charge separation.
\nCo-doping with two different elements can exhibit better photocatalytic activity than the doping of single element. Wang et al. [76] reported that photodegradation of MO over BiVO4 doped with B species showed a higher MO degradation rate than the pure BiVO4 sample under visible-light irradiation. With the doping of europium, the photocatalytic MO degradation rate over Eu–B co-doped BiVO4 increased with the rise in europium content, and then decreased when the amount of europium was high enough. Co-doping of two different elements can further increase the photocatalytic activity due to the synergistic effects of a number of factors (such as higher specific area, smaller
Obregón et al. [77] also reported a highly active monoclinic–tetragonal BiVO4 by doping with Yb3+ and Er3+, which can completely photodegrade MB within 1 h of sunlike excitation. According to the results of structural and morphological characterization, one can deduce that the presence of Yb3+ and Er3+ induced the stabilization of the tetragonal phase probably due to its partial incorporation into the BiVO4 lattice. The improved photocatalytic efficiency was ascribed to two reasons: (i) the doping of lanthanide ions favored the co-existence of a monoclinic-tetragonal heterostructure, and such a structural configuration could optimize the charge separation and (ii) Yb3+ and Er3+ luminescence tandem led to a supportive photoluminescence up-conversion process, which could render the energy transfer process from erbium ions to the monoclinic BiVO4 phase.
\nIt should be noted that not all of the photocatalytic activity enhancement can be ascribed to the higher specific area, small crystallite sizes, smaller
In comparison with single-component photocatalyst, the heterostructure photocatalyst usually exhibits a higher photocatalytic performance for the degradation of various organic contaminants since it can facilitate the effective separation of photoinduced carriers and suppress the recombination of the electron–hole pairs, leaving more charge carriers to form reactive species [85].
\nAbsorption of photons by a semiconductor photocatalyst induces the photogenerated electrons and holes. The photogenerated charge carriers are separated or recombined on the way to the surface reaction sites. The charge separation is a crucial factor determining the light to conversion efficiency [9]. Therefore, much attention has been paid on increasing the charge separation efficiency. Fabrication of a heterojunction structure has been recognized as a useful strategy to avoid charge recombination in a semiconductor catalyst.
\nCo3O4 is a
Long et al. [86] prepared the Co3O4/BiVO4 composite photocatalyst with a
Yu and coworkers [87] also investigated the BiVO4 decorated with Co3O4, which showed a much higher photocatalytic activity than pure BiVO4. The authors believed that the high crystallinity of BiVO4 and the formed
Photocatalyst | \nSurface area (m2/g) | \nReaction condition | \nDegradation efficiency and light illumination time | \nReferences | \n|
---|---|---|---|---|---|
0.8 wt% Co3O4/BiVO4 | \n1.38 | \n− | \nVisible light, phenol (18 mg/L), 3 g/L sample | \n96% and 3 h | \n[86] | \n
3 wt% Co3O4/BiVO4 | \n8.03 | \n2.34 | \nVisible light, 80 mL acid orange II (20 mg/L), 0.05 g sample | \n78% and 5 h | \n[87] | \n
9 wt% BiVO4/TiO2 | \n107.7 | \n− | \nVisible light, 80 mL RhB (0.01 mmol/L), 0.08 g sample | \n79% and 6 h | \n[119] | \n
8 mol% BiVO4/TiO2 | \n17 | \n2.4 | \nVisible light, 50 mL RhB (1 mmol/L), 0.02 g sample | \n95% and 2 h | \n[120] | \n
40 mol% CeO2/BiVO4 | \n− | \n2.40 | \nVisible light, 100 mL RhB (5 mg/L), 0.15 g sample | \n73% and 4 h | \n[121] | \n
40 mol% CeO2/BiVO4 | \n− | \n2.46 | \nVisible light, 50 mL MB (0.02 mmol/L), 0.05 g sample | \n80% and 30 min | \n[89] | \n
30 mol% BiVO4/C3N4 | \n4.52 | \n2.45 | \nVisible light, 50 mL RhB (0.01 mmol/L), 0.05 g sample | \n85% and 5 h | \n[97] | \n
16.7 mol% BiVO4/C3N4 | \n12.99 | \n2.25 | \nVisible light, 100 mL MB (10 mg/L), 0.05 g sample | \n96% and 1 h | \n[98] | \n
1 wt% GR/BiVO4 | \n10 | \n2.38 | \nVisible light, 100 mL RhB (10 mg/L), 0.02 g sample | \n94% and 140 min | \n[122] | \n
3 wt% GR/BiVO4 | \n44.2 | \n1.94 | \nVisible light, 100 mL RhB (0.01 mmol/L), 0.6 mmol sample | \n100% and 10 min | \n[123] | \n
5 wt% RGO/BiVO4 | \n15.73 | \n2.41 | \nVisible light, 50 mL RhB (10 mg/L), 0.1 g sample | \n89% and 3 h | \n[100] | \n
3 wt% RGO/BiVO4 | \n4.84 | \n2.32 | \nSunlight, 200 mL RhB (7.5 mg/L), 0.15 g sample | \n96.5% and 6 h | \n[124] | \n
50 mol% Bi2WO6/BiVO4 | \n2.69 | \n2.08 | \nVisible light, 100 mL RhB (0.01 mmol/L), 0.1 g sample | \n100% and 0.5 h | \n[105] | \n
3 wt% Bi2WO6/BiVO4 | \n− | \n2.50 | \nVisible light, 50 mL phenol (10 mg/L), 0.15 g sample | \n81% and 6 h | \n[125] | \n
2.5 wt% Cu2O/BiVO4 | \n− | \n2.4 | \nVisible light, 50 mL MB (0.02 mmol/L), 0.05 g sample | \n100% and 75 min | \n[126] | \n
33 wt% Cu2O/BiVO4 | \n− | \n2.45 | \nVisible light, 100 mL phenol (100 mg/L), 0.2 g sample | \n41% and 6 h | \n[109] | \n
8 wt% CuO/BiVO4 | \n− | \n2.12 | \nVisible light, 30 mL MO (5 mg/L), 0.03 g sample | \n90.4% and 3 h | \n[127] | \n
1 wt% CuO/BiVO4 | \n2 | \n2.28 | \nVisible light, 100 mL acid orange 7 (0.05 mmol/L), 0.05 g sample | \n95% and 3 h | \n[128] | \n
Bi2O3/BiVO4 (Bi/V molar ratio = 1.1) | \n2.3 | \n2.40 | \nSunlight, 100 mL MB (0.02 mmol/L), 0.05 g sample | \n100% and 40 min | \n[129] | \n
Bi2O3/BiVO4 | \n1.48 | \n2.52 | \nVisible light, 100 mL RhB (0.01 mmol/L), 0.1 g sample | \n88% and 4 h | \n[113] | \n
43 mol% BiOBr/BiVO4 | \n− | \n2.38 | \nVisible light, 50 mL MB (10 mg/L), 0.05 g sample | \n97.2% and 4 h | \n[130] | \n
13 mol% BiOCl/BiVO4 | \n2.80 | \n2.38 | \nVisible light, 100 mL MO (0.0263 mmol/L), 0.1 g sample | \n85% and 11 h | \n[118] | \n
15 mol% BiIO4/BiVO4 | \n− | \n2.40 | \nVisible light, 50 mL RhB (0.01 mmol/L), 0.05 g sample | \n75% and 5 h | \n[131] | \n
MoS2/BiVO4 | \n− | \n− | \nVisible light, 100 mL MB (40 mg/L), 0.1 g sample | \n95% and 2 h | \n[132] | \n
80 mol% InVO4/BiVO4 | \n25.45 | \n2.52 | \nVisible light, 100 mL MB (0.02 mmol/L), 0.1 g sample | \n87% and 2 h | \n[133] | \n
16.7 wt% Ag2O/BiVO4 | \n− | \n2.06 | \nVisible light, 30 mL MO (5 mg/L), 0.03 g sample | \n91% and 160 min | \n[134] | \n
22.47 wt% AgBr/BiVO4 | \n− | \n− | \nVisible light, 75 mL MB (10 mg/L), 0.075 g sample | \n83.1% and 2.5 h | \n[135] | \n
10 mol% Ag3PO4/BiVO4 | \n− | \n2.46 | \nVisible light, 100 mL MB (10 mg/L), 0.05 g sample | \n92% and 10 min | \n[136] | \n
Physical properties and photocatalytic activities of the BiVO4-based heterojunction photocatalysts.
As we know, TiO2 has been widely used in environmental purification, H2 production, photosynthesis, CO2 reduction, etc. TiO2 is cheap, stable, nontoxic, and environmentally friendly, and hence an ideal model for investigations of semiconductor photocatalysts [9]. However, a major drawback of TiO2 is that only UV in the solar spectrum (about 3–5%) can be utilized to initiate the photocatalytic redox processes.
\n\nTable 4 summarizes the physical properties and photocatalytic activities of the TiO2/BiVO4 heterojunction samples reported in the literature. Xie et al. [88] prepared TiO2/BiVO4 nanocomposites with different molar ratios by impregnating BiVO4 particles into a TiO2 sol and after a thermal treatment at 450°C. The phenol degradation efficiency (74% after 1 h of visible-light illumination) over the TiO2/BiVO4 nanocomposites was as 4 times as that over pure BiVO4. The results of the transient-state surface photovoltage responses and atmosphere-controlled steady-state surface photovoltage spectra demonstrated that the lifetime of photogenerated charge carriers over the nanosized BiVO4 sample could be prolonged by approximately millisecond timescale after a proper molar ratio of nanocrystalline TiO2 was coupled. The promoted charge separation was responsible for the unexpected high photocatalytic activity for phenol degradation under visible-light irradiation.
\nApart from the most commonly used TiO2 catalyst, cubic fluorite cerium dioxide (CeO2), a semiconductor with a bandgap energy similar to that of TiO2 [89], shows a promising photocatalytic activity for the degradation of various organic dye pollutants [90]. CeO2 has been used in the splitting of water for H2 evolution and the degradation of phenol or chlorinated phenol under UV irradiation [91, 92]. However, the broad bandgap energy of CeO2 limits its applications in visible-light illumination [92]. As we know, the heterojunction structure in composite photocatalysts can dominate photoinduced charges in the direction of transport, distance of separation, and rate of recombination, leading to the efficient separation of photogenerated charges and thus greatly improving the photocatalytic activity of the heterojunction-structured sample. If BiVO4 is coupled with CeO2 to form a heterojunction structure, it is possible to generate visible-light-driven catalysts that show excellent photocatalytic performance.
\nWetchakun et al. [89] prepared the BiVO4/CeO2 nanocomposites by coupling a homogeneous precipitation method with a hydrothermal process. Photocatalytic activities of the as-prepared samples were examined for the degradation of MB, MO, and a mixture of MB and MO aqueous solutions under visible-light irradiation. The XRD patterns reveal that the BiVO4/CeO2 nanocomposite was composed of BiVO4 and CeO2, and BiVO4 in the composite sample was present in two crystalline phases. The sample with a BiVO4/CeO2 molar ratio of 0.6: 0.4 showed the highest photocatalytic activity (the highest MB degradation of 80% was achieved within 30 min of light irradiation). The absorption of BiVO4/CeO2 nanocomposites increased in the visible-light region (485–505 nm). Moreover, the low bandgap energy (2.46 eV) of BiVO4/CeO2 nanocomposites also influenced the dyes degradation.
\nThe physical properties and photocatalytic activities of the CeO2/BiVO4 heterojunction samples reported in the literature are summarized in Table 4.
\nAs a promising photocatalyst candidate for organic pollutant removal, graphite-like carbon nitride (g-C3N4) exhibits a relatively high photocatalytic activity under visible-light illumination due to its rapid separation of photoinduced charge carriers [93, 94]. The very negative CB (−1.13 eV) of g-C3N4 enables a strong reduction power of electrons (e−) in the CB. Nevertheless, there are still some shortcomings (e.g., the limited visible-light absorption below 450 nm and the low surface area) for the utilization of g-C3N4 in photocatalysis [95, 96]. Recently, continuous efforts have been made to improve the photocatalytic performance of g-C3N4. Among these, combining g-C3N4 with other semiconductors to construct heterostructures can effectively promote the separation rate of photoexcitated charge carriers [97]. BiVO4 and g-C3N4 are selected to construct heterojunction photocatalysts according to the following considerations: (i) both BiVO4 and g-C3N4 have been proved to be promising visible-light photocatalysts with desirable chemical stability and (ii) their suitable energy band alignments are beneficial for the separation of light-induced electron–hole pairs in the as-formed heterojunction photocatalysts. More importantly, the g-C3N4/BiVO4 heterojunction structures can be easily modified to achieve a controllable coverage of g-C3N4 on BiVO4 via a thermal annealing process, during which the g-C3N4 phase can be thermally etched by oxidation in air [7, 98].
\nLi et al. [98] prepared an efficient g-C3N4/BiVO4 heterojunction photocatalyst with BiVO4 networks decorated by discrete g-C3N4 nanoislands for highly efficient photocatalytic degradation of MB. There was the co-existence of BiVO4 and g-C3N4 phase in the composite samples. Among these heterojunction photocatalysts, the g-C3N4/BiVO4 heterojunction sample with a g-C3N4/BiVO4 ratio of 15: 3 performed the best photocatalytically in the degradation of MB. In this sample, the g-C3N4 phase displayed a discrete nanoisland morphology (5–10 nm in diameter), which was attached tightly to the surface of BiVO4. The as-synthesized g-C3N4/BiVO4 photocatalyst showed a superior visible-light photocatalytic activity, which was about 4.5 and 6.9 times as high as that over pure BiVO4 and g-C3N4, respectively. The enhanced photocatalytic activity can be ascribed to the increased charge separation efficiency, fully exposed reactive sites, and separated redox reaction sites as well as excellent visible-light response in the network composites. The physical properties and photocatalytic activities of the g-C3N4/BiVO4 heterojunction samples are summarized in Table 4.
\nReduced graphene oxide (rGO) with excellent electrical conductivity and high carrier mobility has been proved to be an excellent media for electron transfer. The widely accepted mechanism for the enhancement in photocatalytic performance is that chemical bonding between rGO and semiconductor could accelerate the transfer of photogenerated electrons in semiconductor to rGO, thus effectively suppressing the recombination of photogenerated carriers [99]. The rGO/BiVO4 composites have attracted much attention and significant research progress has been achieved.
\nWang et al. [100] fabricated the rGO/BiVO4 nanocomposite photocatalysts with excellent visible-light photocatalytic activities through electrostatic self-assembly via a simple surface charge modification on amorphous BiVO4 powders with silane coupling agent. The surface areas of rGO/BiVO4 and BiVO4 were 23.57 and 2.62 m2/g, respectively, and their corresponding bandgap energies were 2.41 and 2.47 eV. The photocatalytic MB degradation efficiency over rGO/BiVO4 was 94.1%, whereas that over bare BiVO4 was just 24.1% after 30 min of visible-light irradiation. The smaller particle size with a high surface area and an increased interfacial interaction in rGO/BiVO4 gave rise to increased photocatalytic reaction sites, extended photoresponding range, and enhanced photogenerated charge separation and transportation efficiency.
\nThe physical properties and photocatalytic activities of the rGO/BiVO4 heterojunction samples reported in the literature are summarized in Table 4.
\nAs one of the typical Aurivillius oxides with a layered structure, Bi2WO6 has attracted increasing attention in many research fields due to its excellent intrinsic physicochemical properties [101], including ferroelectric piezoelectricity, pyroelectricity, catalytic activity, non-linear dielectric susceptibility, and luminescence. Besides, Bi2WO6 is a typical
Cu2O is a
Wang et al. [109] prepared the Cu2O/BiVO4 photocatalysts with a heterogeneous nanostructure and a
Bi2O3 is an active
Guan et al. [113] synthesized the BiVO4 and BiVO4@Bi2O3 microspheres with a hollow olive-like morphology and a
In recent years, much attention has been paid on the bismuth oxyhalides (BiOX, X = Cl, Br, I) [114] and their composites in heterogeneous photocatalysis because of their characteristic hierarchical structures and unique optical properties [115]. Among them, BiOCl has drawn considerable attention as a novel photocatalyst due to their unique layered structure and high photocorrosion property [116]. However, BiOCl is similar to TiO2, which is semiconductor with a wide bandgap
A visible-light-active BiOCl/BiVO4 photocatalyst with a
Due to fast recombination of photogenerated electrons and holes or lack of appropriate reaction sites, single semiconductor-based photocatalysts usually do not show high efficiency in photocatalysis [9]. To improve the photocatalytic performance, it is necessary to fabricate composite photocatalysts by loading proper oxidation or reduction cocatalyst(s) on a semiconductor. In such a composite photocatalyst, the role of the cocatalyst(s) is as follows [9]: (i) providing trapping sites for the photogenerated charges and promoting the charge separation, thus enhancing the quantum efficiency; (ii) improving the photostability of the catalyst by timely consuming the photogenerated electrons and holes; and (iii) catalyzing the reactions by lowering the activation energy. Various kinds of cocatalysts have been applied to BiVO4 to improve the photocatalytic removal of organics, including metal cocatalysts, metal oxide cocatalysts, and metal sulfide cocatalysts. As early in 2005, Kohtani et al. [137] prepared silver particles loaded on BiVO4 by an impregnation method for the degradation of 4-
Chen et al. [138] prepared the Ag/BiVO4 composites using a one-step method with ethylene glycol and water as solvent and L-lysine as surfactant. The photocatalytic performance of the composites was evaluated for the degradation of MB in an aqueous solution under visible-light irradiation. Based on the XRD and XPS results, only a small part of the Ag presented as metallic Ag (Ag0) dispersed on the surface of BiVO4, whereas most of Ag was present in oxidized Ag (Ag+). The Ag particles with a size of about 5 nm were in close contact with BiVO4. More than 98% of MB could be degraded over 6.5 wt% Ag/BiVO4 within 100 min of visible-light illumination. The 6.5 wt% Ag/BiVO4 sample had a surface area of 4.84 m2/g and a bandgap energy of 2.4 eV. The results demonstrate that a proper amount of Ag in the composite could promote the separation of photogenerated electrons and holes.
\nAu/BiVO4 heterogeneous nanostructures were synthesized using a cysteine-linking strategy through the
Table 5 summarizes the physical properties and photocatalytic activities of BiVO4-supported reduction cocatalysts reported in the literature.
\n\nLi et al. [140] prepared the CuO/BiVO4 photocatalysts by an impregnation method. The highest MB photodegradation efficiency was obtained over the sample with a 5 atom% Cu content and after calcination at 300°C. MB could be completely degraded after 2 h of light irradiation. The bandgap energies of pure BiVO4 and 5 atom% CuO/BiVO4 were 2.40 and 2.34 eV, respectively. Moreover, the surface area (5.62 m2/g) of 5 atom% CuO/BiVO4 was higher than that (1.89 m2/g) of pure BiVO4. Therefore, the authors concluded that a proper Cu loading could effectively improve the photocatalytic activity.
\n\nPhotocatalyst | \nCrystal structure | \nCrystallite size (nm) | \nSurface area (m2/g) | \nReaction condition | \nDegradation efficiency and light illumination time | \nReferences | \n|
---|---|---|---|---|---|---|---|
6.5 wt% Ag/BiVO4 | \nMonoclinic | \n5 | \n4.83 | \n2.40 | \nVisible light, 100 mL MB (0.02 mmol/L), 0.05 g sample | \n98% and 100 min | \n[138] | \n
1.5 wt% Ag/BiVO4 | \nMonoclinic | \n10−30 | \n− | \n2.10 | \nVisible light, MB (10 mg/L), 1 g/L sample | \n98% and 2 h | \n[144] | \n
3.5 wt% Au/BiVO4 | \nMonoclinic | \n5 | \n− | \n2.54 | \nVisible light, 10 mL MO (5 mg/L), 0.01 g sample | \n100% and 50 min | \n[139] | \n
1 wt% Au/BiVO4 | \nMonoclinic | \n8−10 | \n− | \n2.0 | \nVisible light, 50 mL phenol (10 mg/L), 3 g/L sample | \n99% and 2.5 h | \n[145] | \n
1 mol% CuO/BiVO4 | \nMonoclinic | \n32.7 | \n5.62 | \n2.34 | \nUV light, 200 mL MB (10 mg/L), 0.2 g sample | \n100% and 2 h | \n[140] | \n
5.0 mol% Fe2O3/BiVO4 | \nMonoclinic | \n20.38 | \n15.27 | \n2.38 | \nVisible light, 50 mL MB (0.05 mmol/L), 0.05 g sample | \n81% and 0.5 h | \n[141] | \n
0.1 wt% Pt/0.1 wt% MnO | \nMonoclinic | \n− | \n− | \n− | \nVisible light, 100 mL MO (10 mg/L), 0.05 g sample | \n100% and 1.5 h | \n[142] | \n
0.03 wt% Pt/0.01 wt% RuO2/BiVO4 | \nMonoclinic | \n− | \n− | \n2.3 | \nVisible light, 30 mL thiophene (600 ppm), 0.05 g sample | \n78% and 3 h | \n[143] | \n
1 mol% Ag2O/BiVO4 | \nMonoclinic | \n100 | \n2.70 | \n2.31 | \nVisible light, 50 mL ibuprofen (10 mg/L), 0.04 g sample | \n96% and 4 h | \n[146] | \n
1 wt% PdO/BiVO4 | \nMonoclinic | \n− | \n− | \n1.63 | \nVisible light, 30 mL MO (10 mg/L), 0.2 g sample | \n100% and 15 h | \n[147] | \n
Physical properties and photocatalytic activities of the BiVO4-supported photocatalysts.
Chala et al. [141] prepared the pure BiVO4 and Fe-loaded BiVO4 samples by a hydrothermal method. Photocatalytic activities of the samples were examined using the degradation of MB under visible-light irradiation. The Fe/BiVO4 sample with an optimal iron loading of 5.0 mol% showed the best photodegradation performance (81%) within 30 min of visible-light illumination. The iron loading did not affect the crystal structure of BiVO4, and the iron oxides (mainly Fe2O3) might be loaded merely on the surface of BiVO4. The bandgap energies of BiVO4 and 5.0 mol% Fe/BiVO4 were 2.51 and 2.38 eV, respectively. Loading with Fe2O3 creates subband states in the bandgap of BiVO4 which could then be easily excited to produce more electron–hole pairs under visible-light irradiation, hence resulting in higher photocatalytic performance. Surface areas of the pure BiVO4 and 5.0 mol% Fe/BiVO4 samples were 6.44 and 15.27 m2/g, respectively, indicating that loading of BiVO4 with iron oxides led to an increase in surface area. The higher surface area could possibly provide more active sites on the catalyst surface, which gave rise to an enhancement in photocatalytic activity. The physical properties and photocatalytic activities of BiVO4-supported oxidation cocatalysts and dual cocatalysts reported in the literature are summarized in Table 5.
\nIn comparison with single cocatalyst-loaded BiVO4 photocatalysts stated above, Li et al. [142] prepared two types of photocatalysts (
According to the literature, the main factors influencing the degradation rate of organic dyes are hydroxyl radicals (•OH), superoxide radical (•O2−), dissolved oxygen (O2), and holes (h+). The mechanisms for degradation of organic dyes (such as MB, MO, and RhB) are similar. Taking an example, the photocatalytic degradation mechanism over the BiVO4 quantum tubes–graphene composite sample for the degradation of RhB under visible-light illumination is illustrated in Figure 11.
\nIt is well known that a complete photocatalytic process is generally divided into three stages: light harvesting, separation of photogenerated charges, and interfacial reactions [148]. In the photocatalytic reaction of converting dyes to CO2 and H2O over the BiVO4–graphene composite material, the electrons (e−) are provided by photoexcitation of BiVO4 (CB electrons). In this regard, BiVO4 can absorb visible light to generate electron–hole pairs (reaction (1)). In fact, the photogenerated electrons instantly transfer from the CB of BiVO4 to the carbon atoms of graphene (reaction (2)). Simultaneously, these electrons on the surface of graphene can be captured by the adsorbed O2 molecules to produce •O2− (reaction (3)). Meanwhile, the holes on the surface of BiVO4 can be scavenged by the ubiquitous H2O molecules or OH− to yield •OH radicals (reaction (4)). In this case, the RhB molecules can be subsequently destroyed into CO2 and H2O (reaction (5)) by the generated •O2− and OH radicals due to their high activities [123].
A schematic reaction mechanism illustrating the visible light-driven photodegradation of RhB over the
It is noteworthy that holes (h+) can directly react with RhB molecules to generate CO2 and H2O (reaction (6)). Moreover, in order to improve the photocatalytic performance, H2O2 is often added to the dye solution as electronic sacrificial agent. It has been reported that a small amount of H2O2 in the initial dye solution was beneficial for trapping e− to form •OH radicals (reaction (7)) and also inhibiting the recombination of e−/h+ pairs.
\nThe difference of degradation of phenol and its derivatives from that of degradation of organic dyes is that the intermediate products are usually generated, which are difficult to be completely degraded to CO2 and H2O.
There are at least 20 intermediates (see Figure 12) of phenol photodegradation [149], the photodegradation process of phenol is hence very complicated. Furthermore, the routes of phenol photodegradation are different under different experimental conditions. Although the active species for phenol degradation are also the •OH, •O2−, O2, and h+, phenol is difficult to be completely destroyed to CO2 and H2O.
\nChemical structures of the by-products derived from phenol photocatalytic degradation [
For example, Guo et al. [150] studied degradation of phenol (
Phenol photodegradation route [
Moreover, Devi and Rajashekhar [151] also proposed a possible phenol degradation mechanism over TiO2 under the conditions of UV light, catalyst dosage = 400 mg/L, phenol concentration = 20 mg/L, and ammonium persulfate (APS) = 100 mg/L), as shown in Figure 14.
\nBased on a plenty of literature, many possible phenol degradation mechanisms have been proposed. Unfortunately and inevitably, the by-products are always generated. It is noted that the toxicity of the by-products generated in phenol degradation processes may be stronger than phenol itself. Therefore, how to directly convert phenol into harmless products is still a big challenge.
\nPhenol photodegradation mechanism [
A large number of BiVO4 and its related materials with different morphologies and various structures, such as well-defined morphological BiVO4, porous BiVO4, heteroatom-doped BiVO4, BiVO4-based heterojunction, and supported BiVO4, have been successfully synthesized in the literature. Most of them show good or even excellent photocatalytic performance for the degradation of organic dyes, phenol or its derivatives under the illumination of visible light. The structure–photocatalytic performance relationship of these materials has been established, and the involved photocatalytic degradation mechanisms have been proposed.
\nDue to severe situations in water contamination, researchers have devoted themselves to resolve these problems. In particular, the photocatalytic technology has attracted more and more attention because of its unique advantages. However, it has still a long way to make photocatalytic technology widely practicable. Therefore, three strategies are suggested to further improve the photocatalytic performance: (i) It is greatly desired to design and fabricate novel and highly efficient photocatalytic materials; (ii) although photocatalytic reaction mechanisms have been studied for many years, it is still difficult to identify the elementary reaction steps, therefore
Among the cetacean, the dolphin is the common name of aquatic mammals. Over the last decades, aquatic mammal conservation is a global concern due to human anthropogenic activities and rapidly declining the biodiversity. Losses of aquatic mammals or biodiversity directly affect on ecosystem locally or internationally that concerned by the Convention of Biological Diversity (CBD) in 1992. Marine mammal conservation is continuing process which cannot ever be well-thought-out completely in south Asia. In the Bay of Bengal, Swatch of No-ground has been established as Marine Protected Area (MPA) for biological species. As a big delta basin Ganges, Brahmaputra, and Meghna river systems are present along with the coastal regions in Bangladesh. IUCN Bangladesh [1] reported 10 cetacean species are present in the aquatic ecosystem of Bangladesh include the Ganges river dolphin. All marine dolphins are included in the Family Delphinidae. The very little study occurred on the dolphins in the maritime area of Bangladesh, except some reports of species events [2, 3, 4, 5, 6, 7, 8]. According to WCS [9] about 1738 km2 areas are considered as a marine protected area (MPA) for marine mammal species, and MPA is constructed at the Northwest and Southeast geographic area of Bangladesh that is recognized with the Indian Ocean in Figure 1.
Map of dolphin occurrence in the maritime area, black color line box indicated site (WCS, 2015).
However, some author little studies completed on dolphins [7, 8, 9, 10, 11, 12] but the status of dolphin investigation is not sufficient in the maritime area of Bangladesh due to lack of funds, strategic plan, and awareness. Although, False Killer whale, Bryde’s whale, and Sperm whales are found in the marine water but different types of dolphins are survived in maritime areas of Bangladesh.
The species conservation effort should be a concern with ecological, behavioral, population, and species diversity. Among the mammal Irrawaddy dolphin, Indo-Pacific Humpback dolphin, Bottlenose dolphin, Spotted dolphin, Spinner dolphin, and Rough-toothed dolphin are present in the maritime area of Bangladesh in Figure 2. Only Ganges river dolphins survive in the freshwater, coastal water, and the mouth of the Ganges at Sundarban area.
Different types of dolphin occurred in the maritime area of Bangladesh. (1) Irrawaddy dolphin, (2) Indo-Pacific Humpback dolphin, (3) Indo-Pacific Bottlenose dolphin, (4) Spotted dolphin, (5) Spinner dolphin, and (6) Ganges river dolphin.
This dolphin name comes from the Irrawaddy River, Myanmar and endangered species among all cetacean species in the world. Its scientific name is
Number of species sighted in the maritime water of Bangladesh.
The Indo-Pacific humpback dolphin has been recorded in the marine water of Bangladesh and also sighted near the eastern India region [18]. This species scientific name is
This mammal scientific name is
The spotted dolphin is the most dominant animal in the cetacean groups in tropical area. Generally, Pantropical spotted dolphins occurred in the marine protected areas of the Bay of Bengal. This dolphin’s scientific name is
The Spinner dolphin’s scientific name is
This dolphin scientific name is
Mortality of dolphins in fishing nets and the highest level of water pollution through oil, plastic, and industrial waste are the extreme threats. Illegal fishing such as poisoning or electro fishing and large ship boat, vessel strikes, overfishing, sand and resources mining are also threat for dolphins. In Bangladeshi water, most of the dolphin species death occurs by fishing net specially gill net. Dolphin killing and hunting was extensive in several countries that also threat for the environment [2, 30, 31]. UNDP Bangladesh [16] reported that 130 dolphins were killed from 2007 to 2016 in the waters of Bangladesh which most of the species’ death by fishing nets and propellers of ships. GoB [32] also reported a total of 52 dolphins were lost by gillnets in the Sundarban area. Dolphin killing occurred due to collecting body parts has required in fisheries that are used as dolphin oil [33]. Although, several organizations are trying to conserve dolphins but it’s not enough, such as SharkLab, United Nations Development Program (UNDP), the Global Environment Facility (GEF), the Forest Department, IUCN Bangladesh, and World Conservation Society (WCS). Dolphin conservation is highly important for other aquatic species in the ecosystem as well as the better health regulator of water. Bangladesh Government has been attentive for the marine protected area (MPA) to conserve cetaceans whereas most of the dolphin sightings occurred in the water. We should concern about bycatch through fishing gear, awareness, and biological data monitoring to conserve dolphins as well as their habitat. Six sanctuaries have been recognized as conservation areas by the Government of Bangladesh for marine mammal and other species. The Swatch of no-Ground is also known as a special conservation area for biological resources.
The present condition does not well promise for the future plan of the dolphins. The different key programs should consider improving dolphin conservation. Such as taxonomy study through morphologically and genetically, impact and risk assessment, habitat management assessment, ocean traffic plan, population size and movement, ecology, water quality, environmental hazards and threat, etc. Also season wise fisheries interaction should high attention because dolphin mortality rate increases due to fishing and human anthropogenic activities. Monitoring programs of dolphins, their primary habitat, size, structure, and population can guide or lead delta plan, conservation plan, and climate movement.
We would like to express thank all members who contributed to the dolphin research. Also, thanks to Dr. Mohammad Saiful Islam, chairman, Department of Zoology, JnU for his special discussion on marine mammals. In specific, we would like to express our heartfelt gratitude to Rafi, Nur Alam, Kisor Kumar Sarkar, and Hasan Al Razi. Special thanks to Ifat Jahan for picture editing and collection. We also thank an unsigned assessor for useful notes on a former draft.
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Saxena",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bRET3QAO/Profile_Picture_2022-05-10T10:10:26.jpeg",institutionString:"King George's Medical University",institution:{name:"King George's Medical University",institutionURL:null,country:{name:"India"}}}],equalEditorOne:null,equalEditorTwo:null,equalEditorThree:null}]},subseriesFiltersForPublishedBooks:[{group:"subseries",caption:"Bacterial Infectious Diseases",value:3,count:2},{group:"subseries",caption:"Parasitic Infectious Diseases",value:5,count:4},{group:"subseries",caption:"Viral Infectious Diseases",value:6,count:7}],publicationYearFilters:[{group:"publicationYear",caption:"2022",value:2022,count:2},{group:"publicationYear",caption:"2021",value:2021,count:4},{group:"publicationYear",caption:"2020",value:2020,count:3},{group:"publicationYear",caption:"2019",value:2019,count:3},{group:"publicationYear",caption:"2018",value:2018,count:1}],authors:{paginationCount:229,paginationItems:[{id:"318170",title:"Dr.",name:"Aneesa",middleName:null,surname:"Moolla",slug:"aneesa-moolla",fullName:"Aneesa Moolla",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/318170/images/system/318170.png",biography:"Dr. Aneesa Moolla has extensive experience in the diverse fields of health care having previously worked in dental private practice, at the Red Cross Flying Doctors association, and in healthcare corporate settings. She is now a lecturer at the University of Witwatersrand, South Africa, and a principal researcher at the Health Economics and Epidemiology Research Office (HE2RO), South Africa. Dr. Moolla holds a Ph.D. in Psychology with her research being focused on mental health and resilience. In her professional work capacity, her research has further expanded into the fields of early childhood development, mental health, the HIV and TB care cascades, as well as COVID. She is also a UNESCO-trained International Bioethics Facilitator.",institutionString:"University of the Witwatersrand",institution:{name:"University of the Witwatersrand",country:{name:"South Africa"}}},{id:"419588",title:"Ph.D.",name:"Sergio",middleName:"Alexandre",surname:"Gehrke",slug:"sergio-gehrke",fullName:"Sergio Gehrke",position:null,profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0033Y000038WgMKQA0/Profile_Picture_2022-06-02T11:44:20.jpg",biography:"Dr. Sergio Alexandre Gehrke is a doctorate holder in two fields. The first is a Ph.D. in Cellular and Molecular Biology from the Pontificia Catholic University, Porto Alegre, Brazil, in 2010 and the other is an International Ph.D. in Bioengineering from the Universidad Miguel Hernandez, Elche/Alicante, Spain, obtained in 2020. In 2018, he completed a postdoctoral fellowship in Materials Engineering in the NUCLEMAT of the Pontificia Catholic University, Porto Alegre, Brazil. He is currently the Director of the Postgraduate Program in Implantology of the Bioface/UCAM/PgO (Montevideo, Uruguay), Director of the Cathedra of Biotechnology of the Catholic University of Murcia (Murcia, Spain), an Extraordinary Full Professor of the Catholic University of Murcia (Murcia, Spain) as well as the Director of the private center of research Biotecnos – Technology and Science (Montevideo, Uruguay). Applied biomaterials, cellular and molecular biology, and dental implants are among his research interests. He has published several original papers in renowned journals. In addition, he is also a Collaborating Professor in several Postgraduate programs at different universities all over the world.",institutionString:null,institution:{name:"Universidad Católica San Antonio de Murcia",country:{name:"Spain"}}},{id:"342152",title:"Dr.",name:"Santo",middleName:null,surname:"Grace Umesh",slug:"santo-grace-umesh",fullName:"Santo Grace Umesh",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/342152/images/16311_n.jpg",biography:null,institutionString:null,institution:{name:"SRM Dental College",country:{name:"India"}}},{id:"333647",title:"Dr.",name:"Shreya",middleName:null,surname:"Kishore",slug:"shreya-kishore",fullName:"Shreya Kishore",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/333647/images/14701_n.jpg",biography:"Dr. Shreya Kishore completed her Bachelor in Dental Surgery in Chettinad Dental College and Research Institute, Chennai, and her Master of Dental Surgery (Orthodontics) in Saveetha Dental College, Chennai. She is also Invisalign certified. She’s working as a Senior Lecturer in the Department of Orthodontics, SRM Dental College since November 2019. She is actively involved in teaching orthodontics to the undergraduates and the postgraduates. Her clinical research topics include new orthodontic brackets, fixed appliances and TADs. She’s published 4 articles in well renowned indexed journals and has a published patency of her own. Her private practice is currently limited to orthodontics and works as a consultant in various clinics.",institutionString:null,institution:{name:"SRM Dental College",country:{name:"India"}}},{id:"323731",title:"Prof.",name:"Deepak M.",middleName:"Macchindra",surname:"Vikhe",slug:"deepak-m.-vikhe",fullName:"Deepak M. Vikhe",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/323731/images/13613_n.jpg",biography:"Dr Deepak M.Vikhe .\n\n\t\n\tDr Deepak M.Vikhe , completed his Masters & PhD in Prosthodontics from Rural Dental College, Loni securing third rank in the Pravara Institute of Medical Sciences Deemed University. He was awarded Dr.G.C.DAS Memorial Award for Research on Implants at 39th IPS conference Dubai (U A E).He has two patents under his name. He has received Dr.Saraswati medal award for best research for implant study in 2017.He has received Fully funded scholarship to Spain ,university of Santiago de Compostela. He has completed fellowship in Implantlogy from Noble Biocare. \nHe has attended various conferences and CDE programmes and has national publications to his credit. His field of interest is in Implant supported prosthesis. Presently he is working as a associate professor in the Dept of Prosthodontics, Rural Dental College, Loni and maintains a successful private practice specialising in Implantology at Rahata.\n\nEmail: drdeepak_mvikhe@yahoo.com..................",institutionString:null,institution:{name:"Pravara Institute of Medical Sciences",country:{name:"India"}}},{id:"204110",title:"Dr.",name:"Ahmed A.",middleName:null,surname:"Madfa",slug:"ahmed-a.-madfa",fullName:"Ahmed A. Madfa",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/204110/images/system/204110.jpg",biography:"Dr. Madfa is currently Associate Professor of Endodontics at Thamar University and a visiting lecturer at Sana'a University and University of Sciences and Technology. He has more than 6 years of experience in teaching. His research interests include root canal morphology, functionally graded concept, dental biomaterials, epidemiology and dental education, biomimetic restoration, finite element analysis and endodontic regeneration. Dr. Madfa has numerous international publications, full articles, two patents, a book and a book chapter. Furthermore, he won 14 international scientific awards. Furthermore, he is involved in many academic activities ranging from editorial board member, reviewer for many international journals and postgraduate students' supervisor. Besides, I deliver many courses and training workshops at various scientific events. Dr. Madfa also regularly attends international conferences and holds administrative positions (Deputy Dean of the Faculty for Students’ & Academic Affairs and Deputy Head of Research Unit).",institutionString:"Thamar University",institution:null},{id:"210472",title:"Dr.",name:"Nermin",middleName:"Mohammed Ahmed",surname:"Yussif",slug:"nermin-yussif",fullName:"Nermin Yussif",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/210472/images/system/210472.jpg",biography:"Dr. Nermin Mohammed Ahmed Yussif is working at the Faculty of dentistry, University for October university for modern sciences and arts (MSA). Her areas of expertise include: periodontology, dental laserology, oral implantology, periodontal plastic surgeries, oral mesotherapy, nutrition, dental pharmacology. She is an editor and reviewer in numerous international journals.",institutionString:"MSA University",institution:null},{id:"204606",title:"Dr.",name:"Serdar",middleName:null,surname:"Gözler",slug:"serdar-gozler",fullName:"Serdar Gözler",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/204606/images/system/204606.jpeg",biography:"Dr. Serdar Gözler has completed his undergraduate studies at the Marmara University Faculty of Dentistry in 1978, followed by an assistantship in the Prosthesis Department of Dicle University Faculty of Dentistry. Starting his PhD work on non-resilient overdentures with Assoc. Prof. Hüsnü Yavuzyılmaz, he continued his studies with Prof. Dr. Gürbüz Öztürk of Istanbul University Faculty of Dentistry Department of Prosthodontics, this time on Gnatology. He attended training programs on occlusion, neurology, neurophysiology, EMG, radiology and biostatistics. In 1982, he presented his PhD thesis \\Gerber and Lauritzen Occlusion Analysis Techniques: Diagnosis Values,\\ at Istanbul University School of Dentistry, Department of Prosthodontics. As he was also working with Prof. Senih Çalıkkocaoğlu on The Physiology of Chewing at the same time, Gözler has written a chapter in Çalıkkocaoğlu\\'s book \\Complete Prostheses\\ entitled \\The Place of Neuromuscular Mechanism in Prosthetic Dentistry.\\ The book was published five times since by the Istanbul University Publications. Having presented in various conferences about occlusion analysis until 1998, Dr. Gözler has also decided to use the T-Scan II occlusion analysis method. Having been personally trained by Dr. Robert Kerstein on this method, Dr. Gözler has been lecturing on the T-Scan Occlusion Analysis Method in conferences both in Turkey and abroad. Dr. Gözler has various articles and presentations on Digital Occlusion Analysis methods. He is now Head of the TMD Clinic at Prosthodontic Department of Faculty of Dentistry , Istanbul Aydın University , Turkey.",institutionString:"Istanbul Aydin University",institution:{name:"Istanbul Aydın University",country:{name:"Turkey"}}},{id:"240870",title:"Ph.D.",name:"Alaa Eddin Omar",middleName:null,surname:"Al Ostwani",slug:"alaa-eddin-omar-al-ostwani",fullName:"Alaa Eddin Omar Al Ostwani",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/240870/images/system/240870.jpeg",biography:"Dr. Al Ostwani Alaa Eddin Omar received his Master in dentistry from Damascus University in 2010, and his Ph.D. in Pediatric Dentistry from Damascus University in 2014. Dr. Al Ostwani is an assistant professor and faculty member at IUST University since 2014. \nDuring his academic experience, he has received several awards including the scientific research award from the Union of Arab Universities, the Syrian gold medal and the international gold medal for invention and creativity. Dr. Al Ostwani is a Member of the International Association of Dental Traumatology and the Syrian Society for Research and Preventive Dentistry since 2017. He is also a Member of the Reviewer Board of International Journal of Dental Medicine (IJDM), and the Indian Journal of Conservative and Endodontics since 2016.",institutionString:"International University for Science and Technology.",institution:{name:"Islamic University of Science and Technology",country:{name:"India"}}},{id:"42847",title:"Dr.",name:"Belma",middleName:null,surname:"Işik Aslan",slug:"belma-isik-aslan",fullName:"Belma Işik Aslan",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/42847/images/system/42847.jpg",biography:"Dr. Belma IşIk Aslan was born in 1976 in Ankara-TURKEY. After graduating from TED Ankara College in 1994, she attended to Gazi University, Faculty of Dentistry in Ankara. She completed her PhD in orthodontic education at Gazi University between 1999-2005. Dr. Işık Aslan stayed at the Providence Hospital Craniofacial Institude and Reconstructive Surgery in Michigan, USA for three months as an observer. She worked as a specialist doctor at Gazi University, Dentistry Faculty, Department of Orthodontics between 2005-2014. She was appointed as associate professor in January, 2014 and as professor in 2021. Dr. Işık Aslan still works as an instructor at the same faculty. She has published a total of 35 articles, 10 book chapters, 39 conference proceedings both internationally and nationally. Also she was the academic editor of the international book 'Current Advances in Orthodontics'. She is a member of the Turkish Orthodontic Society and Turkish Cleft Lip and Palate Society. She is married and has 2 children. Her knowledge of English is at an advanced level.",institutionString:"Gazi University Dentistry Faculty Department of Orthodontics",institution:null},{id:"178412",title:"Associate Prof.",name:"Guhan",middleName:null,surname:"Dergin",slug:"guhan-dergin",fullName:"Guhan Dergin",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/178412/images/6954_n.jpg",biography:"Assoc. Prof. Dr. Gühan Dergin was born in 1973 in Izmit. He graduated from Marmara University Faculty of Dentistry in 1999. He completed his specialty of OMFS surgery in Marmara University Faculty of Dentistry and obtained his PhD degree in 2006. In 2005, he was invited as a visiting doctor in the Oral and Maxillofacial Surgery Department of the University of North Carolina, USA, where he went on a scholarship. Dr. Dergin still continues his academic career as an associate professor in Marmara University Faculty of Dentistry. He has many articles in international and national scientific journals and chapters in books.",institutionString:null,institution:{name:"Marmara University",country:{name:"Turkey"}}},{id:"178414",title:"Prof.",name:"Yusuf",middleName:null,surname:"Emes",slug:"yusuf-emes",fullName:"Yusuf Emes",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/178414/images/6953_n.jpg",biography:"Born in Istanbul in 1974, Dr. Emes graduated from Istanbul University Faculty of Dentistry in 1997 and completed his PhD degree in Istanbul University faculty of Dentistry Department of Oral and Maxillofacial Surgery in 2005. He has papers published in international and national scientific journals, including research articles on implantology, oroantral fistulas, odontogenic cysts, and temporomandibular disorders. Dr. Emes is currently working as a full-time academic staff in Istanbul University faculty of Dentistry Department of Oral and Maxillofacial Surgery.",institutionString:null,institution:{name:"Istanbul University",country:{name:"Turkey"}}},{id:"192229",title:"Ph.D.",name:"Ana Luiza",middleName:null,surname:"De Carvalho Felippini",slug:"ana-luiza-de-carvalho-felippini",fullName:"Ana Luiza De Carvalho Felippini",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/192229/images/system/192229.jpg",biography:null,institutionString:"University of São Paulo",institution:{name:"University of Sao Paulo",country:{name:"Brazil"}}},{id:"256851",title:"Prof.",name:"Ayşe",middleName:null,surname:"Gülşen",slug:"ayse-gulsen",fullName:"Ayşe Gülşen",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/256851/images/9696_n.jpg",biography:"Dr. Ayşe Gülşen graduated in 1990 from Faculty of Dentistry, University of Ankara and did a postgraduate program at University of Gazi. \nShe worked as an observer and research assistant in Craniofacial Surgery Departments in New York, Providence Hospital in Michigan and Chang Gung Memorial Hospital in Taiwan. \nShe works as Craniofacial Orthodontist in Department of Aesthetic, Plastic and Reconstructive Surgery, Faculty of Medicine, University of Gazi, Ankara Turkey since 2004.",institutionString:"Univeristy of Gazi",institution:null},{id:"255366",title:"Prof.",name:"Tosun",middleName:null,surname:"Tosun",slug:"tosun-tosun",fullName:"Tosun Tosun",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/255366/images/7347_n.jpg",biography:"Graduated at the Faculty of Dentistry, University of Istanbul, Turkey in 1989;\nVisitor Assistant at the University of Padua, Italy and Branemark Osseointegration Center of Treviso, Italy between 1993-94;\nPhD thesis on oral implantology in University of Istanbul and was awarded the academic title “Dr.med.dent.”, 1997;\nHe was awarded the academic title “Doç.Dr.” (Associated Professor) in 2003;\nProficiency in Botulinum Toxin Applications, Reading-UK in 2009;\nMastership, RWTH Certificate in Laser Therapy in Dentistry, AALZ-Aachen University, Germany 2009-11;\nMaster of Science (MSc) in Laser Dentistry, University of Genoa, Italy 2013-14.\n\nDr.Tosun worked as Research Assistant in the Department of Oral Implantology, Faculty of Dentistry, University of Istanbul between 1990-2002. \nHe worked part-time as Consultant surgeon in Harvard Medical International Hospitals and John Hopkins Medicine, Istanbul between years 2007-09.\u2028He was contract Professor in the Department of Surgical and Diagnostic Sciences (DI.S.C.), Medical School, University of Genova, Italy between years 2011-16. \nSince 2015 he is visiting Professor at Medical School, University of Plovdiv, Bulgaria. \nCurrently he is Associated Prof.Dr. at the Dental School, Oral Surgery Dept., Istanbul Aydin University and since 2003 he works in his own private clinic in Istanbul, Turkey.\u2028\nDr.Tosun is reviewer in journal ‘Laser in Medical Sciences’, reviewer in journal ‘Folia Medica\\', a Fellow of the International Team for Implantology, Clinical Lecturer of DGZI German Association of Oral Implantology, Expert Lecturer of Laser&Health Academy, Country Representative of World Federation for Laser Dentistry, member of European Federation of Periodontology, member of Academy of Laser Dentistry. Dr.Tosun presents papers in international and national congresses and has scientific publications in international and national journals. He speaks english, spanish, italian and french.",institutionString:null,institution:{name:"Istanbul Aydın University",country:{name:"Turkey"}}},{id:"171887",title:"Prof.",name:"Zühre",middleName:null,surname:"Akarslan",slug:"zuhre-akarslan",fullName:"Zühre Akarslan",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/171887/images/system/171887.jpg",biography:"Zühre Akarslan was born in 1977 in Cyprus. She graduated from Gazi University Faculty of Dentistry, Ankara, Turkey in 2000. \r\nLater she received her Ph.D. degree from the Oral Diagnosis and Radiology Department; which was recently renamed as Oral and Dentomaxillofacial Radiology, from the same university. \r\nShe is working as a full-time Associate Professor and is a lecturer and an academic researcher. \r\nHer expertise areas are dental caries, cancer, dental fear and anxiety, gag reflex in dentistry, oral medicine, and dentomaxillofacial radiology.",institutionString:"Gazi University",institution:{name:"Gazi University",country:{name:"Turkey"}}},{id:"256417",title:"Associate Prof.",name:"Sanaz",middleName:null,surname:"Sadry",slug:"sanaz-sadry",fullName:"Sanaz Sadry",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/256417/images/8106_n.jpg",biography:null,institutionString:null,institution:null},{id:"272237",title:"Dr.",name:"Pinar",middleName:"Kiymet",surname:"Karataban",slug:"pinar-karataban",fullName:"Pinar Karataban",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/272237/images/8911_n.png",biography:"Assist.Prof.Dr.Pınar Kıymet Karataban, DDS PhD \n\nDr.Pınar Kıymet Karataban was born in Istanbul in 1975. After her graduation from Marmara University Faculty of Dentistry in 1998 she started her PhD in Paediatric Dentistry focused on children with special needs; mainly children with Cerebral Palsy. She finished her pHD thesis entitled \\'Investigation of occlusion via cast analysis and evaluation of dental caries prevalance, periodontal status and muscle dysfunctions in children with cerebral palsy” in 2008. She got her Assist. Proffessor degree in Istanbul Aydın University Paediatric Dentistry Department in 2015-2018. ın 2019 she started her new career in Bahcesehir University, Istanbul as Head of Department of Pediatric Dentistry. In 2020 she was accepted to BAU International University, Batumi as Professor of Pediatric Dentistry. She’s a lecturer in the same university meanwhile working part-time in private practice in Ege Dental Studio (https://www.egedisklinigi.com/) a multidisciplinary dental clinic in Istanbul. Her main interests are paleodontology, ancient and contemporary dentistry, oral microbiology, cerebral palsy and special care dentistry. She has national and international publications, scientific reports and is a member of IAPO (International Association for Paleodontology), IADH (International Association of Disability and Oral Health) and EAPD (European Association of Pediatric Dentistry).",institutionString:null,institution:null},{id:"202198",title:"Dr.",name:"Buket",middleName:null,surname:"Aybar",slug:"buket-aybar",fullName:"Buket Aybar",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/202198/images/6955_n.jpg",biography:"Buket Aybar, DDS, PhD, was born in 1971. She graduated from Istanbul University, Faculty of Dentistry, in 1992 and completed her PhD degree on Oral and Maxillofacial Surgery in Istanbul University in 1997.\nDr. Aybar is currently a full-time professor in Istanbul University, Faculty of Dentistry Department of Oral and Maxillofacial Surgery. She has teaching responsibilities in graduate and postgraduate programs. Her clinical practice includes mainly dentoalveolar surgery.\nHer topics of interest are biomaterials science and cell culture studies. She has many articles in international and national scientific journals and chapters in books; she also has participated in several scientific projects supported by Istanbul University Research fund.",institutionString:null,institution:null},{id:"260116",title:"Dr.",name:"Mehmet",middleName:null,surname:"Yaltirik",slug:"mehmet-yaltirik",fullName:"Mehmet Yaltirik",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/260116/images/7413_n.jpg",biography:"Birth Date 25.09.1965\r\nBirth Place Adana- Turkey\r\nSex Male\r\nMarrial Status Bachelor\r\nDriving License Acquired\r\nMother Tongue Turkish\r\n\r\nAddress:\r\nWork:University of Istanbul,Faculty of Dentistry, Department of Oral Surgery and Oral Medicine 34093 Capa,Istanbul- TURKIYE",institutionString:null,institution:null},{id:"172009",title:"Dr.",name:"Fatma Deniz",middleName:null,surname:"Uzuner",slug:"fatma-deniz-uzuner",fullName:"Fatma Deniz Uzuner",position:null,profilePictureURL:"https://mts.intechopen.com/storage/users/172009/images/7122_n.jpg",biography:"Dr. Deniz Uzuner was born in 1969 in Kocaeli-TURKEY. After graduating from TED Ankara College in 1986, she attended the Hacettepe University, Faculty of Dentistry in Ankara. \nIn 1993 she attended the Gazi University, Faculty of Dentistry, Department of Orthodontics for her PhD education. After finishing the PhD education, she worked as orthodontist in Ankara Dental Hospital under the Turkish Government, Ministry of Health and in a special Orthodontic Clinic till 2011. Between 2011 and 2016, Dr. Deniz Uzuner worked as a specialist in the Department of Orthodontics, Faculty of Dentistry, Gazi University in Ankara/Turkey. In 2016, she was appointed associate professor. Dr. Deniz Uzuner has authored 23 Journal Papers, 3 Book Chapters and has had 39 oral/poster presentations. She is a member of the Turkish Orthodontic Society. Her knowledge of English is at an advanced level.",institutionString:null,institution:null},{id:"332914",title:"Dr.",name:"Muhammad Saad",middleName:null,surname:"Shaikh",slug:"muhammad-saad-shaikh",fullName:"Muhammad Saad Shaikh",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",biography:null,institutionString:null,institution:{name:"Jinnah Sindh Medical University",country:{name:"Pakistan"}}},{id:"315775",title:"Dr.",name:"Feng",middleName:null,surname:"Luo",slug:"feng-luo",fullName:"Feng Luo",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",biography:null,institutionString:null,institution:{name:"Sichuan University",country:{name:"China"}}},{id:"423519",title:"Dr.",name:"Sizakele",middleName:null,surname:"Ngwenya",slug:"sizakele-ngwenya",fullName:"Sizakele Ngwenya",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",biography:null,institutionString:null,institution:{name:"University of the Witwatersrand",country:{name:"South Africa"}}},{id:"419270",title:"Dr.",name:"Ann",middleName:null,surname:"Chianchitlert",slug:"ann-chianchitlert",fullName:"Ann Chianchitlert",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",biography:null,institutionString:null,institution:{name:"Walailak University",country:{name:"Thailand"}}},{id:"419271",title:"Dr.",name:"Diane",middleName:null,surname:"Selvido",slug:"diane-selvido",fullName:"Diane Selvido",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",biography:null,institutionString:null,institution:{name:"Walailak University",country:{name:"Thailand"}}},{id:"419272",title:"Dr.",name:"Irin",middleName:null,surname:"Sirisoontorn",slug:"irin-sirisoontorn",fullName:"Irin Sirisoontorn",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",biography:null,institutionString:null,institution:{name:"Walailak University",country:{name:"Thailand"}}},{id:"355660",title:"Dr.",name:"Anitha",middleName:null,surname:"Mani",slug:"anitha-mani",fullName:"Anitha Mani",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",biography:null,institutionString:null,institution:{name:"SRM Dental College",country:{name:"India"}}},{id:"355612",title:"Dr.",name:"Janani",middleName:null,surname:"Karthikeyan",slug:"janani-karthikeyan",fullName:"Janani Karthikeyan",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",biography:null,institutionString:null,institution:{name:"SRM Dental College",country:{name:"India"}}},{id:"334400",title:"Dr.",name:"Suvetha",middleName:null,surname:"Siva",slug:"suvetha-siva",fullName:"Suvetha Siva",position:null,profilePictureURL:"//cdnintech.com/web/frontend/www/assets/author.svg",biography:null,institutionString:null,institution:{name:"SRM Dental College",country:{name:"India"}}}]}},subseries:{item:{id:"4",type:"subseries",title:"Fungal Infectious Diseases",keywords:"Emerging Fungal Pathogens, Invasive Infections, Epidemiology, Cell Membrane, Fungal Virulence, Diagnosis, Treatment",scope:"Fungi are ubiquitous and there are almost no non-pathogenic fungi. Fungal infectious illness prevalence and prognosis are determined by the exposure between fungi and host, host immunological state, fungal virulence, and early and accurate diagnosis and treatment. \r\nPatients with both congenital and acquired immunodeficiency are more likely to be infected with opportunistic mycosis. Fungal infectious disease outbreaks are common during the post- disaster rebuilding era, which is characterised by high population density, migration, and poor health and medical conditions.\r\nSystemic or local fungal infection is mainly associated with the fungi directly inhaled or inoculated in the environment during the disaster. The most common fungal infection pathways are human to human (anthropophilic), animal to human (zoophilic), and environment to human (soilophile). Diseases are common as a result of widespread exposure to pathogenic fungus dispersed into the environment. \r\nFungi that are both common and emerging are intertwined. In Southeast Asia, for example, Talaromyces marneffei is an important pathogenic thermally dimorphic fungus that causes systemic mycosis. Widespread fungal infections with complicated and variable clinical manifestations, such as Candida auris infection resistant to several antifungal medicines, Covid-19 associated with Trichoderma, and terbinafine resistant dermatophytosis in India, are among the most serious disorders. \r\nInappropriate local or systemic use of glucocorticoids, as well as their immunosuppressive effects, may lead to changes in fungal infection spectrum and clinical characteristics. Hematogenous candidiasis is a worrisome issue that affects people all over the world, particularly ICU patients. CARD9 deficiency and fungal infection have been major issues in recent years. Invasive aspergillosis is associated with a significant death rate. Special attention should be given to endemic fungal infections, identification of important clinical fungal infections advanced in yeasts, filamentous fungal infections, skin mycobiome and fungal genomes, and immunity to fungal infections.\r\nIn addition, endemic fungal diseases or uncommon fungal infections caused by Mucor irregularis, dermatophytosis, Malassezia, cryptococcosis, chromoblastomycosis, coccidiosis, blastomycosis, histoplasmosis, sporotrichosis, and other fungi, should be monitored. \r\nThis topic includes the research progress on the etiology and pathogenesis of fungal infections, new methods of isolation and identification, rapid detection, drug sensitivity testing, new antifungal drugs, schemes and case series reports. It will provide significant opportunities and support for scientists, clinical doctors, mycologists, antifungal drug researchers, public health practitioners, and epidemiologists from all over the world to share new research, ideas and solutions to promote the development and progress of medical mycology.",coverUrl:"https://cdn.intechopen.com/series_topics/covers/4.jpg",hasOnlineFirst:!0,hasPublishedBooks:!1,annualVolume:11400,editor:{id:"174134",title:"Dr.",name:"Yuping",middleName:null,surname:"Ran",slug:"yuping-ran",fullName:"Yuping Ran",profilePictureURL:"https://s3.us-east-1.amazonaws.com/intech-files/0030O00002bS9d6QAC/Profile_Picture_1630330675373",biography:"Dr. Yuping Ran, Professor, Department of Dermatology, West China Hospital, Sichuan University, Chengdu, China. Completed the Course Medical Mycology, the Centraalbureau voor Schimmelcultures (CBS), Fungal Biodiversity Centre, Netherlands (2006). International Union of Microbiological Societies (IUMS) Fellow, and International Emerging Infectious Diseases (IEID) Fellow, Centers for Diseases Control and Prevention (CDC), Atlanta, USA. Diploma of Dermatological Scientist, Japanese Society for Investigative Dermatology. Ph.D. of Juntendo University, Japan. Bachelor’s and Master’s degree, Medicine, West China University of Medical Sciences. Chair of Sichuan Medical Association Dermatology Committee. General Secretary of The 19th Annual Meeting of Chinese Society of Dermatology and the Asia Pacific Society for Medical Mycology (2013). In charge of the Annual Medical Mycology Course over 20-years authorized by National Continue Medical Education Committee of China. Member of the board of directors of the Asia-Pacific Society for Medical Mycology (APSMM). Associate editor of Mycopathologia. Vice-chief of the editorial board of Chinses Journal of Mycology, China. Board Member and Chair of Mycology Group of Chinese Society of Dermatology.",institutionString:null,institution:{name:"Sichuan University",institutionURL:null,country:{name:"China"}}},editorTwo:null,editorThree:null,series:{id:"6",title:"Infectious Diseases",doi:"10.5772/intechopen.71852",issn:"2631-6188"},editorialBoard:[{id:"302145",title:"Dr.",name:"Felix",middleName:null,surname:"Bongomin",slug:"felix-bongomin",fullName:"Felix Bongomin",profilePictureURL:"https://mts.intechopen.com/storage/users/302145/images/system/302145.jpg",institutionString:null,institution:{name:"Gulu University",institutionURL:null,country:{name:"Uganda"}}},{id:"45803",title:"Ph.D.",name:"Payam",middleName:null,surname:"Behzadi",slug:"payam-behzadi",fullName:"Payam Behzadi",profilePictureURL:"https://mts.intechopen.com/storage/users/45803/images/system/45803.jpg",institutionString:"Islamic Azad University, Tehran",institution:{name:"Islamic Azad University, Tehran",institutionURL:null,country:{name:"Iran"}}}]},onlineFirstChapters:{},publishedBooks:{},testimonialsList:[{id:"27",text:"The opportunity to work with a prestigious publisher allows for the possibility to collaborate with more research groups interested in animal nutrition, leading to the development of new feeding strategies and food valuation while being more sustainable with the environment, allowing more readers to learn about the subject.",author:{id:"175967",name:"Manuel",surname:"Gonzalez Ronquillo",institutionString:null,profilePictureURL:"https://mts.intechopen.com/storage/users/175967/images/system/175967.png",slug:"manuel-gonzalez-ronquillo",institution:{id:"6221",name:"Universidad Autónoma del Estado de México",country:{id:null,name:"Mexico"}}}},{id:"8",text:"I work with IntechOpen for a number of reasons: their professionalism, their mission in support of Open Access publishing, and the quality of their peer-reviewed publications, but also because they believe in equality.",author:{id:"202192",name:"Catrin",surname:"Rutland",institutionString:null,profilePictureURL:"https://mts.intechopen.com/storage/users/202192/images/system/202192.png",slug:"catrin-rutland",institution:{id:"134",name:"University of Nottingham",country:{id:null,name:"United Kingdom"}}}},{id:"18",text:"It was great publishing with IntechOpen, the process was straightforward and I had support all along.",author:{id:"71579",name:"Berend",surname:"Olivier",institutionString:"Utrecht University",profilePictureURL:"https://mts.intechopen.com/storage/users/71579/images/system/71579.png",slug:"berend-olivier",institution:{id:"253",name:"Utrecht University",country:{id:null,name:"Netherlands"}}}}]},submityourwork:{pteSeriesList:[],lsSeriesList:[],hsSeriesList:[],sshSeriesList:[],subseriesList:[],annualVolumeBook:{},thematicCollection:[],selectedSeries:null,selectedSubseries:null},seriesLanding:{item:null},libraryRecommendation:{success:null,errors:{},institutions:[]},route:{name:"profile.detail",path:"/profiles/237896",hash:"",query:{},params:{id:"237896"},fullPath:"/profiles/237896",meta:{},from:{name:null,path:"/",hash:"",query:{},params:{},fullPath:"/",meta:{}}}},function(){var e;(e=document.currentScript||document.scripts[document.scripts.length-1]).parentNode.removeChild(e)}()