Visible light active non-metal doped photocatalysts.
Semiconductor photocatalysis gained reputation in the early 1970s when Fujishima and Honda revealed the potential of TiO2 to split water in to hydrogen and oxygen in a photoelectrochemical cell. Their work provided the base for the development of semiconductor photocatalysis for the environmental remediation and energy applications. Photoactivity of some semiconductors was found to be low due to larger band gap energy and higher electron-hole pair recombination rate. To avoid these problems, the development of visible light responsive photocatalytic materials by different approaches, such as metal and/or non-metal doping, co-doping, coupling of semiconductors, composites and heterojunctions materials synthesis has been widely investigated and explored in systematic manner. This chapter emphasizes on the different type of tailored photocatalyst materials having the enhanced visible light absorption properties, lower band gap energy and recombination rate of electron-hole pairs and production of reactive radical species. Visible light active semiconductors for the environmental remediation purposes, particularly for water treatment and disinfection are also discussed in detail. Studies on the photocatalytic degradation of emerging organic compounds like cyanotoxins, VOCs, phenols, pharmaceuticals, etc., by employing variety of modified semiconductors, are summarized, and a mechanistic aspects of the photocatalysis has been discussed.
- visible light photocatalysis
- semiconductor composites
- organic pollutants
- wastewater treatment
1. Introduction to photocatalysis
Catalysis refers to a phenomenon in which a substance (the catalyst) speed up a kinetically slow reaction and the catalyst is fully restored at the end of each catalytic cycle and the “Photocatalysis” is defined as a specific process for the acceleration of the “photoreaction” in the presence of a catalyst . Photocatalysis can also be regarded as the catalysis of photochemical reaction on a solid substrate, mostly a semiconductor . The term “Photocatalysis” is still an arguable subject due to controversies, according to some researchers the “light” acts as a catalyst, while it always acts as a “reactant” where it is spent in the chemical process .
The word “photoreaction” is sometimes explained as a “Photoinduced” or “Photoactivated,” process, whereas in the field of photocatalysis, “catalytic activity” is the ability of a catalyst to show performance under light depending upon the reaction sites/active sites at the catalyst. The performance of a catalyst can be determined by its “turnover frequency” which is “number of turnovers per unit time of reaction, it is used to show how many times one active site produces a reaction product(s) within unit time.” In case of photocatalysis, the reaction rate depends on the frequency of irradiated light which acts as the initiator of photoreaction. The term photocatalysis indicates the relation of light and some substance; (say a catalyst) so in the absence of light, the process of photocatalytic activities on active sites is not possible [1, 4].
1.1 Brief history of semiconductor photocatalysis
In 1839, the production of voltage and an electric current were reported when silver chloride electrode, immersed in electrolyte solution (connected to counter electrode) exhibited illumination under sunlight, which lately was known as “Becquerel effect” led to the beginning of existing era of photo electrochemistry . In 1921, the Renz published first article on the degradation of carbon compounds by using titanium dioxide. In 1924 the photocatalytic deposition of silver on zinc oxide was observed for the production of metallic silver . In 1929, the “chalking” (fading of paints) effect of titanium white (TiO2), under the strong sunlight was observed, which in 1938 became the basis for self-cleaning property and modification in the concept of photo-induced reduction .
During 1950s, the insights of photocatalysis were shifted to ZnO. In 1953, two studies for the production of H2O2 on ZnO under the UV irradiation started a series of follow-up studies in the upcoming years which explained that an organic compound is oxidized when atmospheric oxygen is reduced. Till 1955, the photocatalytic behaviour of ZnO, Sb2O3 and TiO2 including photoconductivity and fluorescence were well known. In 1958, the adsorption of reduced O2 on the TiO2 surface, as a result of photoexcitation, having the ability to degrade a dye was studied. During 1960s and 1970s, the processes and concepts of photo-oxidation of CN− and photo-deposition of Pt, Cu, Pd, and other metals on TiO2, WO3, Al2O3, and SnO2 to be used as co-catalysts, had been evolved. In 1972 the field of photo-electrochemical got more attention when Fujishima and Honda reported the ability of an illuminated TiO2 and Pt electrode to generate the H2 gas by a publication in
1.2 Semiconductor photocatalysis
The phenomenon gained importance during late 1970s and mid 1980s after the evolution of H2 by illuminated TiO2 (pristine semiconductor) in the presence of noble metal electrode, after that great concern was shown in water splitting followed by emergence of new era of photo electrochemistry at a single semiconductor crystal. The processes of semiconductor photocatalysis for environmental concerns have gained fame during the last 3 decades [8, 9].
Semiconductor photocatalysis can be of two types (i) homogenous photocatalysis, (ii) heterogeneous photocatalysis, depending on the phase differences of reactants and catalysts, triggered the concept of advanced oxidation processes (AOPs) at the end of twentieth century. TiO2 is the semiconductor which can act as both the hetero and homogenous photocatalyst photoreactions  (Figure 1).
Heterogeneous photocatalysis is a process which includes a large variety of reactions: reductions oxidations, dehydrogenation, transfer of charge carriers, bacterial inactivation, organic pollutant degradation, water detoxification, etc. under both UV and visible light irradiation [1, 11]. Having TiO2 as a semiconductor, the general mechanism is illustrated in Figure 2.
The chemistry behind the process is explained as :
In Figure 2, process “2” is “recombination.” When it occurs, the excited electron return to valence band and recombines with hole (by dispersing the absorbed energy as heat) in the absence of electron acceptor in the conduction band. Recombination of photoexcited electron is the major drawback of semiconductors as it lessens the efficiency of overall process. The chances of recombination can be reduced by modifications in the crystalline structure either by doping with metals, non-metals, ions or by the formation of heterostructures .
1.4 Basics of heterojunctions
In the internal structure of semiconductors (SCs), there are some band alignments which act as basis for the formation of heterojunctions/heterostructures; prepared for the enhanced activity of SCs’ under sunlight. “Heterojunction is the junction in single crystal, formed by the combination of two dissimilar SCs.” These heterostructures are formed on the basis of band gap, electron affinity and bands position thus leading to the formation of new energy levels. By the formation of HSs/HJs, the movement of charge carriers in a reaction can be controlled. There are three types of heterostructures depending on the energy band alignments. (i) Type I band alignment; the “Straddling” band Pattern. (ii) Type II band alignment; the “Staggered” band Pattern; (iii) Type III band alignment; the “Broken gap” Pattern. Agrawal 
The formation of Type II heterojunctions are good candidates in the field of photocatalysis as it has capability to enhance the charge separation to improve the photoreactions, photocatalytic degradation and water splitting .
1.5 General mechanism of water splitting by semiconductors for wastewater treatment
Globally, 1 billion people do not have access to safe drinking water and approximately 2.6 billion people are suffering from safe sanitation, this is particularly an issue in Asia, Africa, South and central America , so there is no ambiguity in saying that water management has become an emerging issue for the twenty-first century. Number of anthropogenic activities like industrial activities, discharge of effluents in the water bodies, oil spills and leaching of compounds to groundwater, etc. are interfering the quality of water, thus making it unfit for drinking and domestic purposes and also threatening the natural water resources. It has been estimated that the water quality will be a worst in upcoming decades. In this regard, there is a need for advancement in the fields of water and wastewater treatment because the conventional treatment plants are not capable to remove some persistent pollutants from water .
In this perspective the concept of photocatalytic water splitting has been emerged in last decade which are a favorable method for attaining green and renewable energy. For effective water splitting the CB of a SC should be more negative than the redox potential of H+/H2 (0 V vs. NHE) and the top of the valence band should be more positive than the redox potential of O2/H2O (1.23 V vs. NHE). In splitting process water breaks in oxygen and hydrogen by the photoexcitation of electron leaving a hole behind. Semiconductor absorbs the energy equal to or greater than its band gap, the photogenerated electrons and holes starts the redox reactions. Three key stages of water splitting mechanism are; (i) energy absorbance and generation of e−/h+ as result of photoexcitation; (ii) the charges remain separated at the opposite sides of SC crystal as a result of minimal recombination; (iii) charge carriers trigger the oxidation and reduction at valance and conduction band or vice versa. By production of reactive species as result of reduction of oxygen and oxidation of water or hydroxyl ion, like H+, OH• and O2•− the wide variety of organic pollutants in water are mineralized in to CO2 and H2O . The water splitting mechanism is given in Figure 4.
1.6 Roles of reactive species in pollutant degradation
General reactive or oxidizing species formed during the photocatalytic degradation of pollutants are H+, OH, HO2, H2O2 and O2•−. These photo-oxidants are formed by the steps as described in Eqs. (2)–(7).
Hole and hydroxyl radical: A hole generates when an electron moves to CB as a result of photo excitation, and hydroxyl radical generates when the hole oxidizes the hydroxyl ion or the water molecule. There is a debate on the reactiveness of hole and a hydroxyl radical, as they both are important for photocatalytic degradation, because it is still uncertain whether the hole or hydroxyl radical is core oxidant, or is there any dependence on the type of substrate. Minero et al.  has investigated that OH• has higher oxidizing power as compared to other oxidizing agents as it has the oxidation potential of +2.80 eV slightly less than that of Fluorine +2.87 eV. There are many studies which support the reactivity of OH• as an oxidant . Turchi and Ollis  have proposed the four ways by which the OH• oxidizes the pollutant, Figure 5.
Draper et al.  has investigated the direct oxidation by the hole, it can be said that the oxidation process in the valence band is started by the hole, by the oxidation of H2O molecule and hydroxyl ion. It would be rational to say that both the hole and OH• deal with different classes of compounds; like the production of hydroxylated rings from the oxidation of aromatic compounds and the degradation of paracetamol (acetaminophen) on the TiO2 is caused by OH• .
Superoxide radical: This specie has been reported to play an important for the degradation/oxidation of many pollutants under both, the visible and ultra violet light irradiations. In addition to direct participation in oxidation the formation of superoxides confirms the decreased recombination rate, as it is formed by the reduction of oxygen molecule. Therefore, superoxide formation is a vital process which controls the reaction rate by accepting the excited electron ().
Hydrogen peroxide: Hydrogen peroxide is formed in the solution by the combination of two hydroperoxyl radicals (HOO·) or by the two electron reduction of O2 in the conduction band as shown in Eqs. (6), (7) and (10). It can affect the photocatalytic reaction by acting as electron acceptor directly from organic or inorganic pollutant or by its dissociation into OH• due to “homolytic scission” . Reactivity depends on rate of its production and the substrate concentration on the semiconductor. H2O2 mostly in the TiO2 solutions cannot be readily detected due to its high unstable nature. H2O2 is dissipated as it is produced into OH• by reduction .
Photoproduced reactive species on the photocatalysts undergo oxidation that have been extensively studied during the last decades for environmental remediation including water disinfection, wastewater treatment, air decontamination, self-cleaning glass/surfaces degradation of organic compounds, etc. The reason to attraction towards this process lies in the end products of any type of pollutant which are CO2 and H2O. Actually, the mineralisation of compounds having high carbon hydrogen content, occurs via the formation of many intermediates which also undergo oxidation. In short, the significance of photocatalytic process and photo-oxidation cannot be underestimated because of its emerging demand for the decomposition of refractory organics or recalcitrant compounds.
2. Development of visible light active photocatalysts
Among the several advanced oxidation processes, semiconductor assisted photoreactions are gaining importance in recent years due to their higher mineralization potential of organic pollutants in environment. The main limitation for the pure SC photocatalysts is their large band gap which means there is a need for shorter wavelength of light and high energy photons (λ < 380 nm) to excite the electron from VB to CB. For this purpose, the photons falling in ultra violet region are required. Under the UV irradiation, the electrons in the VB of SCs are excited and e−/h+ pair is formed. The problem is, the UV light makes only 4–5% of the solar spectrum while about 40–45% of the solar light falls in visible spectra. The need of UV light limits the photocatalytic activity due to its less availability [12, 20].
In recent years, Yongquan Quab  has pointed some critical requirements for a stable SC catalyst to yield the solar energy which are; firstly, the SC must have an appropriate band gap to produce robust electrons (Eg > 1.3 eV commonly >2 eV but <3 eV) and sufficient band gap to allow effective absorption of light under visible region. Secondly, there should be less chances for recombination, i.e., should have an efficient charge separation system; lastly there should be a process to protect the semiconductors from the direct electrochemical reactions to confirm the photoelectrochemical strength of the system.
A single pure semiconductor photocatalyst is unable to fulfill the all above mentioned requirements. Therefore, in order to enhance the photocatalytic activity of the SC, there is a need to enhance their visible light activity, which can either be done by enhancing the surface modifications, i.e., by increasing the surface area and porosity, or by chemicals modifications like doping of metals, non-metals, ions, non-metal co-doping, dye sensitization or by the formation of junctions unitary, binary and tertiary, i.e., semiconductor/semiconductor, semiconductor/metal, semiconductor/metal oxides or the semiconductors/nano-composites .
2.1 Doping/grafting of semiconductor photocatalysts
Among all semiconductors TiO2 is considered as pristine, first-generation oldest one with many physical and structural properties. In addition to TiO2 other
In order to understand, doping can be defined as “when impurities are added to semiconconductors, the band structure is modified; this process is known as doping.” During the doping process, the doped atoms can present the interstitial, substitution or defect factor in structure of SC. When a semiconductor is doped with an acceptor atom, it is converted into
2.2 Non-metal-doped semiconductors
For this type of doping to SCs the non-metals like N, C, S and F have been used. The production of visible light active photocatalysts starts with the doping of N to TiO2 or ZnO lattice, due to its small size, low ionization energy, and high stability. Livraghi et al.  proposed that contrary to the concept that nitrogen species are reason for formation of VLA photocatalyst the nitrogen precursor during the doping process induces the oxygen vacancies which renders the SCs able to absorb visible light and to increase phocatalytic activity. In 1986, Sato discovered the addition of NH4OH in the titania sol followed by the calcination of obtained product, the resulting products was visible light active . After that Asahi et al.  first time explored the VL activity of N-doped TiO2 by the sputter method of TiO2 under N-Ar atmosphere. They also proposed that nitrogen doping creates a delocalized mixing/hybridization of O 2p and N 2p orbitals causing the rise in valence band position. Later on, for the efficient doping of N to TiO2 either in bulk or at surface both types the dry or wet methods have been adopted. Techniques, like sputtering [31, 32] and ion implementation are based on the direct treatment of TiO2 with nitrogen ions [32, 33].
The most used method of N doping in TiO2 is sol-gel method, in this method the titanium precursors are combined with the nitrogen containing surfactants, for example, the N-doped TiO2 have been prepared by using dodecylammonium chloride (DDCA) as surfactant acting as nitrogen source which provided it damaging capability for microcystins-LR under visible irradiation  Figure 7. Degradation of MC-LR and mineralization of 78% of carbon has also been reported by using Bi-doped TiO2 under visible light irradiation having OH• as a reactive oxidation specie .
Several processes have been proposed to prepare the nanobelts by doping the 1D titania nanostructure with nitrogen following hydrothermal method having the anatase TiO2 particles and NaOH as precursors and heating treatment with NH3 (). Production of N-doped TiO2 nanotubes by the anodization of Ti in HF/H2SO4 electrolyte have been reported .
In addition to the N-doped TiO2, ZnO can also be doped which is one of the most studied SC other than TiO2 due to its applications in disinfection process and diversity of shapes but it has low stability. ZnO has also three crystalline forms, named as Zinc blend, Rocksalt and Wurtzite, having third one as most stable and active. The example of N-doped ZnO is preparation of zinc nanobundles by thermal treatment of (already prepared) ZnOHF nanobundles with NH3 at different temperatures, as the temperature was increased the ZnOHF nanobundles were converted to N-ZnO nanobundles (Figure 8). These N-ZnO nanobundles gave dramatic increase absorption of light in visible region at λ > 420 nm .
Formation of the N-doped ZnO mesoporous nanospheres is an example of use of solvothermal treatment of Zn (NO3)2.6H2O which is the source of both Zn and nitrogen, in the presence of oleic acid, oleylamine, and octadecene. Mixture was heated at 260°C for 20 min and cooled at room temperature for 2 h followed by centrifugation, washing of precipitate and calcination at 400°C for 2 h led to the production of mesoporous nanospheres having size between 100–300 nm. This structure had the higher photoactivity as compared to pristine ZnO (). The nitrogen doped silver deposited ZnO thin films have been successfully prepared on a glass substrate by Kumar et al. via Radio frequency (RF) magnetron sputtering for the degradation of 2-CP under the visible light irradiation λ 390–700 nm and resulted in production of mineralized products as in Figures 9 and 10 .
Nitrogen doped ZnO films were prepared by chemical vapour deposition (CVD) process using metallic zinc, NO2 and NH3 as precursors. The nitrogen concentration was varied while the temperature was kept constant at 350°C. The gradual addition of dopant to ZnO films led to the formation of stable nitrogen vacancies clusters and n-type defects, the stability of vacancies is the beauty of this process because the vacancies formed by addition of other impurities are easily removable . Other techniques for the production of N-ZnO films on glass substrate, like high vacuum plasma-assisted chemical vapour deposition (HVP-CVD)  and pulsed-filtered cathodic vacuum arc deposition (PFCVAD)  have been reported. In both techniques, N2 or N2O was used as doping agents and as the dopant quantity was increased the semiconductor changed from
In literature, in addition to the doping of TiO2 with nitrogen, there are studies which have reported the carbon doped TiO2 as visible light photocatalyst. In contrast to the nitrogen doped TiO2 which is commonly present in substitutional form, the carbon is doped to TiO2 in different ways depending on the doping process, the three possible ways for carbon addition to lattice are (i) replacement of lattice oxygen with carbon; (ii) replacement of Ti atom with carbon atom; (iii) addition of carbon at interstitial position. Due to relatively smaller size of C atom, third one can occur without creating too much strain in structure . The green synthesis for the C-doped TiO2 has been described by using Ti (SO4)2 and sucrose as the precursors for Ti and carbon. This hydrothermal method is adoptable due to its low cost, nontoxic and easiness to perform, the C-TiO2 was prepared by hydrothermal method and post-thermal treatment was applied at different temperatures and this was found to be effective to promote the visible light activity of C-TiO2 for the degradation of toluene . C-doped TiO2 material have been prepared by the oxidation of titanium carbide (TiC) coated multiwalled carbon nanotubes (MWCNTs). The MWCNTs were used as a reaction template and carbon source, and titanium powder as the titanium source. XPS results indicated that chemical structure of Ti in TiO2 coated-MWCNTs was different from that of pristine anatase due to the formation of Ti-O-C strong bond and interaction between TiO2-MWCNT (Figure 11). The photocatalytic activity of this material was tested for the degradation of methylene blue under visible light .
Carbon doped TiO2 has been reported to improve its VL response and photocatalytic activity and has been shown to be more effective than nitrogen doping. C-doped TiO2 nanomaterials were prepared by the oxidative annealing of titanium (IV) carbide, used as a precursor. XPS analysis revealed that the carbon in the sample was present as carbonate species. The nanopowders were used for the degradation of methylene blue in the aqueous solution and for anti-bactericidal activity of
Sulfur can also be used as a promising dopant to enhance the visible light activity despite of its difficulty to doping due to its large ionic radius. Sulfur-doped TiO2 was prepared by using thiourea and titanium (IV) isopropoxide as precursors followed by mixing and vigorous stirring in ethanol resulted in the production of white powder annealed at 450°C for 4 h, the resulting material was S-doped TiO2. These powders gave degradation of quinoline at λ = 495 nm . S-doped material can be produced by the oxidation heating of TiS2 powder followed by the annealing at 300°C, the XRD and XPS patterns gave the results which confirmed that the S atoms doped into the substitutional site of TiO2 (e.g., the substitution of S for O) are effective for the band gap narrowing. Moreover, band calculations showed that the band gap narrowing due to the S doping originates from mixing the S 3p states with VB, leading to an increase in the VB width .
Incorporation of S to ZnO is little difficult due to its low solubility in ZnO and separation of ZnS particles at high temperatures. To overcome this problem, homogenously mixed precursors should be treated at low temperature. Formation of sulfur-doped ZnO films have been reported by pulse laser deposition , reactive sputtering () and chemical spray pyrolysis . S-ZnO films are more appropriate for the uses in electronics, sensors and photoelectrochemical cells. But for the photocatalytic processes, S-ZnO powders give better results than films. Patil et al.  has proposed a method to make S-ZnO by a novel two steps process. First was the formation of bis-thiourea zinc oxalate (BTZO) powders by a mechanochemical method followed by its thermal decomposition/annealing at different temperatures to produce S-ZnO. At lower temperatures the resulting product was ZnS but as the temperature rose to 600°C the product was S-ZnO. The prepared powder was used to degrade the resorcinol under visible light and complete photocatalytic degradation (PCD) of 150 ppm resorcinol was observed in 7 h of light exposure at pH 7 . ZnO has also been reported to be doped with iodine by following a solvothermal method using zinc salts and iodic acids in polyol medium as precursors with heating at 160°C. XRD and EDX analysis proved the presence of I in ZnO lattice. I doping increased the visible light absorbance, i.e., λ > 510 nm. In addition to the change in absorption spectra, it was proposed that doped I could act as the electron trapping sites thus reducing the chances for recombination .
To enhance the absorption in visible spectrum, P doping to TiO2 has been reported using titanium isopropoxide and phosphide and H3PO4 as precursors. The content of P-TiO2 had different properties prepared from two different precursors (Phosphide and H3PO4). A clear red shift in the absorption was observed due to the substitutional position of P3− for oxygen in lattice. The presence of P3− was confirmed by XPS analysis, the ion-doped product gave 4-CP and acetaldehyde degradation under pure visible light at λ 410–440 nm .
Graphitic carbon nitride (g-C3N4) is a polymeric semiconductor, in order to increase its visible light activity and to reduce band gap it is doping with phosphorous has been reported. Ligang et al. prepared P-doped g-C3N4 by one pot green synthesis approach using dicyandiamide and phosphorous containing ionic liquid as precursors. The prepared particles were characterized and analysed and were used for the degradation of organic dyes like Rhodamine B and Methyle Orange under visible light. The photoactivity of particles was dependent on the post annealing temperature, doped particles gave higher photocatalytic activity as compared to pure g-C3N4, and degraded 95% of pollutants for the irradiation time of 180 min . Chai et al. has also reported the degradation of dye by using P-doped gCN under visible light, synthesized by co-pyrolsis method, analysis like XRD, SEM, FESEM, XPS and FTIR were performed to check crystalline, morphological, structural and optical properties of catalyst. Prepared catalyst gave greater photocatalytic activity by substituting P atoms with C resulted in enhanced light harvesting phenomenon as it degraded 95% of dye in 30 min, additionally radical scavenging test unveiled that holes and superoxide radicals were dominant reactive species . Sulfur-doped gCN porous rods were prepared in one pot by a simple pyrolysis method of melamine-trithiocyanuric acid at different temperatures, analysis confirmed the formation of porous rods with high surface area than that of pure gCN, surface area increased with increasing temperature, as prepared catalyst gave higher photocatalytic activity and increased absorption of light in visible region and gave 92% of rhB degradation within 50 min . g-C3N4 has also been reported to be doped with boron  and carbon atoms , to enhance the photocatalytic activity under visible light.
Some other non-metals like fluorine, bromine, and oxygen have also been reported to dope SCs to enhance the photocatalytic property. Doping of different type of dopant into the lattice structure of some other semiconductors like Ta2O5, Nb2O5, BiVO4, InVO4, Bi2WO6, La2Ti2O7, H2Ti4O9, NaTaO3, Nb2O5,V2O5, Sb2O3, Bi2O3, Fe2O3, NiO, ZrO2, CeO2, Ga2O3, CuO, Cu2O, HNb3O8, WO3, ZnO, K2La2Ti3O10, K2Ti4O9, BiMoO6 and TiO2 have been reported. Some doped SCs with their water treating abilities is given in Table 1. Among the above mentioned semiconductors some have the large band gaps and show excitation under the UV irradiation only, like ZrO2 has the band gap of 5 eV and Ga2O3 have band gap of 4.8 eV needs the excitation energy of 248–265 nm, while some SCs like WO3 and venedates have small band gaps but they are doped in order to enhance the quantum efficiency of the process. However, dependant on their synthetic approaches and crystalline structures some metal oxides have shown the degradation activity of organic and inorganic compounds under visible light .
|Pristine photocatalyst||Non-metal dopant||Doping process||Target pollutant for visible light induced degradation||References|
|TiO2||Nitrogen||Colloidal solution hydrolysis||Methylene blue|||
|DC sputtering and oxidation||Rhodamine B|||
|Sol-gel, hydrothermal and pyrolysis||Microcystin-LR|||
|Thermal decomposition, one-step synthesis||MO degradation|||
|Boron (F-B-S tri-doped)||Solvation/evaporation/sol-gel synthesis||Acid napthol red (ANR)|||
|C-S||Solvation/evaporation||Toluene, 2-methlypyridine and MO, ||[69, 70, 71]|
|[72, 73, 74]|
|C-N-S||Ti2CN calcination/sol-gel||Reactive brilliant red X-3B, Tetracycline||[75, 76]|
|SrTiO3||N||Solvothermal/Sol-gel||MO, MB, RhB|||
|ZnO||N||Decomposition reaction of Zn nitrate||MO|||
|WO3||N||Thermal decomposition in NH3||MeOH Oxidation, MO oxidation||[87, 88]|
|F||Hydrothermal||rhB degradation Phenol||[89, 90]|
|LaCoO3||C||Sol-gel process||CO2 reduction|||
2.3 Grafting of semiconductors by co-doping
2.3.1 Non-metal co-doping
Photocatalysts are not only doped with single
In addition to above mentioned non-metals, some halogens have also been reported for doping of TiO2 [99, 100]. An example for halogens doping is preparation of Cl-B co-doped nanocrystalline titanium dioxide by a hydrothermal method using TiCl4 as a titanium source and mixed hydrobromic acid (HBr) with ethanol as a bromine source, the doping of Cl− and Br− indicated narrowing of band gap and enhanced the photocatalytic activity for the overall water splitting process under visible light .
Microcystins (MCs) are the effective toxins which are produced and released by algae in the fresh and brackish waters upon cell rapture. Among dozens of congeners MC-LR is becoming a cause for disturbance to water quality and environment due to its concentration in water and high solubility and stability in water. Among many practices, N-F co-doped TiO2 has been reported to degrade it by the attack of OH• on the toxic ADDA (3-Amino-9-methoxy-2,6,8-trimethyl-10-phenyldeca-4,6-dienoic acid) chain under the visible light, normally the destruction of ADDA chain eliminates the associated toxicity but this breakage requires UV light <280 nm, but in case of N-F co-doped TiO2 the production of free radicals due to photoexcitation, reductions and oxidations have reported to attack the ADDA and Mdha (Methyl-dehydroalanine group) chains and have resulted in the degradation of toxin and production of non-toxic intermediates and products .
Among titanates, co-doped K2TiO4, SrTiO3, La2Ti2O7, K2Ti4O9 have been reported. The Co-doping of SrTiO3 with carbon and sulfur has been reported. Co-doped product was produced by the calcination of mixture of thiourea and SrTiO3 powders in lidded crucible at different temperatures. The addition of C and Si were confirmed by FTIR, XRD, XPS analysis, the obtained powder had the enhanced absorption shift from 400 to 700 nm. Cationic sulfur and tetravalent carbon doping increased the oxidative degradation of 2-propanol under visible light at λ 440 nm .
Nisar et al.  investigated the increased efficiency of BiTaO4 by non-metal mono and co-doping in order to enhance its visible light activity. This SC has the band gap of 2.75 eV but it has ability to absorb only 19% of the visible light. Nitrogen doping to lattice created an electron acceptor state just above the VB in order to increase VBM. The lattice was co-doped with carbon and sulfur and after doping it was compared with the bulk. It was analysed that C-S doping led to the notable band gap reduction about 39% which was very close to the required band gap for a good photocatalytic material. The doped material had good overall water splitting ability . Recently, co-doping of CeO2 with Carbon and nitrogen has been reported to enhance its visible light photocatalytic activity. Analysis and calculations revealed the addition of non-metals in the lattice. C-N co-doping shifts the fermi level at the bottom of conduction band by creating impurities in the lattice followed by the increased absorption of light under visible region. The surprising fact about this catalyst was its absorption intensity between 400 and 600 nm was very high as compared to other co-doped and N-doped CeO2 and C-doped CeO2 .
2.3.2 Non-metal-metal co-doping
To enhance the photocatalytic activity of semiconductors, co-doping with metal and non-metals has also been reported. In case of TiO2, Bagwasi et al. has reported the synthesis, characterization and application of Bi-B-TiO2 nanoparticles. The co-doped nanoparticles were prepared by sol-gel method. Results indicated the bismuth and boron were doped in TiO2 lattice, as Bi substituted Ti as Bi3+ which reduced the rate of recombination and B was present as interstitial and substitutional B which enhanced the visible light absorption. Bi-B co-doped samples showed better activities for degradation of acid orange 7 (AO7) and 2,4-dichlorophenol under visible light (λ = 700 nm) irradiation .
TiO2 is also co-doped with boron and nickel in the form of its oxide. As mentioned in Figure 12. The addition of boron at substitutional or interstitial position increases the response to visible spectra while the loading of Ni2O3 further enhanced its photocatalytic activity. TCP, 2,4-DCP and sodium benzoate were chosen as target pollutants. TCP was not only efficiently degraded under the visible light but also its was mineralized, moreover the degradation of other two pollutants was also same as of TCP .
Doping of NaNbO3 powders with Cr-N and Mo-N has been studied by using hybrid density functional theory. Co-doping with two pairs of metal/non-metal was tested separately to check the enhanced visible light activity of doped NaNbO3. Metal atoms (Mo or Cr) replaced the Nb from the lattice while the O was replaced by nearest Nitrogen atom. Analysis and calculations revealed that monodoping of different dopants and co doping of Cr-N are inappropriate for photocatalytic decomposition of water under visible light because the defects formed due to dopants are above the fermi level so they cannot act as charge trapping sites thus resulting to increased rate of recombination. While, the co-doping of Mo-N proved to be an appropriate dopant as it reduced the band gap by creating different energy levels. Whereas the band gap reduction is dependent on the concentration of dopant material. Mo-N doped NaNbO3 have overall enhanced water splitting ability and a promising photocatalyst for pollutant degradation ().
2.4 Metal doping
Doping in the semiconductors mostly become a reason to point defects which introduces the levels or states near, above or below the valence and conduction bands which are identified and calculated by different analysis. When the metal is incorporated in a lattice, it is doped in the form of metal ion which produces a band or energy level in the forbidden energy area thus rendering the photocatalyst able to absorb visible light irradiation. Additionally, doped metal in the form of metal ion can change the equilibrium concentration of charge carriers by acting as an electron acceptor. Thus, increasing the overall quantum efficiency of the photocatalytic process . The doping of semiconductors with metals/metallic ions has also been investigated in recent decades using many procedures including sol-gel, hydrothermal, solvothermal processes, etc. (as discussed earlier). Photocatalysts can be doped with transition metals like Fe, Cr, Mn, W, Ru, Rh, low cost, non-noble transition and earth abundant metals like Co, Cu, Ni and the noble metals like Pt, Au and Ag.
Co-doping of N-doped TiO2 with metals like
Radio frequency (RF) sputtering technique was used to deposit
Besides TiO2 and ZnO,
Electronic, geometric and optical properties of
Hu et al. reported the band gap-tunable K-doped g-C3N4 which had enhanced mineralization capacity, using dicyandiamide monomer and potassium hydrate as precursors followed by mixing, heating and annealing. SEM, TEM, FTIR, XRD and XPS analysis were used for the characterization and catalyst was used for the degradation of organic rhB under visible light and showed 6.5 times greater photocatalytic activity as compared to pristine gCN as it gave 70% decomposition during the irradiation time of 120 min . Tungsten doped porous g-C3N4 was synthesized by hydrothermal method using urea, dicyandiamide and Na2WO4.2H2O as precursors and catalysts with varying molar ratios of precursors were prepared and the catalyst W5/PGCN (P stands for porous) gave the highest photocatalytic activity due to separation of charges and shown 99.6% degradation of MO under visible light (λ = 400–420 nm) for the irradiation time of 60 min and 100% in 70 min . Beside W, other transition metals like Yttrium (), Iron , Eu, Zr , etc. doped gCN for the increased photocatalytic activity has also been reported in literature.
3. Dye sensitized VLA semiconductors
Dye photosensitizations have been reported by different scientists being a most operative mode to increase the response of semiconductors for visible light. Sensitization has been used for different approaches, from development of solar cells to degradation of pollutants in water. Many dyes like erythrosine B, eosin, rose bengal, rhodamine B, cresyl violet, thionine, chlorophyllin, anthracene-9-carboxylic acid, porphyrins, phthalocyanines and carbocyanines have been reported for their work as sensitizers, in addition to these organic dyes some inorganic dyes and coordination metal complexes are also reported. Inorganic sensitizers are basically the semiconductors with smaller band gap which are highly stable to photodegradation or photocorrosion. Their smaller band gap gives the light absorption at the wider wavelength region and examples are Mn, Fe, Ni, V, and Cr . The principle of sensitization for photodegradation of pollutants is “an electron in a sensitizer molecule under visible light (as dyes have conjugate system that absorbs visible light) is excited (from HOMO to LUMO) to its conduction band from where it jumps quickly to the conduction band of attached semiconductor oxide and dye itself changed into its cationic radical and SC’s CB act as an electron mediator where it is accepted by oxygen, thus starting the oxidations reactions by forming superoxide and OOH•, which are then converted to OH• for the degradation of pollutants”. A main limitation/drawback of sensitization with an organic dye is its steady decomposition because of photocatalytic degradation due to its natural capacity to undergo redox reactions by donating its electrons, to dodge this limitation the addition of sacrificial electron donor is possible like the incorporation of EDTA and TEOA (triethanolamine) will improve the stability of dye. In a dye sensitized process the dye can be used as both a sensitizer or a substrate to be degraded in order to decolorize water . The general mechanism for dye sensitized process for example rhB is given as:
Many organic dyes have been tested for their excellent sensitizing ability to semiconductors like TiO2. Degradation of phenylurea herbicide monuron has been reported by using riboflavin-assisted photosensitization, an enhanced photodegradation effect was observed as compared to direct photolysis , degradation of micosporine like amino acids (small secondary metabolites produced by organisms that live in environments with high volumes of sunlight, usually marine environments by some type of algae) was observed by using rose bengal and riboflavin sensitizers . Degradation of dye named reactive red 198 has been reported under visible light irradiation by using dye sensitized TiO2 activated by ultrasound, degradation rates were analysed by varying experimental parameters like initial concentration, pH and catalyst loading, the singlet oxygen and superoxide radical were found as dominant oxidative species which also degraded the produced intermediates like phenols. The results determined that a conventional dye can be used as a photosensitizer of TiO2 functioning under visible light . A study investigated the application of TiO2 sensitized by tris(4,4′-dicarboxy-2,2′-bipyridyl) ruthenium(II) complex for CCl4 deprivation under visible light irradiation. The transferred electrons to the CB of TiO2 from the excited complex molecule decomposed CCl4 at λ > 420 nm, experiment in the absence of TiO2 revealed that there was no direct transfer between excited sensitizer complex molecule and pollutant, results also determined that sensitizing complex undergo redox reaction and photodegradation decreased in the absence of sacrificial electron donor which restore the RuII complex which undergo continuous oxidations by electron transfer, to avoid this problem different types of alcohols can be used but 2-propanol was used for RuIIL3/TiO2/CCl4, in this process CCl4 was decomposed in CCl3 and Cl. .
Construction of heterojunctions or nanocomposites is a method to increase the charge separation and to increase the absorption towards visible light region in the solar spectrum. As discussed above, the increased charge separation will reduce recombination resulting in increased production of reactive oxidizing species leading to enhanced degradation of contaminants in water and wastewater treatment. The crystal lattice structure at the point of interface or junction plays an important role in tailoring the photocatalytic properties or quantum efficiency of the photocatalyst. A difference in the lattice spacing of two SC crystals cause the lattice mismatch at junction point which is the reason for defects formation which act as excited electron sink and lessens the electron hole fusion . Careful selection of semiconductor material is required with respect to band edge positions. The band edge positions of widely used semiconductors are given in Figure 16. The traits for ideal nano-heterostructures which have to be used for photocatalytic processes are; (i) it should have large surface area and contain enough active sites; (ii) it should have high light absorption capacity to make efficient use of solar spectrum; (iii) there should be an effective separation of charge carriers in order to produce active radicals for pollutant degradation; while a co-catalyst in heterostructure should have ability to enhance the reaction rate, provide active sites and should act as electron scavengers . Due to their increasing demand for the degradation of pollutants controllable fabrication of heterostructures/nano-composites is possible, the different techniques which are being used over decades are chemical vapor deposition, chemical deposition, electrodeposition, etc. By using these techniques different types of heterostructures (capped and coupled) such as nano-composites, nano-rods, nano-sheets, nano-wires and core-shells (capped) structures have been reported. In comparison to single/alone SC the heterojunctions like CdS/TiO2, CdS/ZnO, ZnSe/ZnO, ZnS/ZnO, SnO2/CdS, Bi2S3/TiO2 and some ternary composites like Fe3O4/SiO2/TiO2, ZnO/TiO2/CuO, etc. have been reported.
The heterojunction which are made by the combination of two or more nanocystalline semiconductors are very fruitful for photocatalysis regarding pollutant degradation and water splitting and being very famous as the Z-scheme process. Two main benefits of linking two or more semiconductors are (i) coupling of semiconductor having larger band gap with the semiconductor having smaller one, amplifies the photo response acting as a sensitizer; (ii) recombination is avoided by the transfer of excited electron in the low lying CB of SC bearing larger band gap . So, it is crucial to find a suitable sensitizer for a semiconductor having larger band gap to get enhanced photocatalytic activity under visible light.
4.1 Some TiO2-based heterostructures/nanocomposites
CdS is an attractive semiconductor with a smaller band gap of 2.4 eV, which means it can be activated under visible irradiation. The drawback to this and some other semiconductors having smaller band gaps is their unstability against photocorrosion. To avoid this problem, this type of semiconductors are coupled with those which have larger band gap like ZnO, ZrO2, TiO2, etc. and play a vital role in improving charge separation. As mentioned above there are many strategies to prepare the heterostructures and one is micro-emulsion method. CdS nanoparticles were coupled with TiO2 via micro-emulsion method under ultrasonic irradiation for the formation of core-shell type of nanostructure with uniformed coating of TiO2 nanoparticles on CdS, the depth of TiO2 shell was in range from 1.4 to 2.3 nm which could be controlled by varying the preparation temperature and precursors concentration. The nanostructure gave the red-shift in spectra which is typical trait of core-shell heterojunction . Another TiO2/CdS core-shell nano-rod heterostructure was obtained by chemical bath deposition method, TiO2 core was prepared firstly by the hydrothermal method and was converted to substrate for the deposition of CdS nanoparticles by dipping it an aqueous bath having 10 ml 0.02 M CdCl2.2.5H2O, 10 ml 0.2 M CH4N2S, 10 ml of 1.5 M NH4NO3 and 10 ml 0.5 M KOH to adsorb CdS nanoparticles on TiO2 rod at 85°C. The resulting structure gave the highest charge separation (Figure 17) efficiency at incident wavelength of 500 nm .
A thin film heterostructure of copper zinc tin sulfide (Cu2ZnSnS4)-TiO2 was prepared by combining an
Recently, the preparation of magnetic core-shell-shell heterostructure nanocomposite of Fe3O4/SiO2/TiO2 has been reported for the degradation of 2-CP in unreal wastewater under UV irradiation. Catalyst was prepared by three steps-facile synthesis process. Analysis was performed for surface morphology, chemical properties and for crystal structure. The size of NPs of magnetic core was 24.0 nm and that of magnetic shell-shell was 70.2 nm. Experiments were performed by varying the experimental parameters like pH, catalyst loading and pollutant concentration; results determined that effective degradation was pH dependant. Catalyst was regenerated after use by placing magnet under reaction container and retained its efficiency about 60% even after 3 cycles of use .
Another example of heterojunction is coupling of Ag3PO4 with TiO2 to degrade the organic pollutants under visible light irradiation using silver nitrate, sodium phosphate and TiO2 Degussa (P25) as precursors followed by in-situ precipitation method, by coupling the semiconductors the band gap reduced to 2.3–2.5 eV and shown a notable shift from UV region to visible spectra. Analysis confirmed the size of particles and uniform crystallinity 2-CP was selected as the target pollutant because this parent compounds and derivatives are being an emerging pollutant and already in the POPs. Experiments were performed by changing the parameters like pH, catalyst loading and pollutant concentration. At low pH of 3 greater adsorption of pollutant was observed and maximum degradation was reported. The structure maintained its stability to 100% (Figure 19) even after 3 cycles of use with fresh 2-CP .
Pan et al. has reported a novel structure of TiO2-ZnO nanocomposite spheres decorated with ZnO, this structure was prepared in order to increase the photocatalytic activity by improving charge separation in heterostructure. The composite was prepared by one-pot solvothermal method using tributyl titanate and zinc acetate as precursors and heating the mixed solution at 150°C for 24 h followed by calcination in air, as-prepared product was characterized. Surprisingly, by increasing to amount of Zn precursor the clusters of ZnO were produced on the surface of spheres (Figure 20). Analysis determined that prepared ZnO and TiO2 had the particle size in spheres was about 4 nm and spheres’ surface thickness was about 5 nm. It was also discovered that the clusters which decorated the spheres only had Zn and O and did not have Ti atoms. PL spectra for composite indicated the increased charge transfer and separation as compared to pristine ZnO and TiO2 due to presence of ZnO clusters acting as electron scavengers. To investigate the photocatalytic performance of ZnO-TiO2-SC rohdamine B (rhB) degradation was tested, OH• were reported to be the reactive specie, the activity of ZnO-TiO2-SC for photodegradation was 2.3–2.8 times higher than that of pristine nanoparticles .
Stable preparation of core/shell nanocomposite of TiO2/FeS2 by solvothermal method has been reported for the photocatalytic production of hydrogen . The benefits for incorporating different metal oxides/sulfides led to the structural and chemical modifications which render them better than that of parent materials. Rashid et al. has reported the formation of stable spherical nanocrystals of anatase-TiO2/FeS2 by following wet chemical process, for the degradation of organic pollutants under visible light using FeSO4.7H2O, Na2S2O3 and TiCl4 as precursors. Micrographs and other analysis determined the morphology, chemical properties, crystal structure, oxidation states and band gap positions which was 2.67 eV for the composite and gave the red shift in spectra. The photocatalytic activity of FeS2 and TiO2 was tested alone and also for composite but the photoactivity of nanocrystal composite for the degradation of methylene blue, was much higher than that of pristine compounds. Experiments were performed by varying the parameters like pH, catalyst dose and pollutant concentration. Composite was found to be much stable as it shown only 9% loss in photocatalytic activity after 3 cycles of use .
Among venedates, bismuth vanadate and indium vanadate have gained much respect mainly due to stability, nontoxicity and photocatalytic activity under visible light (λ > 420 nm) in coupled or single conditions. For coupled semiconductor heterostructure of TiO2/InVO4, InVO4 was prepared using organic precursor method and was incorporated with TiO2 by grinding, the catalyst shown higher photocatalytic degradation of 2-CP under visible light as compared to TiO2 alone. Among different conditions the best condition for degradation were found at 5pH in 1 g/L of catalyst and 50 mg/L of pollutant with irradiation time of 180 min [143, 144]. Li et al. has reported the unique structure of TiO2 incorporated on the polymethyl methacrylate (PMMA) nanofibers for the degradation of pollutants under the UV irradiation. The TiO2 nanoparticles were supported on fibers by the hydrothermal treatment at 135°C for 8 h using titanium n-butoxide and PMMA nanofibers as precursors. Analysis indicated that about 42% of tetragonal anatase TiO2 particles were adsorbed on the surface of fibers (Figure 21). Methylene orange was used as model pollutant and its complete degradation was observed after 50 min using 0.1 g of catalyst for 10 mg/L of pollutant. This good photocatalytic activity could be attributed to the (i) decoration of TiO2 nanoparticles on the PMMA fibers which assisted the adsorption of pollutants and helped them to come in contact with photocatalyst; (ii) high quantity of adsorbed TiO2 provides numerous action sites for the degradation of pollutants. Catalyst revealed the efficiency of about 94.4% even at the end of fifth cycle for the degradation of fresh MO which determined the stability and reusability of catalyst .
A novel nanocomposite of BiOBr/TiO2 has been reported and prepared for the first time with facile acid assisted precipitation method by using TTIP, KBr and ((BiNO3)3.5H2O) as precursors. Catalysts of different percentages were prepared by using different molar ratios of TiO2 as a base material and 15% BiOBr/TiO2 behaved as an active catalyst. Analysis and characterization revealed the perfect structural integrity, increased surface area and increased absorption of light because of the formation of nanoscale layered butterfly like clustal structures with each flake having the broad absorption spectrum of about 500–800 nm with <50 nm thickness (Figure 22). PL spectral analysis determined the band gap of 2.81 eV and wavelength was observed from 480 to 570 nm for 15% BiOBr/TiO2 and it gave the degradation of aqueous ciprofloxacin (target pollutant) under visible light at λ > 420 nm about 92.5% and under direct sunlight it gave 100% degradation utilizing reaction time of 2.5 h. Radical scavenging study indicated that besides superoxide radicals and holes the OH• had dominant effect on net photodegradation process. Results also suggested that the catalyst was 9.4 and 5.2 times active in degradation than pristine BiOBr and TiO2, reusability experiments determined the high stability of catalyst as it suffered loss of only 12% even after 5 cycles of fresh CIP degradation .
4.2 Heterostructures/nanocomposites of different SCs
In addition to TiO2 there are numerous semiconductors which can be coupled with other SC and can be incorporated into heterostructures or composites like WO3, ZnO, BiVO4, ZnSe, C3N4, In2O3, CuS, MoS, Cu2O and many more. So another example of inorganic heterostructure is the template free simple synthesis of CdS-ZnO nanocomposites. This self-assembled flower like structure resulted from coupling of two SCs which increased the charge separation and demonstrated greater photocatalytic activity. The average size of flower was 400 nm with the petal size of 100–150 nm and the rod among petals had the size of 10 nm, band gap of composite was analyzed to be 2.19 eV and absorption wavelength of 561 nm was reported. The composite gave the photodegradation of rhB about 90% in 190 min under solar light and 24% in dark. The scheme of process of particles is shown in (Figure 23
Cho et al. prepared three different types of 3D ZnSe/ZnO heterostructures by simple solution-based surface modification reactions. Three different types of heterostructures demonstrated higher photocatalytic activities by exhibiting absorption in visible region (at λ > 486 nm) as compared to pure 3D ZnSe and ZnO structures, the visible light activity of heterostructures varied according to the crystal structures. As shown in (Figure 24) the CB of ZnO is in between the CB and VB of ZnSe showing the type II band alignment, before exposure to sunlight the catalysts and orange II (targeted pollutant) were kept at stirring for 30 min in dark to attain an equilibrium for adsorption and desorption, upon exposure to visible light the e−/h+ pair was generated in ZnSe crystal, electron transferred to the CB of ZnO to reduce oxygen and holes could oxidize either the water or OH ion or directly oxidize the orange II, ended with the mineralization of organic compound .
Zeyan et al. has produced the In2O3/ZnO heteronanostructures by the co-precipitation method having average size of 40–60 nm by using the respective precursors. The composite was annealed at different temperatures ranging from 600 to 1000°C, among changed compositions and annealing temperatures the highest photocatalytic activity for the degradation of methylene blue was shown by the composite annealed at 800°C with In/Zn molar ratio of 1:1 and the maximum absorption was about λ = 663 nm. A p-n junction was established at the SCs interface and presence of Zn2+ and In3+ was reported in lattice, that enhanced the charge separation and production of OH• and O2•− attributed as the main reason for enhanced photocatalytic activity semiconductor coupling (). Coupling of mixed oxide SC with metal oxide has also been reported and have shown some modified properties, example for this type of heterojunction is the nanocomposite of ZnO-ZnWO4 (both are the n-type SCs) prepared by the sol-gel method and was analysed by XRD, BET, SEM and TEM. The nanocomposites were prepared by varying the molar ratio of ZnO and ZnWO4 to study the influence of molarity on photoactivity and Zn-ZW0.25 calcined for 2 h at 600°C shown greater photodegradation of 4-nitrophenol (target pollutant). The band gaps for ZnO and ZnWO4 was calculated to be 3.21 and 3.14 eV, when the nanocomposite was exposed to UV light the electron transferred from the CB of ZnO (ECB = −0.36 eV) to CB of ZnWO4 (ECB = −0.14 eV) due to difference in the position of CBs (from cathodic to anodic condition) and same behaviour was proposed for hole to transfer from VB of ZnWO4 (EVB = 3.00 eV) to VB of ZnO (EVB = 2.84 eV), thus enhancing the charge separation and completion of circuit due to formation of heterostructures which resulted from the mixing of two SCs with dissimilar energy levels of VB and CB . In addition to the above mentioned heterostructures other structures like nanorods, nano sheets, nanowires, CdSe/ZnO, CdsSe/ZnO , TiO2/ZnO , CuS/ZnO  has also been found to enhance visible light activity either for pollutant degradation, overall water splitting or hydrogen production.
BiOCl/BiVO4, another novel p-n heterostructure of coupled semiconductors with type II band alignment was prepared by hydrothermal method for the decomposition of methyl orange under visible light irradiation having ability for active separation of charges (Figure 25), the powders were prepared by using NH4VO3, Bi(NO3)3·5H2O, NaOH and HCl as precursors for BiVO4 and BiOCl, followed by the stirring, heating and washing. Catalysts having different molar concentrations were prepared by varying the amount of HCl in the mixture and the catalyst having the molar ratio of 0.75BiOCl/BiVO4 was seemed to be more active. Analysis and characterizations determined th-presence of Bi as Bi3+ and vanadium as V5+ and O as O2•− and Cl as Cl−. For the tests of photocatalytic activity, Degussa P25 was used as control group, and results determined the increased degradation of MO in BiOCl/BiVO4 system and it was about 1.89 times greater than that of TiO2 and 3.54 times from BiVO4. Free radical scavengers illuminated that the holes in the valence band of
WO3 is a known semiconductor due to its polycrystalline forms and smaller band gap of about 2.4–2.8 eV depending on crystal structure; which means its electrons can be excited by visible light irradiation, the main limitations of this SC which keep it far from becoming a useful semiconductor are; higher rate of recombination and its unstability against photocorrosion . WO3 is incorporated in heterojunctions in order to increase the absorption in visible light region. Shamaila et al. has reported the formation of WO3/BiOCl heterojunction or the degradation of organic pollutants under visible light using BiCl3, Ammonium tungstate and ethanol as precursors, 2D nanoflakes of BiOCl of the size of 75–200 nm were fabricated (Figure 26) by following a new low temperature route and nanocomposite was prepared to enhance the visible light response, BiOCl performed the role of a main photocatalyst while WO3 worked as a sensitizer. For the prepared composite the absorption range increased from 360 to 500 nm as the quantity of WO3 increased while synthesis, the catalyst gave 100% deterioration of Rhodamine B was under visible light during the irradiation time of 180 min, which was greater than the activity of WO3, BiOCl and Degussa P25 .
Another heterojunction photocatalyst with high photocatalytic activity is WO3/SrNb2O6, was prepared by the milling-annealing method which was found to be better than the direct mixing method as this method could build a firm chemically bonded interface between two semiconductors. Results determined that the composite had higher photocatalytic activity as compared to pure WO3 and SrNb2O6. As we know that anything which can scavenge the excited electron can be a reason for increased photocatalytic process so, the effective charge separation among semiconductors and formation of holes and radicals led to the direct or indirect degradation of methyl orange . Ag3PO4/WO3 nanocomposites were prepared by a deposition-precipitation method using Na2WO4·2H2O, NH4Cl, AgNO3 and Na2HPO4 as precursors and prepared powders were characterized by SEM, XRD and UV-Vis. Catalysts were prepared of variable molar ratios of Ag3PO4:WO3 and the catalyst having ratio of 6:4 (AW6/4) shown the greater photocatalytic activity for the degradation of rhB and MO at the wavelength λ > 420 nm, mainly due to the excellent separation of charge carriers. Reusability tests indicated that composite had higher recyclability as compared to Ag3PO4 alone as AW6/4 gave 97% removal of rhB and MO in 6 and 35 min (after being exposed to visible light) even after the fifth run (had same efficiency for first run) while Ag3PO4 gave only 25% degradation at the fifth run due to the absence of sacrificial donor. Stability analysis revealed that catalyst AW6/4 was stable against photocorrosion as it retained the XRD pattern even after 5 cycles for degrading fresh rhB, only a small amount of metallic Silver was observed on Ag3PO4 after use, SEM analysis also supported stability result .
A hybrid photocatalyst W18O49/TiO2 having an urchin like structure (Figure 27) was prepared by an alcohol thermal method, which had high surface area of 178 m2 g−1 and shown absorption in the wide range of 200–800 nm and tested for the photodisintegration of MO and phenol under UV-visible irradiation. The hybrid photocatalyst attained synergetic increase in photoactivity and photostability of W18O49, well-related band structure enhanced the charge separation and transfer which led to the production of free radicals as well as prevented the W18O49 from self-oxidation due to holes as they moved towards TiO2. Free radical scavenging tests indicated that O2•− was reactive oxidizing specie for the degradation of MO and phenol. Reusability tests revealed the stability of catalyst as it maintained its XRD spectra even after the fifth cycle which meant catalyst did not suffer any noticeable loss, hybrid composite also maintained its original blue color at the end of fifth run .
From metal tungstate an example of a p-n heterojunction is the fabrication of a novel Z-scheme WO3/CdWO4 photocatalyst by the fusion of sheet like WO3 (n-type) and rod like nanostructure of CdWO4 (p-type), for this purpose the catalyst were prepared separately by using respective precursors and fusion was done by using hydrothermal and chemisorption methods. As-prepared catalysts were used for the degradation of organic dyes like Methly orange, Rhodamine B and methylene blue, upon exposure of light the transfer of electrons and holes occurs from the CdWO4 to WO3 and vice versa which led to circuit completion and efficient increase in charge separation, PL spectra gave the smaller curve peak proving the less relaxation of electron towards VB and the absorption intensity of λ > 476 nm. Stability tests were performed to check the structural reliability of catalyst, it did not show any significant loss even after 3 cycles of reuse for the degradation of fresh dyes. Results also indicated the degradation of dye was about 7 and 2.3 times greater than CdWO4 and WO3 alone which was credited to enhanced surface area and effective separation of charge carriers .
In addition to the binary composites, some tertiary (complex) composites have been reported, where the multi-photon excitation took place in the photoactive materials and charge transfer and separation was increased due to increased surface area and different transition states. KTaO3-CdS-MoS2 is an example of tertiary composite which was prepared by hydrothermal method by rigorously following the temperature and pressure conditions, the obtained powders were of different structures like nanoleaf, cubic and hexagonal spheres exhibiting activity under both visible and UV light and were used for the degradation of toluene and phenol. The catalysts shown 42% degradation under visible light and 80% degradation of pollutants under UV light. Prepared catalyst exhibited good stability (about 50%) even after 4 cycles for the degradation of fresh toluene . In case of some ternary composites like ZnO-AgBr-Ag2CrO4 (n-n junctions), two SCs worked as donors of photoexcited electrons and oxidation of pollutants occurred by the formation of superoxide radicals at the CB. By the charge separation the phocatalytic activity of composite was 16 and 7 times higher than those of ZnO and ZnO/AgBr for the degradation of rhB . Rhodamine B also suffered degradation by the photocatalytic activity of In2O3-AgBr-BiWO6 (Figure 28), prepared by microwave assisted irradiation method, optical, morphological and structural properties were analysed by XRD, SEM, TEM, XPS, HRTEM which indicated the flower-like pattern of assembled nanoparticles. The increased photoactivity under UV, visible and solar light was attributed to increased surface area and charge separation due to differences in the redox potentials of SCs bands. Reactive species scavenging testes determined that OH• and superoxide radicals were dominant reactive species .
Besides all of the above discussed heterostructures, nanocomposites, coupled semiconductors, either oxides or sulfides, there are numerous other heterojunctions like WO3/NiWO4 , Ag3PO4/Bi2MoO6 , Ag3PO4/AgBr , CdS/Bi2MoO6 , CdS/Ta2O5 , BiOBr/ZnFe2O4 , Cu2O/SrTiO3 (), ZnS/CuS/CdS , SnO2/ZnO/ZnWO4  and many more have been reported to increase the ability of pure SCs to harvest the sun light either in the field of water or wastewater treatment for the overall splitting of water, degradation of Organic, inorganic pollutants, phenols, MCs, POPs and other emerging contaminants.
5. A glance at g-C3N4-based heterostructures/nanocomposites
It has been more than a decade that people are being aware from environmental protection and conservation, the era of industrialization besides increasing the gross productivity also posed serious effects on the health of water bodies by discharging unchecked amounts of effluents and other chemicals, in order to improve the water quality the focuses are being paid to treat water and wastewater, the idea of semi-conductor photocatalysis has been emerged which uses solar energy in its full potential, for this purpose many SCs either in single or in heterostructures have been discussed in Section 6.
In addition to first generation photocatalysts, an emerging polymeric photocatalyst is Graphitic Carbon Nitride (g-C3N4) which is an earth copious visible light active catalyst, having unique 2D structure with high stability and flexible structure (which can be tailored) and low band gap of 2.7 eV. Pure gCN have high rate of recombination, smaller surface area and low ability to exploit visible light thus reducing the quantum efficiency of photosystem, the VL activity of gCN has been reported to increase by making heterostructures with other SCs by taking the advantage of its layered structure which assisted in hybridization with other constituents like CdS, TiO2, ZnWO4, ZnO, etc. either for the degradation of pollutants or for the evolution of O2 or H2 gas . Some examples of gCN HSs/HJs/Composites are discussed below.
Novel g-C3N4/TiO2 composites were prepared by the facile sonication method using melamine and titanium tetrachloride as precursors followed by stirring, sonication and drying at room temperature. Different catalysts were prepared by varying the concentrations of precursors and g-C3N4/TiO2-1.5 was found to be more active among other catalysts, as it shown higher photocatalytic degradation of MB under UV and visible light. Results demonstrated that catalyst shown 6.92 and 2.65 time greater activity than pure gCN and TiO2 under UV light, while 9.27 (gCN) and 7.03 (TiO2) folds greater photoactivity under visible light, which can be attributed the increased visible light absorption and efficient charge transfer in composite at interfaces of SCs. In the hybrid catalyst gCN could be triggered under visible light and the photoexcited electrons of gCN transferred to the CB of TiO2 due to interfacial connections and differences of redox potentials . Tunable band gap of some semiconductors is an effective way to harness solar light and among those gCN is a known SC. Two SCs having smaller band gaps (gCN and Bi2MoO6) were coupled to prepare a Z-scheme nanocomposite, number of catalysts were prepared by varying the concentrations of precursors and 25% g-C3N4/Bi2MoO6 was seemed to be most active, structure, morphology, light absorption spectra and charge carriers separation efficiency was analyzed and photocatalytic activities were evaluated for the degradation of MB. Both SCs in composite were excited at the λ = 410 nm, due to the negative redox potentials of gCN (as compared to Bi2MoO6), excited electrons of gCN transferred to CB of Bi2MoO6 and holes of later should had been migrated to the VB of gCN, but by this route the holes at the VB of gCN could not react with water of OH ion near its surface and same for Bi2MoO6, so it was observed that the excited electrons transferred to their respective CB, the relectrons from the CB of Bi2MoO6 were transferred to the VB of gCN (spatial separation) which inhibited the local recombination (Figure 29) thus completing the Z-scheme route, the CB of Bi2MoO6 and VB of gCN could not react with molecules in their vicinity and the catalyst shown 4.8 and 8.2 folds greater photoactivity than pristine SCs .
Feng et al. reported the fabrication of S-doped g-C3N4/Au/CdS composite as Z-scheme photocatalyst where CdS was deposited on g-CNS system in which Au nanoparticles were sandwiched between g-CNS and CdS (two visible light responsive SCs) by the chemical bath deposition and worked as charge transporter (Figure 30), whole system increased the degradation of rhB, MO, MB and increased reduction of water to hydrogen was observed under visible light (λ = 560 nm). The Z-scheme photocatalyst was characterized by SEM, HRTEM, PL spectra, Vis-diffuse spectra. These elementary, crystal and microcrystal analysis demonstrated the uniformity of novel composition, results revealed that the catalyst exhibited great photocatalytic activity as compared to g-CNS, g-CNS/Au, g-CNS/CdS, and pure CdS . Novel organic-inorganic composite of g-C3N4-CdS has been prepared which gave the degradation of organic pollutants under visible light. Results indicated the higher photocatalytic activity of about 20.5 and 3.1 times for degradation of MO as compared to gCN and CdS alone and 41.6 and 2.7 times higher for the degradation of 4-aminobenzoic acid .
GCN has also been reported to be composed with 2D graphene which is being focused due to its unique properties like amazing thermal, mechanical, surficial and electric properties. Tong et al. has prepared 3D porous gCN/graphene oxide aerogel structure by using gCN sheets and graphene oxide as precursors by following hydrothermal treatment method this composition resulted to enhanced visible light absorption, decreased charge relaxation and increased adsorption capacity. Analysis and characterizations were performed to check intrinsic properties. As-prepared catalyst was used for the CO2 evolution and MO degradation which was about 92% in 4 h under visible light . Han et al. has reported different g-C3N4/graphene nanocomposites which were proved to be effective for the degradation of dyes under visible light, different hybrids of gCN/graphene were prepared by using different methodologies and synthesis processes like solvothermal treatment, hydrothermal treatment, electrochemical reactions, etc. and their photoactivity was investigated for the hydrogen, oxygen, CO2 evolution and degradation of different organic compounds .
Among ternary composites the novel magnetically recoverable composite of g-C3N4/Fe3O4/NiWO4 was prepared by refluxing calcination method, different hybrids were prepared by varying the precursor’s concentration among which gCN/Fe3O4/NiWO4 (30%) was found to be more active, catalysts were characterized for their morphology, texture, electronic, thermal and magnetic properties. Hybrid catalyst shown their high photocatalytic activity under visible light for the degradation of rhB, MO, MB, fuchsine and phenolic compounds. Results confirmed that formation of HJs between gCN/M/NiWO4 increased the surface area and charge separation (Figure 31), thus increasing the quantum efficiency of system, photocatalytic activity of gCN/M/NiWO4 (30%) was 12, 30, 52 and 6 folds greater for rhB, MB, MO, fuchsine and phenol as compared to gCN, Fe2O3 and NiWO4 alone. Additionally the prepared composites exhibited high degree of stability even after the 4 cycles of reusability as it degraded about 87% of rhB at fourth cycle, unluckily, nanohybrid suffered from reduced surface area after the last run which was attributed to the blockage of degradation reaction intermediates at surface sites . Zhang et al. has used one-step solvothermal method for the preparation of spinel ZnFe2O4 nanoparticles and its decoration on g-C3N4 sheets for formation of water soluble magnetic-functionalized g-C3N4/ZnFe2O4. The magnetic properties of composite were controlled by the size of composite and decorated quantity of ZnFe2O4. Results indicated that catalyst exhibited efficient photocatalytic activity for degradation of MO under visible light and it was mainly due to the synergist effect of both SCs like smaller particle size and high solubility in water, interestingly the catalyst could be separated from aqueous solution by magnet. CN-ZnFe showed 98% of degradation of MO in 180 min which was 6.4 and 5.6 times higher than g-C3N4 and ZnFe2O4 alone. Free radical scavenging test revealed the decrease in efficiency indicated the vital role of OH• and superoxide radical in the pollutant degradation. The increased photocatalytic activity was credited to sufficient charge separation (). Synthesis of novel magnetic CdS/ZnFe2O4 nanocomposites has been reported (by two-step hydrothermal method) in order to enhance photocatalytic activity and photostability of SCs under visible region .
Heterojunctions of g-C3N4 with carbonaceous particles has been reported to make recyclable, stable and more efficient photocatalyst for the water treatment purposes. Chai et al. synthesized the g-C3N4 modified with fullerene for the removal of dyes from water under visible light. Fullerenes (C60) are known to have 30 molecular orbits with 60 π electrons with closed shell structure which helped in separation and transport of charge carriers, especially the photoexcited electrons. Because of the larger surface area and unique morphology, the electrons excited from g-C3N4 shifted on C60 thus got separated from hole and lessened the electron relaxation towards hole, the electron hole pair separation resulted in the opening of benzene ring during the process of organic molecule degradation [182, 183]. Bai et al. prepared g-C3N4/fullerene composite using thermal polymerization of dicyandiamide in the availability of C60 at 550°C. Addition of C60 in the gCN, shifted the VB of gCN at lower energy level thus its oxidation potential under visible light was increased. Figure 32 demonstrate the increased photocatalytic activity due to effective electron hole pair separation, when the catalyst was exposed to visible light electrons got excited from VB (formed by N2p orbitals) to CB (formed by 2Cp orbitals) of g-C3N4 leaving the holes behind in the VB, the excited electrons jumped to C60 from CB of gCN thus retaining the separation. Results demonstrated the enhanced degradation of MB and phenol at λ > 420 nm, degradation was about 2.9 and 3.2 time greater than that of bulk gCN, due to the efficient production of OH• from holes, which acted as oxidation species and played a vital role in opening of benzene rings ().
In addition to above discussed g-C3N4-based nanocomposites, there is a lot of literature based on the synthesis, uses and types of heterostructures based on the multifunctional approaches, as g-C3N4-based nanostructures (either with oxides or sulfides, either binary or tertiary) have become the main member of semiconductor photocatalysis family for the degradation of pollutants in environment specially in water. Besides g-C3N4/Fe2O3, g-C3N4/CeO2 g-C3N4/MoO3, g-C3N4/Fe3O4, g-C3N4/Ni(OH)2, g-C3N4/Ag2O, g-C3N4/MoS2, g-C3N4/NiS, g-C3N4/TaON, g-C3N4/ZnO, g-C3N4/g-C3N4, g-C3N4/In2O3, g-C3N4/WO3, SiO2/g-C3N4 and some ternary composites like, gCN/Fe3O4/CuWO4, BiOCl/Bi2MoO6/g-C3N4, Ag2CrO4/g-C3N4/GO, g-C3N4/TiO2/CNT, G-C3N4/CeO2/ZnO there are innumerable gCN composites, some composites with their photocatalytic activity and efficiency under visible light are mentioned in Table 2.
|Composite||Precursor/synthesis method||Targeted pollutant||Degradation efficiency/reason under visible light||References|
|TiO2/g-C3N4||P-25 and dicyandiamide||Methylene blue||90% degradation in 300 min, 3.5 greater efficiency than SC alone.|||
|WO3/ g-C3N4||Dicyandiamide and (NH4)5H5[H2(WO4)6]·H2O||MB and 4-CP||Degraded 97% of MB and 43% of 4-CP|||
|CdWO4/ g-C3N4||Melamine/mixed calcination synthesis||rhB||Degradation of rhB due to O2•− radical formation, 1.6 and 54.6 times greater efficiency than gCN and CWO.|||
|In2S3/ g-C3N4||Urea/hydrothermal synthesis||rhB||HJ formation widened the light absorption spectra, increased EHP separation and O2•− were reactive OS.|||
|V2O5/ g-C3N4||Melamine/one-pot synthesis||rhB||Deterioration of rhB due to O2•− and OH•, charge separation increased quantum efficiency under visible light.|||
|ZnO/ g-C3N4||Melamine and zinc acetate/simple calcination method||MO and p-nitrophenol||Degraded 97% of MO in 80 min, which was three and six times greater than gCN and ZnO alone.|||
|ZnWO4/g-C3N4||Melamine/facile chemisorption||MB||Higher electron hole pair separation, OH and O2•− were reactive species|||
|BiOI/BiOBr/g-C3N4||Dicyandiamide||MB||Effective charge separation, production of OH•, O2•− and h+|||
|ZnO/ZnS/g-C3N4||Melamine/two-step facile synthesis||H2 Production||Hydrogen production 1205 μmol/g-C3N4:16 μmol/g|||
|YVO4/g-C3N4/Ag||Hydrothermal/urea deposition method||MO||3 times higher activity as compared to gCN alone|||
|C3N4/CNT/NiS||Sol-gel method/direct precipitation of cyanamide||H2 Production||148 times higher activity than pure gCN/CNT|||
|Ag3PO4/GO/g-C3N4||Dicyandiamide/precipitation||RhB degradation||94.8% degradation in 50 min.|||
|g-C3N4/AgBr/RGO||Urea/hydrothermal treatment||Tetracycline and 2,4-DP||78.4% degradation in 90 min and 68.2% within 6 h.|||
|g-C3N4/TiO2/ZnO||Hydrothermal treatment||p-toluene sulfonic acid||90% degradation by composite, while only 40% by gCN|||
|g-C3N4/CeO2/ZnO||Urea/pyrolysis and exfoliation method||MB||11 times greater degradation than bare gCN|||
|Ag/g-C3N4/NaTaO3||Melamine/photo deposition process||Dyes and tetracycline||Improved dye degradation and 95.47% removal of tetracycline.|||
Majority organic, inorganic and other numerous pollutants which are either in the records of EPAs or not, are the refractory compounds and tend to become the part of fresh or potable water thus making it unfit for use. Besides employing membrane systems, VLA semiconductor photocatalysis has gained fame due to their cost effectiveness and eco-friendly nature and becoming a promising phenomenon for the treatment of water on global scale. The rapid development in field of nanotechnology has opened the doors for various advanced photocatalytic systems which includes the formation of complex structures by doping, co-doping, heterostructures, 0D to 3D structures and nanocomposites as heterogeneous photocatalysts, has been developed in recent decades and has helped the environment and water to get rid of stubborn pollutant species, such as bacteria like
Serpone N. Advanced oxidation processes. In: Kirk‐Othmer Encyclopedia of Chemical Technology. Vol. 1. Toronto, Canada: John Wiley and Sons, Inc.; 2000. pp. 1-17
Fujishima A, Zhang X, Tryk DA. TiO2 photocatalysis and related surface phenomena. Surface Science Reports. 2008; 63:515-582. DOI: 10.1016/j.surfrep.2008.10.001
Mills A, Le Hunte S. An overview of semiconductor photocatalysis. Journal of Photochemistry and Photobiology A: Chemistry. 2000; 108:1-35
Ohtani B. Photocatalysis A to Z—What we know and what we do not know in a scientific sense. Journal of Photochemistry and Photobiology, C: Photochemistry Reviews. 2011; 11:157-178. DOI: 10.1016/j.jphotochemrev.2011.02.001
Goodeve CF, Kitchener JA. Photosensitisation by titanium dioxide. Transactions of the Faraday Society. 1938; 34:570-579. DOI: 10.1039/TF9383400570
Nuno M, Ball RJ, Bowen CR. Photocatalytic properties of commercially available TiO2 powders for pollution control. In: Semiconductor Photocatalysis—Materials, Mechanisms and Applications. United Kingdom: IntechOpen; 2016. pp. 613-633. DOI: 10.5772/62894
Serpone N, Emeline AV. Semiconductor photocatalysis—Past, present, and future outlook. Journal of Physical Chemistry Letters. 2012; 3:673-677. DOI: 10.1021/jz300071j
Hoffmann MR, Martin ST, Choi W, Bahnemann DW. Environmental applications of semiconductor photocatalysis. Chemical Reviews. 1995; 95:69-96. DOI: 10.1021/cr00033a004
Kisch H. Semiconductor photocatalysis—Mechanistic and synthetic aspects. Angewandte Chemie, International Edition. 2013; 52:812-847. DOI: 10.1002/anie.201201200
Herrmann J. Titania-based true heterogeneous photocatalysis. Environmental Science and Pollution Research. 2012; 19:3655-3665. DOI: 10.1007/s11356-011-0697-8
Herrmann J. Heterogeneous photocatalysis: Fundamentals and applications to the removal of various types of aqueous pollutants. Catalysis Today. 1999; 53:115-129
Pelaez M, Nolan NT, Pillai SC, Seery MK, Falaras P, Kontos AG, et al. A review on the visible light active titanium dioxide photocatalysts for environmental applications. Applied Catalysis B: Environmental. 2012; 125:331-349. DOI: 10.1016/j.apcatb.2012.05.036
Agrawal A. Chapter 4 type I and type II band alignments in ZnO/MgZnO bilayer films. Applied Physics Letters. 2014; 105:081603
Kroemer H. Band Diagrams in Real Space: I2009. pp. 1-13
Wang Y, Wang Q. Visible light driven type II heterostructures and their enhanced photocatalysis properties: A review nanoscale. Nanoscale. 2015; 5:8326-8339. DOI: 10.1039/c3nr01577g
Opoku F, Govender KK, van Sittert CGCE, Govender PP. Recent progress in the development of semiconductor-based photocatalyst materials for applications in photocatalytic water splitting and degradation of pollutants. Advanced Sustainable Systems. 2017; 1:1700006. DOI: 10.1002/adsu.201700006
Wang Y, Wang Y, Li Y, Shi H, Xu Y, Qin H, et al. Simple synthesis of Zr-doped graphitic carbon nitride towards enhanced photocatalytic performance under simulated solar light irradiation. Catalysis Communications. 2015; 72:24-28. DOI: 10.1016/j.catcom.2015.08.022
Ibhadon AO, Fitzpatrick P. Heterogeneous photocatalysis: Recent advances and applications. 2013; 3:189-218. DOI: 10.3390/catal3010189
Fragalà ME, Di Mauro A, Cristaldi DA, Cantarella M, Impellizzeri G, Privitera V. ZnO nanorods grown on ultrathin ZnO seed layers: Application in water treatment. Journal of Photochemistry and Photobiology A: Chemistry. 2017; 332:497-504. DOI: 10.1016/j.jphotochem.2016.09.032
Martyna M, Diak M, Kozak M, Adriana Zaleska-Medynska EG. Some unitary, binary, and ternary non-TiO2 photocatalysts. In: Semiconductor Photocatalysis—Materials, Mechanisms and Applications. United Kingdom: IntechOpen; 2016. DOI: 10.5772/62583
Gaya UI. Heterogenous Photocatalysis Using Inorganic Semiconductor Solids. Switzerland: Springer; 2014
Medina-Ramírez AH-RI. Photocatalytic Semiconductors. Switzerland: Springer; 2015. DOI: 10.1007/978-3-319-10999-2
Turchi CS. Photocatalytic degradation of organic water contaminants: Mechanisms involving hydroxyl radical attack. Journal of Catalysis. 1990; 192:178-192
Ray MB. Photocatalytic oxidation of paracetamol: Dominant reactants, intermediates, and reaction mechanisms. Environmental Science & Technology. 2009; 43:460-465
Wang J, Tafen DN, Lewis JP, Hong Z, Manivannan A, Zhi M, et al. Origin of photocatalytic activity of nitrogen-doped TiO2 nanobelts. JACS. 2009; 131:12290-12297
Yongquan Quab XD. Progress, challenge and perspective of heterogeneous photocatalysts. The Royal Society of Chemistry. 2012; 42:2568-2580. DOI: 10.1039/c2cs35355e
Marschall R, Wang L. Non-metal doping of transition metal oxides for visible-light photocatalysis. Catalysis Today. 2014; 225:111-135. DOI: 10.1016/j.cattod.2013.10.088
Livraghi S, Paganini MC, Giamello E, Selloni A, Di Valentin C, Pacchioni G. Origin of photoactivity of nitrogen-doped titanium dioxide under visible light. Journal of the American Chemical Society. 2006; 128:15666-15671. DOI: 10.1021/ja064164c
Sato S, Nakamura R, Abe S. Visible-light sensitization of TiO2 photocatalysts by wet-method N doping. Applied Catalysis A: General. 2005; 284:131-137. DOI: 10.1016/j.apcata.2005.01.028
Asahi AR, Morikawa T, Ohwaki T, Aoki K, Taga Y, Lee V, et al. Visible-light photocatalysis in nitrogen-doped titanium oxides. Science. 2001; 293:269-271
Abadias G, Paumier F, Eyidi D, Gu P, Girardeau T, Wiley J. Structure and properties of nitrogen-doped titanium dioxide thin films produced by reactive magnetron sputtering. Surface and Interface Analysis. 2010; 42:970-973. DOI: 10.1002/sia.3220
Martínez-ferrero BE, Sakatani Y, Boissière C, Grosso D, Fuertes A. Nanostructured titanium oxynitride porous thin films as efficient visible-active photocatalysts. Advanced Functional Materials. 2007; 17:3348-3354. DOI: 10.1002/adfm.200700396
Premkumar J. Development of super-hydrophilicity on nitrogen-doped TiO2 thin film surface by photoelectrochemical method under. Chemistry of Materials. 2004; 16:3980-3981. DOI: 10.1021/cm049055g
Choi H, Antoniou MG, Pelaez M, De la Cruz AA, Shoemaker JA, Dionysiou DD. Mesoporous nitrogen-doped TiO2 for the photocatalytic destruction of the cyanobacterial toxin microcystin-LR under visible light irradiation. Environmental Science & Technology. 2007; 41:7530-7535. DOI: 10.1021/es0709122
Yang J, Chen DX, Deng AP, Huang YP, Chen CC. Visible-light-driven photocatalytic degradation of microcystin-LR by Bi-doped TiO2. Research on Chemical Intermediates. 2011; 37:47-60. DOI: 10.1007/s11164-010-0224-4
Vitiello RP, Macak JM, Ghicov A, Tsuchiya H, Dick LFP, Schmuki P. N-doping of anodic TiO2 nanotubes using heat treatment in ammonia. Electrochemistry Communications. 2006; 8:544-548. DOI: 10.1016/j.elecom.2006.01.023
Zong X, Sun C, Yu H, Chen ZG, Xing Z, Ye D, et al. Activation of photocatalytic water oxidation on N-doped ZnO bundle-like nanoparticles under visible light. The Journal of Physical Chemistry. 2013; 117:4937-4942. DOI: 10.1021/jp311729b
Zhang D, Gong J, Han G, Tong Z. A facile method for synthesis of N-doped ZnO mesoporous nanospheres and enhanced photocatalytic activity. Dalton Transactions. 2013; 42:16556-16561. DOI: 10.1039/c3dt52039k
Kumar R, Abdel-wahab MS, Barakat MA, Rashid J, Salah N, Al-ghamdi AA. Role of N doping on the structural, optical and photocatalytic properties of the silver deposited ZnO thin films. Journal of the Taiwan Institute of Chemical Engineers. 2016; 69:131-138. DOI: 10.1016/j.jtice.2016.09.027
Tuomisto F, Rauch C, Wagner MR, Hoffmann A, Eisermann S, Meyer BK, et al. Nitrogen and vacancy clusters in ZnO. Journal of Materials Research. 2013; 28:1977-1983. DOI: 10.1557/jmr.2013.195
Barnes TM, Olson K, Wolden CA. On the formation and stability of type conductivity in nitrogen-doped zinc oxide. Applied Physics Letters. 2005; 86:112. DOI: 10.1063/1.1884747
Tuzemen ES, Kara K, Elagoz S, Takci DK, Altuntas I, Esen R. Structural and electrical properties of nitrogen-doped ZnO thin films. Applied Surface Science. 2014; 318:157-163. DOI: 10.1016/j.apsusc.2014.02.118
Di Valentin C, Pacchioni G, Selloni A. Theory of carbon doping of titanium dioxide. Chemistry of Materials. 2005; 17:6656-6665. DOI: 10.1021/cm051921h
Dong F, Guo S, Wang H, Li X, Wu Z. Enhancement of the visible light photocatalytic activity of C-doped TiO2 nanomaterials prepared by a green synthetic approach. The Journal of Physical Chemistry. 2011; 115:13285-13292. DOI: 10.1021/jp111916q
Cong Y, Li X, Qin Y, Dong Z, Yuan G, Cui Z, et al. Carbon-doped TiO2 coating on multiwalled carbon nanotubes with higher visible light photocatalytic activity. Applied Catalysis B: Environmental. 2011; 107:128-134. DOI: 10.1016/j.apcatb.2011.07.005
Gamage McEvoy J, Cui W, Zhang Z. Degradative and disinfective properties of carbon-doped anatase-rutile TiO2 mixtures under visible light irradiation. Catalysis Today. 2013; 207:191-199. DOI: 10.1016/j.cattod.2012.04.015
Rockafellow EM, Stewart LK, Jenks WS. Is sulfur-doped TiO2 an effective visible light photocatalyst for remediation? Applied Catalysis B: Environmental. 2009; 91:554-562. DOI: 10.1016/j.apcatb.2009.06.027
Umebayashi T, Yamaki T, Itoh H, Asai K. Band gap narrowing of titanium dioxide by sulfur doping. Applied Physics Letters. 2002; 454:3-6. DOI: 10.1063/1.1493647
Xu H, Zhou Y-N, Lu F, Fu Z-W. Electrochemistry of ZnO1−xSx thin film with lithium. Journal of the Electrochemical Society. 2011; 158:A285. DOI: 10.1149/1.3532037
Meyer BK, Polity A, Farangis B, He Y, Hasselkamp D, Krämer T, et al. Structural properties and bandgap bowing of thin films deposited by reactive sputtering. Applied Physics Letters. 2004; 4929:2002-2005. DOI: 10.1063/1.1825053
Ratheesh R, Thankalekshmi ACR. Structure and optical band gap of ZnO1-xSx thin films synthesized by chemical spray pyrolysis for application in solar cells. Journal of Applied Physics. 2012; 112:063708. DOI: 10.1063/1.4754014
Patil AB, Patil KR, Pardeshi SK. Ecofriendly synthesis and solar photocatalytic activity of S-doped ZnO. Journal of Hazardous Materials. 2010; 183:315-323. DOI: 10.1016/j.jhazmat.2010.07.026
Zheng YZ, Tao X, Hou Q, Wang DT, Zhou WL, Chen JF. Iodine-doped ZnO nanocrystalline aggregates for improved dye-sensitized solar cells. Chemistry of Materials. 2011; 23:3-5. DOI: 10.1021/cm101525p
Iwase M, Yamada K, Kurisaki T, Prieto-mahaney OO, Ohtani B, Wakita H. Applied catalysis B: Environmental visible-light photocatalysis with phosphorus-doped titanium (IV) oxide particles prepared using a phosphide compound. Applied Catalysis B: Environmental. 2013; 132–133:39-44. DOI: 10.1016/j.apcatb.2012.11.014
Mu X, Hou T, Zhang L, Jiang Y, Guan J, Chen X. Facile synthesis of phosphorus doped graphitic carbon nitride polymers with enhanced visible-light photocatalytic activity. Materials Research Bulletin. 2013; 48:3485-3491. DOI: 10.1016/j.materresbull.2013.05.040
Chai B, Yan J, Wang C, Ren Z, Zhu Y. Enhanced visible light photocatalytic degradation of Rhodamine B over phosphorus doped graphitic carbon nitride. Applied Surface Science. 2017; 391:376-383. DOI: 10.1016/j.apsusc.2016.06.180
Fan Q, Liu J, Yu Y, Zuo S, Li B. A simple fabrication for sulfur doped graphitic carbon nitride porous rods with excellent photocatalytic activity degrading RhB dye. Applied Surface Science. 2017; 391:360-368. DOI: 10.1016/j.apsusc.2016.04.055
Yan SC, Li ZS, Zou ZG. Photodegradation of rhodamine B and methyl Orange over boron-doped g-C3N4 under visible light irradiation. Langmuir. 2010; 26:3894-3901. DOI: 10.1021/la904023j
Dong G, Zhao K, Zhang L. Carbon self-doping induced high electronic conductivity and photoreactivity of g-C3N4. Chemical Communications. 2012; 48:6178-6180. DOI: 10.1039/c2cc32181e
Gole JL, Stout JD, Burda C, Lou Y, Chen X. Highly efficient formation of visible light tunable TiO2-xNx photocatalysts and their transformation at the nanoscale. The Journal of Physical Chemistry. B. 2004; 108:1230-1240
Jiang W, Ullah N, Divitini G, Ducati C, Kumar RV, Ding Y, et al. Vertically oriented TiOxNy nanopillar arrays with embedded Ag nanoparticles for visible-light photocatalysis. Langmuir. 2012; 28:5427-5431. DOI: 10.1021/la203617u
Rhee CH, Bae SW, Lee JS. Template-free hydrothermal synthesis of high surface area nitrogen-doped Titania photocatalyst active under visible light. Chemistry Letters. 2005; 34:660-661. DOI: 10.1246/cl.2005.660
Livraghi S, Pelaez M, Biedrzycki J, Corazzari I, Giamello E, Dionysiou DD. Influence of the chemical synthesis on the physicochemical properties of N-TiO2 nanoparticles. Catalysis Today. 2013; 209:54-59. DOI: 10.1016/j.cattod.2012.12.020
Fang J, Shi F, Bu J, Ding J, Xu S, Bao J, et al. One-step synthesis of bifunctional TiO2 catalysts and their photocatalytic activity. Journal of Physical Chemistry C. 2010; 114:7940-7948
Cong Y, Zhang J, Chen F, Anpo M. Synthesis and characterization of nitrogen-doped TiO2 nanophotocatalyst with high visible light activity. Journal of Physical Chemistry C. 2007; 111:6976-6982. DOI: 10.1021/jp0685030
Lin L, Zheng RY, Xie JL, Zhu YX, Xie YC. Synthesis and characterization of phosphor and nitrogen co-doped titania. Applied Catalysis B: Environmental. 2007; 76:196-202. DOI: 10.1016/j.apcatb.2007.05.023
Li F, Yin X. Investigation on F-B-S tri-doped nano-TiO2 films for the photocatalytic degradation of organic dyes. Journal of Nanoparticle Research. 2011; 13:4839-4846. DOI: 10.1007/s11051-011-0461-5
Zhao W, Ma W, Chen C, Zhao J, Shuai Z. Efficient degradation of toxic organic pollutants with Ni2O3/TiO2-xBx under visible irradiation. Journal of the American Chemical Society. 2004; 126:4782-4783. DOI: 10.1021/ja0396753
Dong F, Zhao W, Wu Z. Characterization and photocatalytic activities of C, N and S co-doped TiO2 with 1D nanostructure prepared by the nano-confinement effect. Nanotechnology. 2008; 19:10. DOI: 10.1088/0957-4484/19/36/365607
Ohno T, Tsubota T, Toyofuku M, Inaba R. Photocatalytic activity of a TiO2 photocatalyst doped with C4+ and S4+ ions having a rutile phase under visible light. 2004; 98:255-258
Hamal DB, Haggstrom JA, Marchin GL, Ikenberry MA, Hohn K, Klabunde KJ. A multifunctional biocide/sporocide and photocatalyst based on titanium dioxide (TiO2) Codoped with silver, carbon, and sulfur. Langmuir. 2010; 26:2805-2810. DOI: 10.1021/la902844r
Pelaez M, Falaras P, Likodimos V, Kontos AG, De AA, Kevin O, et al. Synthesis, structural characterization and evaluation of sol-gel-based NF-TiO2 films with visible light-photoactivation for the removal of microcystin-LR. Applied Catalysis B: Environmental. 2010; 99:378-387. DOI: 10.1016/j.apcatb.2010.06.017
Huang D, Liao S, Liu J, Dang Z, Petrik L. Preparation of visible-light responsive N–F-codoped TiO2 photocatalyst by a sol-gel-solvothermal method. Journal of Photochemistry and Photobiology A: Chemistry. 2006; 184:282-288. DOI: 10.1016/j.jphotochem.2006.04.041
Lv Y, Fu Z, Yang B, Xu J, Wu M, Zhu C, et al. Preparation N–F-codoped TiO2 nanorod array by liquid phase deposition as visible light photocatalyst. Materials Research Bulletin. 2011; 46:361-365. DOI: 10.1016/j.materresbull.2010.12.011
Ao Y, Xu J, Fu D, Yuan C. Synthesis of C, N, S-tridoped mesoporous titania with enhanced visible light-induced photocatalytic activity. Microporous and Mesoporous Materials. 2009; 122:1-6. DOI: 10.1016/j.micromeso.2008.11.010
Wang P, Yap P, Lim T. C-N-S tridoped TiO2 for photocatalytic degradation of tetracycline under visible-light irradiation. Applied Catalysis A: General. 2011; 399:252-261. DOI: 10.1016/j.apcata.2011.04.008
Ohno T, Tsubota T, Nakamura Y, Sayama K. Preparation of S, C cation-codoped SrTiO3 and its photocatalytic activity under visible light. Applied Catalysis A: General. 2005; 288:74-79. DOI: 10.1016/j.apcata.2005.04.035
Zou F, Jiang Z, Qin X, Zhao Y, Jiang L, Zhi J. Template-free synthesis of mesoporous N-doped SrTiO3 perovskite with high visible-light-driven photocatalytic activity. Chemical Communications. 2012; 48:8514-8516. DOI: 10.1039/c2cc33797e
Han P, Su Y, Meng Y, Wang S, Jia Q, Wang X. Preparation and photocatalytic performance of iodine-doped NaTaO3 nanoparticles. Journal of Nanoscience and Nanotechnology. 2011; 11:9600-9606. DOI: 10.1166/jnn.2011.5277
Fu H, Zhang S, Zhang L, Zhu Y. Visible-light-driven NaTaO3-xNx catalyst prepared by a hydrothermal process. Materials Research Bulletin. 2008; 43:864-872. DOI: 10.1016/j.materresbull.2007.05.013
Jiang L, Wang Q, Li C, Yuan J, Shangguan W. ZrW2O8 photocatalyst and its visible-light sensitization via sulfur anion doping for water splitting. International Journal of Hydrogen Energy. 2010; 35:7043-7050. DOI: 10.1016/j.ijhydene.2009.12.187
Zhang J, Huang Z, Xu Y, Kang F. Hydrothermal synthesis of iodine-doped Bi2WO6 nanoplates with enhanced visible and ultraviolet-induced photocatalytic activities. International Journal of Photoenergy. 2012; 2012. DOI: 10.1155/2012/915386
Zhang Z, Wang W, Wang L, Sun S. Enhancement of visible-light photocatalysis by coupling with narrow-band-gap semiconductor: A case study on Bi2S3/Bi2WO6. Applied Materials & Interfaces. 2012; 4:593-597. DOI: 10.1021/am2017199
Shi R, Huang G, Lin J, Zhu Y. Photocatalytic activity enhancement for Bi2WO6 by fluorine substitution. Journal of Physical Chemistry C. 2009; 113:19633-19638
Shifu C, Wei Z, Sujuan Z, Wei L. Preparation, characterization and photocatalytic activity of N-containing ZnO powder. Chemical Engineering Journal. 2009; 148:263-269. DOI: 10.1016/j.cej.2008.08.039
Li X, Pan H, Hu Q, Zhang C. Nitrogen-doped SiO2–HNb3O8 for rhodamine B photodegradation under visible light. Journal of Alloys and Compounds. 2011; 509:6252-6256. DOI: 10.1016/j.jallcom.2011.03.033
Takeuchi M, Shimizu Y, Yamagawa H, Nakamuro T, Anpo M. Preparation of the visible light responsive N3-doped WO3 photocatalyst by a thermal decomposition of ammonium paratungstate. Applied Catalysis B: Environmental. 2011; 110:1-5. DOI: 10.1016/j.apcatb.2011.08.004
Liu Y, Li Y, Li W, Han S, Liu C. Photoelectrochemical properties and photocatalytic activity of nitrogen-doped nanoporous WO3 photoelectrodes under visible light. Applied Surface Science. 2012; 258:5038-5045. DOI: 10.1016/j.apsusc.2012.01.080
Liu S, Yin K, Ren W, Cheng B, Yu J. Tandem photocatalytic oxidation of Rhodamine B over surface fluorinated bismuth vanadate crystals. Journal of Materials Chemistry. 2012; 22:17759-17767. DOI: 10.1039/c2jm33337f
Ji K, Jiang H, Liu Y, Deng J, Dai H, Zhang L. Porous F-doped BiVO4: Synthesis and enhanced photocatalytic performance for the degradation of phenol under visible-light illumination. Solid State Sciences. 2013; 17:2127. DOI: 10.1016/j.solidstatesciences.2012.12.009
Zhao Z, Dai H, Deng J, Liu Y, Au CT. Enhanced visible-light photocatalytic activities of porous olive-shaped sulfur-doped BiVO4-supported cobalt oxides. Solid State Sciences. 2013; 18:98-104. DOI: 10.1016/j.solidstatesciences.2013.01.009
Jia L, Li J, Fang W, Song H, Li Q, Tang Y. Visible-light-induced photocatalyst based on C-doped LaCoO3 synthesized by novel microorganism chelate method. Catalysis Communications. 2009; 10:1230-1234. DOI: 10.1016/j.catcom.2009.01.025
Martha S, Parida KM. Fabrication of nano N-doped In2Ga2ZnO7 for photocatalytic hydrogen production under visible light. International Journal of Hydrogen Energy. 2012; 37:17936-17946. DOI: 10.1016/j.ijhydene.2012.09.025
Gasparotto A, Barreca D, Bekermann D, Devi A, Fischer R a, Fornasiero P, et al. F-doped Co3O4 photocatalysts for sustainable H2 generation from water/ethnol. Journal of the American Chemical Society. 2011; 133:193-625. DOI: 10.1021/ja210078d
Sreethawong T, Ngamsinlapasathian S, Yoshikawa S. Synthesis of crystalline mesoporous-assembled ZrO2 nanoparticles via a facile surfactant-aided sol-gel process and their photocatalytic dye degradation activity. Chemical Engineering Journal. 2013; 228:256-262. DOI: 10.1016/j.cej.2013.04.111
Dolat D, Quici N, Kusiak-nejman E, Morawski AW, Puma GL. Environmental one-step, hydrothermal synthesis of nitrogen, carbon co-doped titanium dioxide (N, C TiO2) photocatalysts. Effect of alcohol degree and chain length as carbon dopant precursors on photocatalytic activity and cata. Applied Catalysis B: Environmental. 2012; 115–116:81-89. DOI: 10.1016/j.apcatb.2011.12.007
Sun H, Bai Y, Cheng Y, Jin W, Xu N. Preparation and characterization of visible-light-driven carbon-sulfur-codoped TiO2 photocatalysts. Industrial and Engineering Chemistry Research. 2006; 45:4971-4976. DOI: 10.1021/ie060350f
Uk H, Chang S, Hae S, Son B, Jae S, Jin H, et al. Highly visible-light active nanoporous TiO2 photocatalysts for efficient solar photocatalytic applications. Applied Catalysis B: Environmental. 2013; 129:106-113. DOI: 10.1016/j.apcatb.2012.09.010
Yang K, Dai Y, Huang B, Whangbo MH. Density functional characterization of the band edges, the band gap states, and the preferred doping sites of halogen-doped TiO2. Chemistry of Materials. 2008; 20:6528-6534. DOI: 10.1021/cm801741m
Zhang L, Zhang H, Xu H, Deng F, Zheng Z. Hierarchical chlorine-doped rutile TiO2 spherical clusters of nanorods: Large-scale synthesis and high photocatalytic activity. Journal of Solid State Chemistry. 2008; 181:2516-2522. DOI: 10.1016/j.jssc.2008.06.019
Luo H, Takata T, Lee Y, Zhao J, Domen K, Yan Y. Photocatalytic activity enhancing for titanium dioxide by Co-doping with bromine and chlorine. Chemistry of Materials. 2004; 16:846-849. DOI: 10.1021/cm035090w
Andersen J, Han C, O’Shea K, Dionysiou DD. Revealing the degradation intermediates and pathways of visible light-induced NF-TiO2 photocatalysis of microcystin-LR. Applied Catalysis B: Environmental. 2014; 154–155:259-266. DOI: 0.1016/j.apcatb.2014.02.025
Nisar J, Wang B, Moyses C, Ferreira A. Band gap engineering by anion doping in the photocatalyst BiTaO4: First principle calculations. International Journal of Hydrogen Energy. 2012; 37:3014-3018. DOI: 10.1016/j.ijhydene.2011.11.068
Yang K, Huang W, Xu L, Luo K, Yang Y, Huang G. Materials science in semiconductor processing insights into enhanced visible-light photocatalytic activity of CeO2 doped with nonmetal impurity from the first principles. Materials Science in Semiconductor Processing. 2016; 41:200-208. DOI: 10.1016/j.mssp.2015.08.039
Bagwasi S, Tian B, Zhang J, Nasir M. Synthesis, characterization and application of bismuth and boron Co-doped TiO2: A visible light active photocatalyst. Chemical Engineering Journal. 2013; 217:108-118. DOI: 10.1016/j.cej.2012.11.080
Di Valentin C, Pacchioni G. Trends in non-metal doping of anatase TiO2: B, C, N and F. Catalysis Today. 2013; 206:12-18. DOI: 10.1016/j.cattod.2011.11.030
Wang G, Chen H, Wu G, Kuang A. Hybrid density functional study on mono- and Co-doped NaNbO3 for visible-light photocatalysis. ChemPhysChem. 2016; 17:489-499. DOI: 10.1002/cphc.201501037
Murakami N, Chiyoya T, Tsubota T, Ohno T. Switching redox site of photocatalytic reaction on titanium(IV) oxide particles modified with transition-metal ion controlled by irradiation wavelength. Applied Catalysis A: General. 2008; 348:148-152. DOI: 10.1016/j.apcata.2008.06.040
Carneiroa JO, Portinha VT, Dupak L, Magalhaes A, Coutinho P. Study of the deposition parameters and Fe-dopant effect in the photocatalytic activity of TiO2 films prepared by dc reactive magnetron sputtering. Vacuum. 2005; 78:37-46. DOI: 10.1016/j.vacuum.2004.12.012
Wu JCS, Chen CH. A visible-light response vanadium-doped titania nanocatalyst by sol-gel method. Journal of Photochemistry and Photobiology A: Chemistry. 2004; 163:509-515. DOI: 10.1016/j.jphotochem.2004.02.007
Rimoldi L, Pargoletti E, Meroni D, Falletta E, Cerrato G, Turco F, et al. Concurrent role of metal (Sn, Zn) and N species in enhancing the photocatalytic activity of TiO2 under solar light. Catalysis Today. 2018; 313:4046. DOI: 10.1016/j.cattod.2017.12.017
Rashid J, Barakat MA, Salah N, Habib SS. Ag/ZnO nanoparticles thin films as visible light photocatalysts. The Royal Society of Chemistry. 2014; 4:56892-56899. DOI: 10.1039/c4ra12990c
Yayapao O, Thongtem T, Phuruangrat A, Thongtem S. Ultrasonic-assisted synthesis of Nd-doped ZnO for photocatalysis. Materials Letters. 2013; 90:83-86. DOI: 10.1016/j.matlet.2012.09.027
Phuruangrat A, Yayapao O, Thongtem T, Thongtem S. Preparation, characterization and photocatalytic properties of Ho doped ZnO nanostructures synthesized by sonochemical method. Superlattices and Microstructures. 2014; 67:118-126. DOI: 10.1016/j.spmi.2013.12.023
Khatamian M, Khandar AA, Divband B, Haghighi M, Ebrahimiasl S. Heterogeneous photocatalytic degradation of 4-nitrophenol in aqueous suspension by Ln (La3+, Nd3+ or Sm3+) doped ZnO nanoparticles. Journal of Molecular Catalysis A: Chemical. 2012; 365:120-127. DOI: 10.1016/j.molcata.2012.08.018
Ding K, Wen L, Xu L, Wu H, Ye Y, Zhang Y. Predicting the electronic and optical properties of IB metals doped monoclinic BiVO4: First principle calculations. International Journal of Quantum Chemistry. 2015; 116:388-395. DOI: 10.1002/qua.25051
Tang JW, Wang DF, Zou ZG, Je Y. Modification of photophysical properties of WO3 by doping different metals. Materials Science Forum. 2003; 425:163-166. DOI: 10.4028/www.scientific.net/MSF.423-425.163
Xue Q, Liu Y, Zhou Q, Utsumi M, Zhang Z, Sugiura N. Photocatalytic degradation of geosmin by Pd nanoparticle modified WO3 catalyst under simulated solar light. Chemical Engineering Journal. 2016; 283:614-621. DOI: 10.1016/j.cej.2015.08.016
Wei W, Ying D, Hao J, Huang B. Density functional characterization of the of Cr-doped SrTiO3. Journal of Physics D: Applied Physics. 2009; 42. DOI: 10.1088/0022-3727/42/5/055401
Liu H, Peng T, Ke D, Peng Z, Yan C. Preparation and photocatalytic activity of dysprosium doped tungsten trioxide nanoparticles. Materials Chemistry and Physics. 2007; 104:377-383. DOI: 10.1016/j.matchemphys.2007.03.028
Li J, Hu W, Zhong J, Zeng J, Huang S, Xiao Z, et al. Photo-induced charge separation and photocatalytic activity of Ga-doped SnO2. Applied Physics A: Materials Science & Processing. 2014; 116:2149-2156. DOI: 10.1007/s00339-014-8428-x
Li Z, Shen Y, Guan Y, Hu Y, Lin Y, Nan CW. Bandgap engineering and enhanced interface coupling of graphene-BiFeO3 nanocomposites as efficient photocatalysts under visible light. Journal of Materials Chemistry A. 2014; 2:1967-1973. DOI: 10.1039/c3ta14269h
Hu S, Li F, Fan Z, Wang F, Zhao Y, Lv Z. Band gap-tunable potassium doped graphitic carbon nitride with enhanced mineralization. Dalton Transactions. 2014; 44:1084-1092. DOI: 10.1039/c4dt02658f
Rong X, Qiu F, Rong J, Zhu X, Yan J, Yang D. Enhanced visible light photocatalytic activity of W-doped porous. Materials Letters. 2016; 164:127-131. DOI: 10.1016/j.matlet.2015.10.131
Wang Y, Li Y, Bai X, Cai Q, Liu C, Zuo Y, et al. Facile synthesis of Y-doped graphitic carbon nitride with enhanced photocatalytic performance. Catalysis Communications. 2016; 84:179-182. DOI: 10.1016/j.catcom.2016.06.020
Song X, Tao H, Chen L, Sun Y. Synthesis of Fe/g-C3N4 composites with improved visible light photocatalytic activity. Materials Letters. 2014; 116:265-267. DOI: 10.1016/j.matlet.2013.11.043
Chatterjee D, Dasgupta S. Visible light induced photocatalytic degradation of organic pollutants. Journal of Photochemistry and Photobiology C: Photochemistry Reviews. 2005; 6:186-205. DOI: 10.1016/j.jphotochemrev.2005.09.001
Abe R, Sayama K, Arakawa H. Dye-sensitized photocatalysts for efficient hydrogen production from aqueous I—Solution under visible light irradiation. Journal of Photochemistry and Photobiology A: Chemistry. 2004; 166:115-122. DOI: 10.1016/j.jphotochem.2004.04.031
Chu W, Chan KH, Jafvert CT, Chan YS. Removal of phenylurea herbicide monuron via riboflavin-mediated photosensitization. Chemosphere. 2007; 69:177-183. DOI: 10.1016/j.chemosphere.2007.04.055
Whitehead K, Hedges JI. Photodegradation and photosensitization of mycosporine-like amino acids. Journal of Photochemistry and Photobiology B: Biology. 2005; 80:115-121. DOI: 10.1016/j.jphotobiol.2005.03.008
Kaur S, Singh V. Visible light induced sonophotocatalytic degradation of reactive red dye 198 using dye sensitized TiO2. Ultrasonics Sonochemistry. 2007; 14:531-537. DOI: 10.1016/j.ultsonch.2006.09.015
Lee C, Hyeon T, Lee H. Visible light-induced degradation of carbon tetrachloride on. Environmental Science & Technology. 2001; 35:966-970
Shim M, Mcdaniel H, Oh N. Prospects for strained type-II nanorod heterostructures. The Journal of Physical Chemistry Letters. 2011; 2:2722-2727
Tian J, Zhenhuan Zhaoa AK, Boughton RI, Liu H. Nanostructured surface heterostructures: A review. Chemical Society Reviews. 2014; 43:6920-6937. DOI: 10.1039/x0xx00000x
Beydoun D, Amal R, Low G. Role of nanoparticles in photocatalysis. Journal of Nanoparticle Research. 1999; 1:439-458. DOI: 10.1023/A:1010044830871
Ghows N, Entezari MH. Fast and easy synthesis of core—Shell nanocrystal (CdS/TiO2) at low temperature by micro-emulsion under ultrasound. Ultrasonics Sonochemistry. 2011; 18:629-634. DOI: 10.1016/j.ultsonch.2010.08.003
Jia H, Xu H, Hu Y, Tang Y, Zhang L. TiO2 @ CdS core—Shell nanorods films: Fabrication and dramatically enhanced photoelectrochemical properties. Electrochemistry Communications. 2007; 9:354-360. DOI: 10.1016/j.elecom.2006.10.010
Covei M, Perniu D, Bogatu C, Duta A. CZTS-TiO2 thin film heterostructures for advanced photocatalytic wastewater treatment. Catalysis Today. 2019; 321–322:172-177. DOI: 10.1016/j.cattod.2017.12.003
Rashid J, Barakat MA, Ruzmanova Y. Fe3O4/SiO2/TiO2 nanoparticles for photocatalytic degradation of 2-chlorophenol in simulated wastewater. Environmental Science and Pollution Research. 2015; 22:3149-3157. DOI: 10.1007/s11356-014-3598-9
Pan L, Shen G, Zhang J, Wei X, Wang L, Zou J, et al. TiO2—ZnO composite sphere decorated with ZnO clusters for E ff ective charge isolation in photocatalysis. Industrial and Engineering Chemistry Research. 2015; 54:7226-7232. DOI: 10.1021/acs.iecr.5b01471
Lee G, Kang M. Physicochemical properties of core/shell structured pyrite FeS2/anatase TiO2 composites and their photocatalytic hydrogen production performances. Current Applied Physics. 2013; 13:1482-1489. DOI: 10.1016/j.cap.2013.05.002
Rashid J, Saleem S, Awan SU, Iqbal A, Kumar R, Barakat MA, et al. Stabilized fabrication of anatase-TiO2/FeS2 (pyrite) semiconductor composite nanocrystals for enhanced solar light-mediated photocatalytic degradation of methylen blue. RSC Advances. 2018; 8:11935-11945. DOI: 10.1039/c8ra02077a
Rashid J, Barakat M. InVO4/TiO2 composite for visible-light photocatalytic degradation of 2-chlorophenol in wastewater. Environmental Technology. 2014; 35:2153-2159. DOI: 10.1080/09593330.2014.895051
Rashid J, Barakat MA. Ag3PO4 Enhanced TiO2 for Visible Light Photocatalysis of 2-Chlorophenol in Wastewater. Institute of Research Engineers and Doctors, USA; 2014. pp. 3-7
Li Y, Zhao H, Yang M. TiO2 nanoparticles supported on PMMA nanofibers for photocatalytic degradation of methyl orange. Journal of Colloid and Interface Science. 2017; 508:500-507. DOI: 10.1016/j.jcis.2017.08.076
Rashid J, Abbas A, Chang LC, Iqbal A, Ihsan-ul-Haq A, Rehman SUA, et al. Butterfly cluster like lamellar BiOBr/TiO2 nanocomposite for enhanced sunlight photocatalytic mineralization of aqueous ciprofloxacin. Science of the Total Environment Elsevier B. 2019; 665:668-677. DOI: 10.1016/j.scitotenv.2019.02.145
Jana TK, Pal A, Chatterjee K. Self assembled flower like CdS–ZnO nanocomposite and its photo catalytic activity. Journal of Alloys and Compounds. 2014; 583:510-515. DOI: 10.1016/j.jallcom.2013.08.184
Cho S, Jang JW, Kim J, Lee JS, Choi W, Lee KH. Three-dimensional type II ZnO/ZnSe heterostructures and their visible light photocatalytic activities. Langmuir. 2011; 27:10243-10250. DOI: 10.1021/la201755w
Wang Z, Huang B, Dai Y, Qin X, Zhang X, Wang P, et al. Highly photocatalytic ZnO/In2O3 heteronanostructures synthesized by a coprecipitation method. The Journal of Physical Chemistry. 2009; 113:4612-4617
Hamrouni A, Moussa N, Di Paola A, Parrino F, Houas A, Palmisano L. Characterization and photoactivity of coupled ZnO-ZnWO4 catalysts prepared by a sol-gel method. Applied Catalysis B: Environmental. 2014; 154–155:379-385. DOI: 10.1016/j.apcatb.2014.02.042
Hernández S, Hidalgo D, Sacco A, Chiodoni A, Lamberti A, Cauda V, et al. Comparison of photocatalytic and transport properties of TiO2 and ZnO nanostructures for solar-driven water splitting. Physical Chemistry Chemical Physics. 2015; 17:7775-7786. DOI: 10.1039/c4cp05857g
Katsumata H, Gomathisankar P, Funasaka K, Kaneco S, Suzuki T, Hachisuka K. Photocatalytic hydrogen production with CuS/ZnO from aqueous Na2S + Na2SO3 solution. International Journal of Hydrogen Energy. 2013; 38:8625-8630. DOI: 10.1016/j.ijhydene.2013.04.131
He Z, Shi Y, Gao C, Wen L, Chen J, Song S. BiOCl/BiVO4 p–n heterojunction with enhanced photocatalytic activity under visible-light irradiation. The Journal of Physical Chemistry. 2014; 118:389-398. DOI: 10.1021/jp409598s
Tahir MB, Nabi G, Rafique M, Khalid NR. Nanostructured-based WO3 photocatalysts: Recent development, activity enhancement, perspectives and applications for wastewater treatment. International journal of Environmental Science and Technology. 2017; 14:2519-2542. DOI: 10.1007/s13762-017-1394-z
Shamaila S, Khan A, Sajjad L, Chen F, Zhang J. WO3/BiOCl, a novel heterojunction as visible light photocatalyst. Journal of Colloid and Interface Science. 2011; 356:465-472. DOI: 10.1016/j.jcis.2011.01.015
Huang T, Lin X, Xing J, Wang W, Shan Z, Huang F. Photocatalytic activities of hetero-junction semiconductors WO3/SrNb2O6. Materials Science & Engineering, B: Solid-State Materials for Advanced Technology. 2007; 141:49-54. DOI: 10.1016/j.mseb.2007.05.007
Zhang J, Yu K, Yu Y, Lou LL, Yang Z, Yang J, et al. Highly effective and stable Ag3PO4/WO3 photocatalysts for visible light degradation of organic dyes. Journal of Molecular Catalysis A: Chemical. 2014; 391:12-18. DOI: 10.1016/j.molcata.2014.04.010
Huang Z, Zou J, Pan L, Wang S, Zhang X, Wang L. Synergetic promotion on photoactivity and stability of W18O49/TiO2 hybrid. Applied Catalysis B: Environmental. 2014; 147:167-174. DOI: 10.1016/j.apcatb.2013.08.038
Aslam I, Cao C, Tanveer M, Farooq MH, Khan SW, Tahir M, et al. A novel Z-scheme WO3/CdWO4 photocatalyst with enhanced visible-light photocatalytic activity for the degradation of organic pollutants. RSC Advances. 2015; 5:6019-6026. DOI: 10.1039/C4RA15847D
Zaleska A, Winiarski M, Klimczuk T, Bajorowicz B, Cybula A. Surface properties and photocatalytic activity of KTaO3, CdS, MoS2 semiconductors and their binary and ternary semiconductor composites. Molecules. 2014; 19:15339-15360. DOI: 10.3390/molecules190915339
Pirhashemi M, Habibi-yangjeh A. Ternary ZnO/AgBr/Ag2CrO4 nanocomposites with tandem n–n heterojunctions as novel visible-light-driven photocatalysts with excellent activity. Ceramics International. 2015; 41:14383-14393. DOI: 10.1016/j.ceramint.2015.07.072
Zhang W, Li Y, Song Q, Zhang J, Chen X, Liu D, et al. Multi-pathway photoelectron migration in globular flower-like In2O3/AgBr/Bi2WO6 synthesized by microwave-assisted method with enhanced photocatalytic activity. Journal of Molecular Catalysis A: Chemical. 2015; 414:27-36. DOI: 10.1016/j.molcata.2015.12.023
Mohamed MM, Ahmed SA, Khairou KS. Unprecedented high photocatalytic activity of nanocrystalline WO3/NiWO4 hetero-junction towards dye degradation: Effect of template and synthesis conditions. Applied Catalysis B: Environmental. 2014; 150–151:63-73. DOI: 10.1016/j.apcatb.2013.12.001
Xu YS, De Zhang W. Monodispersed Ag3PO4 nanocrystals loaded on the surface of spherical Bi2MoO6 with enhanced photocatalytic performance. Dalton Transactions. 2013; 42:1094-1101. DOI: 10.1039/c2dt31634j
Cao J, Luo B, Lin H, Xu B, Chen S. Visible light photocatalytic activity enhancement and mechanism of AgBr/Ag3PO4 hybrids for degradation of methyl orange. Journal of Hazardous Materials. 2012; 217–218:107-115. DOI: 10.1016/j.jhazmat.2012.03.002
Feng Y, Yan X, Liu C, Hong Y, Zhu L, Zhou M, et al. Applied surface science hydrothermal synthesis of CdS/Bi2MoO6 heterojunction photocatalysts with excellent visible-light-driven photocatalytic performance. Applied Surface Science. 2015; 353:87-94. DOI: 10.1016/j.apsusc.2015.06.061
Ghugal SG, Umare SS, Sasikala R. Photocatalytic mineralization of anionic dyes using bismuth doped CdS–Ta2O5 composite. RSC Advances. 2015; 5:63393-63400. DOI: 10.1039/C5RA09974A
Kong L, Jiang Z, Xiao T, Lu L, Jones O, Edwards PP. Exceptional visible-light-driven photocatalytic activity over. Chemical Communications. 2011; 47:5512-5514. DOI: 10.1039/c1cc10446b
Liu C, Li P, Wu G, Luo B, Lin S, Ren A, et al. Enhanced photoelectrochemical and photocatalytic activity by Cu2O/SrTiO3 p–n heterojunction via a facile deposition–precipitation technique. RSC Advances. 2015; 5:33938-33945. DOI: 10.1039/C5RA03086B
Hong E, Kim D, Kim JH. Heterostructured metal sulfide (ZnS-CuS-CdS) photocatalyst for high electron utilization in hydrogen production from solar water splitting. Journal of Industrial and Engineering Chemistry. 2014; 20:3869-3874. DOI: 10.1016/j.jiec.2013.12.092
Moussa N, Houas A, Parrino F, Di Paola A, Hamrouni A, Palmisano L. Photocatalytic activity of binary and ternary SnO2–ZnO–ZnWO4 nanocomposites. Journal of Photochemistry and Photobiology A: Chemistry. 2015; 309:47-54. DOI: 10.1016/j.jphotochem.2015.05.001
Zhao Z, Yanjuan S, Dong F. Graphitic carbon nitride based nanocomposites: A review. Nanoscale. 2015; 7:15-37. DOI: 10.1039/c4nr03008g
Song G, Chu Z, Jin W, Sun H. Enhanced performance of g-C3N4/TiO2 photocatalysts for degradation of organic pollutants under visible light. Chinese Journal of Chemical Engineering. 2015; 23:1326-1334. DOI: 10.1016/j.cjche.2015.05.003
Lv J, Dai K, Zhang J, Geng L, Liang C, Liu Q, et al. Applied surface science facile synthesis of Z-scheme graphitic-C3N4/Bi2MoO6 nanocomposite for enhanced visible photocatalytic properties. Applied Surface Science. 2015; 358:377-384. DOI: 10.1016/j.apsusc.2015.06.183
Dai S, Hua F, Li W, Hou H, Yue J, Feng C. Fabrication of sulfur-doped g-C3N4/Au/CdS Z-scheme photocatalyst to improve the photocatalytic performance under visible light. Applied Catalysis B: Environmental. 2015; 168–169:465-471. DOI: 10.1016/j.apcatb.2015.01.012
Fu J, Chang B, Yanlong Tian FX, Dong X. Novel C3N4-CdS composite photocatalysts with organic-inorganic heterojunctions: In suit synthesis, exceptional activity, high stability and photocatalytic mechanism. Journal of Materials Chemistry A. 2013; 1:3083-3090. DOI: 10.1039/c2ta00672c
Tong Z, Yang D, Shi J, Nan Y, Sun Y, Jiang Z, et al. Three-dimensional porous aerogel constructed by g-C3N4 and graphene oxide nanosheets with excellent visible-light photocatalytic performance. Applied Materials & Interfaces. 2015; 7:25693-25701. DOI: 10.1021/acsami.5b09503
Han Q, Chen N, Zhang J, Qu L. Graphene/graphitic carbon nitride hybrids for catalysis. Materials Horizons. 2017:832-850. DOI: 10.1039/c7mh00379j
Mousavi M, Habibi-Yangjeh A. Integration of NiWO4 and Fe3O4 with graphitic carbon nitride to fabricate novel magnetically recoverable visible-light-driven photocatalysts. Journal of Materials Science. 2018; 53:9046-9063. DOI: 10.1007/s10853-018-2213-8
Zhang S, Li J, Zeng M, Zhao G, Xu J, Hu W, et al. In situ synthesis of water-soluble magnetic graphitic carbon nitride photocatalyst and its synergistic catalytic performance. ACS Applied Materials & Interfaces. 2013; 5:12735-12743
Zou L, Wang H, Yuan G, Wang X. Magnetically separable CdS/ZnFe2O4 composites with highly efficient photocatalytic activity and photostability under visible light. ACS Applied Nano Materials. 2018; 1:831-838. DOI: 10.1021/acsanm.7b00243
Chai B, Liao X, Song F, Zhou H. Fullerene modified C3N4 composites with enhanced photocatalytic activity under visible light irradiation. Dalton Transactions. 2014; 43:982-989. DOI: 10.1039/c3dt52454j
Fu H, Xu T, Zhu S, Zhu Y. Photocorrosion inhibition and enhancement of photocatalytic activity for ZnO via hybridization with C6O. Environmental Science & Technology. 2008; 42:8064-8069. DOI: 10.1021/es801484x
Zhu Y, Bai X, Yao W, Wang L, Wang Y. Enhanced oxidation ability of g-C3N4 photocatalyst via C60 modification. Applied Catalysis B: Environmental. 2014b; 152–153:262-270. DOI: 10.1016/j.apcatb.2014.01.046
Zhu H, Chen D, Yue D. In-situ synthesis of g-C3N4-P25TiO2 composite with enhanced visible light photoactivity. Journal of Nanoparticle Research. 2014; 16:1-10. DOI: 10.1007/s11051-014-2632-7
Huang L, Xu H, Li Y, Li H, Cheng X, Xia J, et al. Visible-light-induced WO3/g-C3N4 composites with enhanced photocatalytic activity. Dalton Transactions. 2013; 4:8606-8616. DOI: 10.1039/c3dt00115f
Tian N, Huang H, Zhang Y. Mixed-calcination synthesis of CdWO4/g-C3N4 heterojunction with enhanced visible-light-driven photocatalytic activity. Applied Surface Science. 2015; 358:343-349. DOI: 10.1016/j.apsusc.2015.07.154
Xing C, Wu Z, Jiang D, Chen M. Hydrothermal synthesis of In2S3/g-C3N4 heterojunctions with enhanced photocatalytic activity. Journal of Colloid and Interface Science. 2014; 433:9-15. DOI: 10.1016/j.jcis.2014.07.015
Liu Q, Fan C, Tang H, Sun X, Yang J, Cheng X. One-pot synthesis of g-C3N4/V2O5 composites for visible light-driven photocatalytic activity. Applied Surface Science. 2015; 358:188-195. DOI: 10.1016/j.apsusc.2015.09.010
Sun JX, Yuan YP, Qiu LG, Jiang X, Xie AJ, Shen YH, et al. Fabrication of composite photocatalyst g-C3N4-ZnO and enhancement of photocatalytic activity under visible light. Dalton Transactions. 2012; 41:6756-6763. DOI: 10.1039/c2dt12474b
Wang Y, Wang Z, Muhammad S, He J. Graphite-like C3N4 hybridized ZnWO4 nanorods: Synthesis and its enhanced photocatalysis in visible light. CrystEngComm. 2012; 14:5065-5070. DOI: 10.1039/c2ce25517k
Yuan D, Huang L, Li Y, Xu Y, Xu H, Huang S, et al. Synthesis and photocatalytic activity of g-C3N4/BiOI/BiOBr ternary composites. RSC Advances. 2016; 6:41204-41213. DOI: 10.1039/C6RA05565F
Dong Z, Wu Y, Thirugnanam N, Li G. Applied surface science double Z-scheme ZnO/ZnS/g-C3N4 ternary structure for efficient photocatalytic H2 production. Applied Surface Science. 2018; 430:293-300. DOI: 10.1016/j.apsusc.2017.07.186
Gao Y, Lin J, Zhang Q, Yu H, Ding F, Xu B, et al. Facile synthesis of heterostructured YVO4/g-C3N4/Ag photocatalysts with enhanced visible-light photocatalytic performance. Applied Catalysis B: Environmental. 2018; 224:586-593. DOI: 10.1016/j.apcatb.2017.11.003
Zhong Y, Yuan J, Wen J, Li X, Xu Y, Liu W, et al. Earth-abundant NiS co-catalyst modified metal-free mpg-C3N4/CNT nanocomposites for highly efficient visible-light photocatalytic H2 evolution. Dalton Transactions. 2015; 44:18260-18269. DOI: 10.1039/c5dt02693h
Yan J, Song Z, Wang X, Xu Y, Pu W, Xu H, et al. Enhanced photocatalytic activity of ternary Ag3PO4/GO/g-C3N4 photocatalysts for rhodamine B degradation under visible light radiation. Applied Surface Science. 2019; 466:70-77. DOI: 10.1016/j.apsusc.2018.09.234
Zhou Y, Li J, Liu C, Huo P, Wang H. Construction of 3D porous g-C3N4/AgBr/rGO composite for excellent visible light photocatalytic activity. Applied Surface Science. 2018; 458:586-596. DOI: 10.1016/j.apsusc.2018.07.121
Jiang D, Yu H, Yu H. Modified g-C3N4/TiO2 nanosheets/ZnO ternary facet coupled heterojunction for photocatalytic degradation of p-toluenesulfonic acid (p-TSA) under visible light. Physica E: Low-dimensional Systems and Nanostructures. 2017; 85:1-6. DOI: 10.1016/j.physe.2016.08.014
Yuan Y, Huang G, Hu W, Xiong D, Zhou B, Chang S. Construction of g-C3N4/CeO2/ZnO ternary photocatalysts with enhanced photocatalytic performance. Journal of Physics and Chemistry of Solids. 2017; 106:1-9. DOI: 10.1016/j.jpcs.2017.02.015
Deng Y, Wang J, Liu Y, Wang J, Feng H, Tang L, et al. Enhanced photocatalytic activity of ternary Ag/g-C3N4/NaTaO3 photocatalysts under wide spectrum light radiation: The high potential band protection mechanism. Applied Catalysis B: Environmental. 2018; 230:102-114. DOI: 10.1016/j.apcatb.2018.02.031