Jai
Prakash
*a,
Pragati
Kumar
b,
Nupur
Saxena
c,
Zonghua
Pu
d,
Zhangsen
Chen
d,
Ankit
Tyagi
e,
Gaixia
Zhang
f and
Shuhui
Sun
*d
aDepartment of Chemistry, National Institute of Technology Hamirpur, Hamirpur-177005, India. E-mail: jaip@nith.ac.in
bNano-Materials and Device Lab, Department of Nano Sciences & Materials, Central University of Jammu, Rahya-Suchani, Samba, Jammu, 181143, India
cDepartment of Physics, Indian Institute of Technology Jammu, 181221, India
dInstitut National de la Recherche Scientifique (INRS), Centre Énergie Matériaux Télécommunications, Varennes, Québec, J3X 1P7, Canada. E-mail: shuhui.sun@inrs.ca
eDepartment of Chemical Engineering, Indian Institute of Technology Jammu, 181221, India
fDepartment of Electrical Engineering, École de Technologie Supérieure (ÉTS), Montreal, QC H3C 1K3, Canada
First published on 18th April 2023
Semiconductor photocatalyst nanomaterials have been extensively studied for the last few decades due to their great potential in solving energy and environmental problems on the earth by harnessing solar light. Cadmium sulfide (CdS) based nanomaterials have emerged as promising photocatalyst materials due to their visible light absorption and physio-chemical properties suitable for high-performance photocatalytic activities in terms of solar-fuel generation and environmental/water remediation. CdS photocatalysts have been reported in several morphologies from 0-dimensional to 3-dimensional (0-3D) nano/micro-architectures. However, regarding CdS photocatalysts with specific nanostructures, 3D nanostructures (nanoflowers, self-assembled -hierarchical, hollow, tetrapod, etc.) have shown special structural features with high surface/volume ratio and significant improvement in their photocatalytic properties for various energy and environment applications. This review deals with CdS-based 3D nano/micro-architectures (sole CdS and nanocomposites with various functional nanomaterials), their formation mechanism and tailoring of properties for visible light induced photocatalytic activities in energy and environmental applications. Particularly, it includes the emerging applications of 3D CdS-based photocatalysts in photocatalytic H2 production, photocatalytic CO2 reduction and photodegradation of organic pollutants with an emphasis on the mechanism as well as the role of functional nanomaterials in boosting photocatalytic activities of CdS. Moreover, various challenges and future prospects in the research of CdS-based photocatalysts have also been discussed.
It has been reported that its properties can be improved in order to enhance its photocatalytic properties by engineering its shape/size and forming hybrid nanocomposite structures with other functional nanomaterials.26–31 Various functional nanomaterials such as noble metals/plasmonics,32–36 semiconductors,37–41 carbon-based materials (graphene, graphene oxides, carbon nanotubes, etc.)20,42–45 have great potential to improve the photocatalytic activity of CdS and other semiconductors. For example, Li et al.31 proposed a CdS/graphene nanocomposite to overcome these problems by first increasing the number of adsorption sites for sacrificial reagents, resulting in more consumption of holes instead of oxidizing CdS itself. Secondly, reduces the bulk recombination of photogenerated e− and h+ pairs resulting in a greater improvement in the photoactivity of CdS/graphene nanocomposite. Various synthesis techniques such as chemical, physical and green synthesis methods have been found to be useful for tailoring the properties of nanostructured materials46–54 and have been used to modify CdS-based nanomaterials in order to enhance their photocatalytic activities.55–60
In the case of nanomaterials, it has been found that the size and shape of nanostructures show great influence on their physical/chemical properties and further on their functionality.62 CdS nanomaterials have been reported in different structures, i.e. 0 to 3 dimensions (0-3D) with some different properties/functionality originating from their geometries8,9,63–68 as shown in Fig. 1a. These different forms of CdS nanostructures have extensively been studied and applied in various fields of energy and environment particularly because of their excellent solar-driven photo activities. All the forms of CdS have unique properties because of their morphologies that contribute to their functionality.7,40,50,69 Especially, 3D nanostructures provide a high surface-to-volume ratio, which promotes better surface activities for functional applications.40,69 For example, 3D CdS nanostructures have been shown to have great potential in photocatalytic applications in the field of energy and environment. Hence, morphology is an important parameter that influences photocatalytic activity. However, the fabrication of such nanostructures or hybrid nanostructures with complex morphology is very difficult as they require high preparation skills.64,70 There have been several studies reporting on the reduced band gap up to 2.25 eV and improved photocatalytic activities by tailoring the shapes/morphologies of the 3D CdS nanostructures using the hydrothermal method.63,65,71 Recently, Shenoy et al.69 studied the comparative photocatalytic functionalities of different morphologies i.e. 1D, 2D and 3D of CdS nanostructures in view of their energy and environmental applications. They studied the photodegradation of erioglaucine and photocatalytic hydrogen evolution using those 1-3D CdS nanostructures under visible light. It was found that out of all these nanostructures, 3D CdS morphology showed better photocatalytic activities as compared to other morphologies along with good photo corrosion stability. Even enhanced photo functional applications have been reported by hybrid CdS 3D nanostructures.72 For example, Wang et al.70 fabricated hierarchical flower-like Au@CdS-CdS nanoparticles composed of a core of Au, a shell of CdS, and CdS nanorod structures. These multi-structured CdS-based nanoflowers exhibited absorption within the whole range of UV-visible region up to 850 nm and the highest photocatalytic degradation as well as photocatalytic hydrogen production under visible light as compared to the sole CdS or Au@CdS 3D nanostructures.
Fig. 1 Schematic diagram of (a) various dimensions of CdS nanostructures and the unit cell of the CdS crystal structure with (b and c) wurtzite (hcp), and zinc blend (ccp) phases. Reprinted with permission from ref. 61. |
In this way, extensive research has been conducted in the past decades for the degradation of harmful/toxic organic pollutants and the generation of hydrogen via photocatalytic water splitting. This could be possible through the rational design, development and tailoring of efficient semiconductor nanomaterials for the next generation of high-performance photocatalysts. These provide a promising way to produce clean energy and to solve the various environmental issues related to air/water pollution as well as global warming.69,73 This review deals with the rational design and development of CdS-based 3D nano-architectures through tailoring and nanocomposites formation with various functional nanomaterials for visible light-induced photocatalytic activities in degradation of emerging organic pollutants with an emphasis on the mechanism and role of functional nanomaterials in boosting its photocatalytic activities. Moreover, emerging applications of 3D CdS-based photocatalysts in photocatalytic H2 production and photocatalytic CO2 reduction have also been reported followed by challenges and future prospects in research of CdS-based photocatalysts in brief.
The bulk bandgap (∼2.4 eV at room temperature) of CdS is well lying in the visible region of the electromagnetic spectrum and allows marvelous applications in vast areas including solar cells, LEDs, lasers, photodetectors, photocatalysis, temperature sensors, biosensors, gas sensor, environmental monitoring, and chemical sensors, etc.61,81–88 In the band structure of CdS, S 3p orbitals contribute to the top of the valence band (VB), while Cd 5s and 5p orbitals contribute to the bottom of the conduction band (CB). The lower position of CB is dominated by Cd 3d orbitals. In particular, photocatalytic technology required the excitation of the photogenerated charge carriers by absorbing light photons, bulk diffusion and surface reaction of photogenerated electrons.61 Thus, the position of CB and VB with respect to redox potential is very important to utilize the extended part of solar radiation for the splitting of a large amount of H2, i.e., efficient photocatalysis. Among various semiconductors, VB and CB levels of CdS are closest to the O2/H2O redox couple (1.23 V vs. normal hydrogen electrode (NHE), pH = 0) and H+/H2 redox couple (0 V vs. NHE, pH = 0).89 In addition, CdS can mobile photogenerated electrons and holes efficiently and timely due to its good carrier transportation ability that increases the carriers' life and leads to high photocatalytic activity.61 Moreover, heat treatment can assist the formation of functional interfaces between CdS and other co-catalysts easily. These functional interfaces are the major decisive asset for photocatalytic property and its application in water splitting.89
Fig. 2 Schematic diagram of formation mechanisms for flower-like, porous flower-like, belt-like and net-like CdS. Reprinted with permission from ref. 92. |
Fig. 3 Change in the morphology of CdS as a function of (a) DETA/DIW ratio. Reprinted with permission from ref. 93 and (b) various reaction parameters. Reprinted with permission from ref. 63. TEM images of CdS NFs with different reaction times: (c) 5 min, (d) 10 min, (e) 30 min at a reaction temperature of 40 °C and (f) growth process. Reprinted with permission from ref. 23. |
A detailed systematic investigation of the processing parameters like growth temperature and time, Cd/S molar ratio, the concentration of capping molecules like thiourea and hexamethylenetetramine (HMT) that influence the shape of 3D nanostructures (NSs) during hydrothermal synthesis was carried out by Chen et al.63 The influence of said processing parameters on the shape of 3D NSs is illustrated in Fig. 3b which describes the mechanism for the formation of 3D CdS NSs.63 The influence of the concentration of complexing agents like ethylenediamine (EDA) along with time and concentration of surfactant (sodium dodecyl benzene sulfonate: SDBS) on 3D CdS NSs was investigated by Yang et al.71 They optimized the concentrations of EDA, SDBS, and time as 0.009 mol, 0.01 g ml−1 and 5 h respectively for the growth of quality CdS NFs cubic phase and found that the photocatalytic degradation of MB was shown better in the case of NFs morphology as compared to CdS NPs.
Doping of CdS nanostructures, reaction temperature and time are other important parameters that affect the morphology of the various nanostructures forming 3D CdS NFs.94,95 For example, the morphology of hydrothermally synthesized CdS NSs at 150 °C for 2 h was found to be changed from nano-flakes to fine NFs by varying the concentration of dopant (Mn).94 It was found that the doping induced a decrease in crystalline size resulting in a high surface area, lower band gap and recombination rate of photogenerated charge carriers. All these contributed to the unprecedented photocatalytic activity for the decomposition of MB and methyl violet (MV) dyes. The effect of reaction time on the morphology and other properties including photocatalysis of hydrothermally grown PVP-capped CdS was investigated. It was observed that the morphology of PVP-capped CdS NSs changes from the spherical-like nanograins to NFs (3 h) to sword-like branched NFs with varying reaction temperatures from 1 h to 5 h at 200 °C. The sword-like branched NFs growth starts beyond the reaction time of 3 h due to the initiation of secondary nucleation.95 Thin films of CdS NFs were also deposited using chemical bath deposition (CBD) at the reaction temperature of 80 °C for 1 h90 and at 60 °C for 3–12 h followed by annealing at 300 °C for 2 h.96 Further, these CdS NFs thin films were applied as photoanode for water splitting and high as well as stable current density with enhanced efficiencies were achieved.96 Besides, the physical vapor deposition (PVD) method was also used to grow CdS microstructures (rose-flower) at an elevated temperature of 800 °C for 1 h.97
A facile colloidal chemical method with the aid of cetyltrimethyl ammonium bromide (CTAB) has also been used to fabricate uniform 3D porous CdS NFs. In this study, the effect of reaction time keeping other parameters fixed was examined to insight into the understanding of the mechanism for the evolution process of the CdS NFs. The overall reaction was carried out at a low reaction temperature of 40 °C and the morphology evolution process was analyzed via TEM images as shown in Fig. 3c–e. It was concluded that nanocrystals were assembled leading to the formation of NFs in intermediate states as schematically shown in Fig. 3f. However, at elevated reaction temperature (90 °C), the reaction rate was so fast and NFs were formed within 10 s.23
In most of the studies, the 3D CdS hollow spherical structures are limited to mesoscale hollow/nano/micro spheres with diameters typically exceeding 100 nm.100 For example, Wang et al.101 synthesized 3D nanostructured CdS nanocrystals with mesospheres (MSPs) morphology on large scale. These hydrothermally synthesized 3D structures were composed of radially arranged nanorods from the center of CdS mesospheres and various reaction conditions were studied for morphological formulation and its mechanism. CdS MSPs were obtained at 200 °C for varying times, i.e. 12, 24, and 40 h, without using any surfactants and it was found that prolonging of reaction time induces larger crystal size. A surfactant and template free synthesis of CdS microspheres was reported using solvothermal process where 4,4′-dipyridyldisulfide (DPDS = (C5H4N)2S2) was used as a temperature controlled in situ source to provide S2− ions at 120–140 °C for 12 h.102 It was observed that the increase in the size of microspheres was temperature dependent. CdS microspheres with spherical morphology sizes ranging from 0.5 to 2 μm were obtained. The morphological analysis exhibited that the microspheres were composed of assembled CdS NCs of ultrasmall (2–5 nm) size (Fig. 4a–c). The formation mechanism was explained on the basis of the breaking of the S–S bond of DPDS at ≥120 °C with the generation of S2− ions followed by a reaction with Cd2+ ions to form CdS NCs. Subsequently, the self-aggregation of these NCs forms CdS microspheres (Fig. 4d).102 These microspheres were found to be excellent visible light active photocatalysts against the degradation of MB molecules. Further, they studied the Zn-doped CdS microspheres with tunable band structures for efficient water splitting and reduction of the aromatic compound for water applications.103 Similarly, mesoporous CdS microspheres of sizes more than 1 μm were fabricated by Patel et al.104 with pronounced photocatalytic activity against the photodegradation of rhodamine B (RhB).
Fig. 4 FESEM images of a CdS microsphere, with (a) and without (b, c) capping agent, (c) shows the presence of nanocrystals (d) the formation mechanism of CdS microspheres. Reprinted with permission from ref. 102 (e) SEM and (f) TEM micrographs of hollow CdS microspheres structures with (g) the formation mechanism of CdS hollow microspheres. Reprinted with permission from ref. 105. |
Han et al.106 synthesized CdS nanospheres (NSPs) using the hydrothermal method by varying the molar concentration ratio of precursors at 200 °C for 5 h. They proposed that the CS bond broken by the attack of the strong nucleophilic O atoms of H2O molecules releases S2− anions slowly that reacted with Cd2+ ions and formed CdS NCs due to constrained growth of nuclei in the presence of an excess of thiourea. Further, the self-assembly of individual NCs occurred to form NSPs. Whereas, the shape of CdS NCs was tuned from NRs to NSPs by manipulating the addition rate of the sulfide precursor and was stabilized via tetraethyl ammonium bromide (TOAB) ligand in a non-aqueous medium. The observations revealed the growth mechanism follows the effective monomer concentration model, where the shape evolution was explained by manipulating the free energy of the crystallographic faces of the nuclei formed. CdS NSPs were also grown at room temperature using a simple and fast sonochemical method with different molar ratios of Cd and S in starting solutions of surfactant EG and CTAB. They believed that the radical species obtained from the solvent EG and the acidity of the solution formed CdS. Further, the observed reduction in NSPs size with an increase in S content in the starting solution was explained by considering the fact that the increased concentration of S, speeded up the releasing of sulfite ions from the CTAB micelles and limited the particle growth and vice versa.107 The surfactant-free CdS NSPs were synthesized by a single-step chemical method where the uniformity in shape was controlled via variation in thioacetamide concentration (C2H5NS-TAA). They observed that smooth NSPs formed if the mole concentration of TAA is equal to the mole concentration of Cd(NO3)2 while transforming into uniform mesoporous NSPs occurred at slightly higher concentration of TAA due to liberation of the H2S gas bubbles during the decomposition of TAA that evolved the reactions as the soft template driven by the minimization of interfacial energy tends to aggregation of NPs. Further, an increase in the mole concentration of TAA tends to agglomerate the spheres with each other and regrowth the NSPs on the surfaces of pre-growth NSPs.108
On the other hand, biomolecule (soulcarboxymthyi chitosan) assisted CdS hollow spheres (HSPs) were synthesized solvothermal at 140 °C for 24 h as shown in Fig. 4e and f.105 Here, the supersaturated solution under alkaline conditions formed CdS NPs nucleate that aggregated into round spheres owing the minimization of the interfacial energy with the assistance of soulcarboxymthyi chitosan. The formed [Cd(NH3)4]2+ complex due to the presence of ammonia in the reaction reacted with S2− under the hydrothermal conditions to form CdS. Subsequently, the dissolution of CdS by NH3 to form [Cd(NH3)4]2+ and the re-precipitation of CdS from the solution simultaneously occur as illustrated by the reactions (Fig. 4g). As the reaction progresses the CdS NPs grew bigger at the surface with the continuous evacuation of the smaller core particles during the dissolution–reprecipitation process which resulted in inner cavities eventually and thus HSPs were formed.105 Similarly, Wang et al.109 demonstrated the formation of CdS hollow microspheres (HMSPs) of size about 5 μm with a diameter of the center hole of about 500 nm using oxalic acid as an auxiliary agent by solvothermal method. They investigated the effect of various parameters such as reaction time (12 h to 24 h), temperature (100–120 °C), and concentration of synthetic auxiliary agent and sodium precursor on growth of high quality CdS HMSPs. It was found that reaction time played an important role in growth of 3D CdS HMSPs (Fig. 5a–d) which exhibited a band gap of 2.31 eV and better absorption in visible light. It was also considered that the S source was the key parameter for the internal structure and mass transport control during the growth mechanism as shown in Fig. 5e. Under high reaction temperature, Cd2+ and H2S formed CdS nanosheets quickly that nucleated rapidly into primary NCs, which grew and self-assembled through random aggregation into small unstable spheres due to a high degree of energy. Thus the excess energy released through the hole formation along the c-axis in each hexagonal CdS sphere and resulted in HMSPs.109
Fig. 5 The FESEM images of CdS at different reaction times. (a) 8 h, (b) 12 h, (c) 24 h, (d) 36 h. (e) Growth mechanism of hollow microsphere CdS structures. Reprinted with permission from ref. 109. |
Fig. 6 (a–d) 3D CdS hierarchical nanostructures i.e. water lily, nanorices, nanofans and porous microparticles under different experimental conditions. Schematic representation of the formation of CdS dendrites. Reprinted with permission from ref. 112. (e) Schematic of mechanism of growth of 3D CdS hierarchical nanoflower. Reprinted with permission from ref. 113. Formation of CdS dendrites nanostructures: SEM images of samples prepared at different temperatures: (f) 120, (g) 150, (h) 180, and (i) 220 °C. Reprinted with permission from ref. 114. (j) Schematic of mechanism for the growth of hierarchical CdS dendrites115 (k and l) Zn-doped dendritic-like CdS structures (k) Zn-doped lower concentration and (l) higher concentration. Reprinted with permission from ref. 116. |
Similarly, Pandit et al.113 proposed another hydrothermally assisted method for synthesizing hierarchical 3D CdS nanoflowers using Lawesson's reagent (LR) as illustrated in Fig. 6e. First, the decomposition of LR in chloroform occurs due to a reaction with cadmium nitrate (aqueous) and forms a monomer that forms a complex with cadmium. Further, this complex decomposed hydrothermally and results in tiny nuclei of CdS (Fig. 6e(A)) that grows with time. Under, prolonged hydrothermal reaction time, nuclei constructs CdS NPs followed by the growth of anisotropic CdS NSs (thin nanopetals) (Fig. 6e(B and C)) due to aggregation of NPs and finally 3D hierarchical flower-like nanostructures (Fig. 6e(D)) were constructed owing the self-assembly of nanopetals were formed. A 3D CdS hierarchical microtremella morphology was fabricated by Dai et al.117 The solvothermal method with the assistance of EDA was used to fabricate MT at 60 °C for 12 h. The growth mechanism of the MT structure was described as the dissolution of thiourea in the water releasing S2− ions slowly due to broken CS chemical bonds. However due to the excess concentration of Cd2+ ions compared to the concentration of S2− ions, a fraction of Cd2+ ions form coordination complexes to react with EDA and restricted the growth of generated CdS NCs largely. Subsequently, NCs gradually aggregated to acquire the shape of minimum surface energy and resulting in the formation of MT. While 3D branched (hierarchical) CdS NS arrays were synthesized through the combination of electro-deposition and subsequent solvothermal methods reaction using EDA as the solvent, thiourea sulfur source, and hexamethylenetetramine (HMTA) as capping agent. The examination of various factors influencing the morphology indicated that the addition of HMTA (≥160 °C) only results in the formation of a branched structure each branch consists of ten thousand of NWs growing preferentially along [0001] direction via EDA and HMTA co-assisted gradual crystallization and subsequent self-assembling process and degree on ordering aspect ratio of NWs depends on the concentration of HMTA. In addition, the concentration of sulfur source, temperature, and time are also critical parameters that controlled the aspect ratio of branched NWs.118
Interestingly, hierarchical CdS dendrites were demonstrated by Yu et al.114 following the same synthesis strategies but varying the reaction temperature and time. It was observed that dendrites were formed at a certain reaction temperature (≥150 °C) for time (∼24 h) and a raise in temperature (180 °C) transformed hyperbranched dendrites into shorter branched dendrites. Further, an increase in temperature (220 °C) resulted in the formation of nanorod-branched dendrites (Fig. 6f–i). These CdS hierarchical nanostructures exhibited excellent photocatalytic activities by degrading eosin red nearly completely (over 95%) after visible light irradiation of 100 min. A slightly different influence on the morphology of CdS dendrites nanostructure was reported by Jamble et al.115 as a result by varying the temperature where dendrites were grown at 160 °C and increasing temperature led to the overall growth, density uniformity, yield, and crystallinity of dendrites at 180 °C and then the fragmentation of dendrites into small parts occurred at 200 °C. However, in both cases, as discussed above, a similar mechanism was proposed for the growth of hierarchical CdS dendrites as demonstrated in Fig. 6j. It was proposed that due to the dual role of thiourea as a sulfur source and bidentate ligand, Cd-thiourea stable system was formed first that weakened with raise in temperature and gradually released Cd2+ ions. Meanwhile, nucleophilic O atoms from H2O molecules attack thiourea, leading to the weakening of the CS bonds and subsequently releasing S2− anions. These S2− then reacted with Cd2+ to produce CdS nuclei, which were further grown preferentially to form rod-like CdS nanostructures. Afterward, the secondary branches turned off aligning mutually parallel along the central trunk and growing further along the secondary branches. Finally, anisotropic growth led to the formation of dendritic structures (Fig. 6j). It was demonstrated that the photocatalytic activities of CdS dendrites as synthesized were found to be enhanced with changes in the morphologies with respect to the increase in temperature. An excellent photocatalytic performance was observed by the dendrites obtained at 200 °C attributed to the greater surface area led to the enhanced adsorption property. Similar 3D CdS crystals with dendrites nanostructures were fabricated by Qui et al.119via an amino acid mediated hydrothermal process where various amino acids were used as capping agents. It was suggested that the growth mechanism of structures required a kinetic growth regime (elevated temperature), whereas thermodynamic control (slow growth at low temperature) was essential for growth of isotropic (aspect ratio) structures. The resulting morphologies exhibited tunability in their optical properties which could be used as ideal building blocks for optoelectronic devices and most importantly as a photocatalyzer attributed to the mixed features of micro and nano-sized crystals. The influence of Zn ions incorporation in growth of dendrite like 3D CdS structure via hydrothermal was investigated by Yang et al.116 It was found that low Zn2+ doping concentration resulted in dendritic-like CdS structures while higher concentrated provided flower-like structures (Fig. 6k and l). These tunability in the morphology improved the photo absorption capability of the overall optical properties with excellent photocatalytic activity.
Fig. 7 (a) TEM and (b) HRTEM images of 3D CdS nanotetrapod. Reprinted with permission from ref. 128. (c) Schematic illustrations showing the formation mechanism of different morphologies of Cd0.9Zn0.1S nanostructures at different temperatures. (d) Mechanism for photogenerated charge separation as well as the redox reaction around the WZ-ZB homojunction. Reprinted with permission from ref. 129. (e) Schematic illustration of the formation process of CdS nanostructures. Reprinted with permission from ref. 130. |
Several groups have been working on the synthesis of such tetrapod nanostructures and the tailoring of their properties. For example, Chu et al.128 studied the growth of such 3D CdS tetrapod nanostructures as shown in Fig. 7a and b. It was proposed that the lattice space match and the location match of ions at the interface of the zinc blende (ZB) core and the wurtzite (WZ) arms in the tetrapod structure were responsible and main structural factors for such anisotropic 3D growth. It was also proposed that by mixing the different proportions of the solvents such as ethylenediamine (EDA) and ethylene glycol (EG), wurtzite or zinc blende CdS rich nanostructures could be formed under the solvothermal conditions. Similarly, the influence of reaction temperature and time on the growth of Cd0.9Zn0.1S nanotetrapods via solvothermal using EDA as both solvent and capping agent was studied.129 The growth mechanism was explained on the basis of the formation of ZB-structured seeds attributed to the temperature-induced nucleation followed by preferential growth of the WZ phase arms (Fig. 7c). It was proposed that the nucleation temperature was the main factor determining the formation of ZB or WZ through nucleation whereas, the monomer deposition and surface diffusion determined the final shape of nanostructures. Furthermore, it was concluded that a relatively low reaction temperature favored the ZB tetrahedral nucleation and subsequent growth initiated via growth monomers depositing (Vdeposition) at one of the ZB-(111) facets of the tetrahedron seed with restricting their diffusion. The growth thus assisted along one direction only led to the formation of nanorods (Fig. 7c, situation 1). At moderate temperature, surface diffusion (Vdiffusion) is initiated, leading to access to other ZB-(111) facets by adsorbed monomers and formed multipods along with nanorods (Fig. 7c, situation 2). The diffusion effect dominated at the elevated reaction temperature, and eventually promoted the formation of tetrapod nanostructures (Fig. 7c, situation 3). In contrast, at a temperature high enough, the nucleation mode switched from ZB tetrahedron to WZ hexagonal plate and growth started at one of the WZ-(0001) facets leading to the formation of WZ nanorods (Fig. 7c, situation 4). A similar argument could be applied to the intermediate case, where only a portion of the nuclei take the WZ hexagonal shape and the resultant product lay between situations 3 and 4. The photocatalytic studies showed that such nanotetrapods exhibited superior photocatalytic hydrogen production due to their high crystallinity and an atomically well-matched phase junction conveniently generated the ZB core and WZ arms (Fig. 7d).129 Here, it is important to mention that temperature plays an important role in determining the stages of formation of tetrapod structures along with the crystal structure. It also provides the formation mechanism of the tetrapod providing the stepwise information during the synthesis of such tetrapod nanostructures.
Interestingly, 3D hierarchical CdS nanotetrapods with tunable optical properties by controlling the length and diameter of the arms of the tetrapod were proposed by Wang et al.130 It was observed that the arm diameter of CdS multipods could be tuned (from 10 to 60 nm) by increasing the S concentration and length could be controlled by varying the reaction time as shown in Fig. 7e. Similarly, Yu et al.131 also synthesized multi-armed CdS tetrapods and observed excellent photocatalytic H2-production activity under visible light with Pt as a co-catalyst attributed to the synergistic effects of several factors including hexagonal phase structure, high surface area, great pore volume and good crystallization. The tetrapods were found to be photostable and no photocorrosion was observed after photocatalytic recycling. It has been found that the shape and composition controlled synthesis of such nanostructures provides better control over the physiochemical properties. Similarly, Vaneski et al.132 demonstrated room temperature aqueous synthesis of CdS tetrapod nanostructures in H2O/EDA mixtures and tested the effect of the addition of common ligands like mercaptopropionic acid (MPA), thioglycolic acid (TGA), and cysteine for their ability to stabilize the colloidal CdS tetrapod nanostructures. It was noticed that the reaction was completed within 3 days without any significant difference in arm length of the tetrapod nanostructures on the addition of ligands. This simple method offered advantages for the subsequent direct use of aqueous-based colloidal CdS nanostructures for photocatalytic hydrogen generation from water avoiding any additional phase transfer.
In summary, growth of CdS tetrapod structures by hydrothermal/solvothermal process is preferably initiated when seed nuclei are in cubic phase and anisotropic growth of hexagonal braches occurs at elevated temperature (usually ≥160 °C). The Cd/S molar ratio plays a critical role for different morphologies and tetrapod structures result when this ratio becomes smaller (nearly 0.6≤). The length of the arms of tetrapod can be controlled by precursors' molarities, for a constant molar ratio, higher the molarities longer the arms. Additionally, the arm length also depends on the reaction time, larger the processing time longer the arm length and lesser the arm diameter, however reaction time do not affect morphology significantly. Besides, the length of tetrapod arms also depends on type of sulphureous precursor.
Fig. 8 Schematic illustration of (a) the major steps involved in the growth process and (b) the formation of a CdS nanocone, a CdS nanofrustum, and a CdS nanoplate, simply controlled by adjusting Cd2+ injection rate. Reprinted with permission from ref. 133. (c) Mechanism of the reaction in the formation of popcorn-shaped CdS nanostructures (d) SEM image with particle size distribution (inset), (e) FESEM and TEM (inset) images of CdS popcorn NPs obtained with 20 mmol L−1 thiourea and 4 g L−1 PVP for 24 h. Reprinted with permission from ref. 134. |
On the other hand, Zhang et al.134 demonstrated the synthesis of popcorn-shaped CdS NPs with potent photocatalytic activity by hydrothermal reaction for 24 h at a certain temperature with and without using PVP-K30 as a surfactant. It was considered that CdS nuclei generated from the reaction of Cd2+ and S2− ions that produced due to the decomposition of [Cd–thiourea]2+ with increasing temperature. Further, the continuous growth of crystal was prevented due to selective adsorption/desorption of organic ligands on the defined crystal plane of CdS and resulted in popcorn-shaped CdS NPs (Fig. 8c). The SEM image in Fig. 8d shows that CdS NPs with regular and uniform spheres of diameter 220 nm were obtained (the inset shows the size distribution). Further investigations were carried out by high-resolution SEM and TEM. Fig. 8e shows the HRSEM image of CdS NPs which were found to be with rough surfaces resulting from the aggregation of small spheres (sizes about 30–50 nm), forming popcorn-shaped NPs as clearly shown by TEM image (inset of Fig. 8e). On the other hand, it was found that CdS NPs synthesized without surfactants i.e. PVP showed different morphology that looked like nanoflowers. It was concluded that CdS NPs prepared using PVP formed like popcorn-shaped CdS NPs whereas, without PVP, the structure followed nanoflowers formation with a rough surface. This indicated that the surfactant i.e. PVP played an important role in tailoring the shape of the CdS NPs. Interestingly, it was observed that as compared to CdS nanoflowers, popcorn-shaped CdS NPss showed a much higher visible-light photocatalytic degradation activity with a rate of 93.3% in 4 h. The popcorn-shaped structure possesses the unsmooth surface with larger surface area and more active sites due to pores structures.
Recently, Kong et al.135 reported the synthesis of hexagonal CdS cones via urothermal reactions at 80–120 °C for 4–12 h as shown in Fig. 9 and its growth was attributed to the dissolution and recrystallization process. It was proposed that during the grinding process of precursors small amount of S2− escaped and promoted the cubic phase of CdS at beginning of the reaction. However, with the passage of time and an increase in temperature, more and more S2− released from thiourea and formed hexagonal CdS nuclei that grew anisotropically along the polar direction (0001) during the prolonged reaction and formed hexagonal CdS cones (Fig. 9). Interestingly, photocatalytic investigations on water splitting under visible light (λ ≥ 420 nm) revealed that hexagonal CdS cones showed a better photocatalytics property (10.5 mmol h−1 g−1) as compared to that of other nanostructures attributed to the exposure of (0001) active crystal plane. Whereas, a 3D sponge-like microporous CdS film was prepared by Feng et al.136 using solvothermal treatment of Ti pale with a seed layer for 24 h at various temperatures. The Ti pale with a seed layer was prepared by spin coating of seed layer solution over the Ti plate followed by thermal annealing at 500 °C for 2 h. It was observed that the raise in temperature increases grain size from a hundred nm to a few μm. The 3D CdS thin-film photoelectrode exhibited excellent photoelectrochemical performance and stability along with high photoelectric conversion efficiency.
Fig. 9 Synthesis of hexagonal CdS cones via urothermal reactions. Reprinted with permission from ref. 135. |
In brief, the above discussion on synthesis of various 3D CdS based nanostructures using different approached resulting in different 3D morphologies with tunable dimensions and optical properties provide a complete overview of the formation mechanism of such nanostructures. It provides a pathway to tune the photocatalytic properties of the materials based on the morphologies and structural changes for enhanced photocatalytic efficiencies in different fields. Various parameters during the synthesis of such nanostructures play important role in designing their morphologies and dimensions. Additionally, the starting materials, their concentrations followed by key reaction experimental parameters also play important role in finalizing the materials architectures. Therefore, various approaches used for the synthesis of 3D CdS based photocatalysts, starting materials, synthesis parameters, resulting morphologies with dimensions are summarized in Table 1. This not only provide the comparative strategies of synthesizing 3D CdS nanostructures but also to find the suitable parameters to desing and engineering such nanostructures with enhanced photocatalytic properties.
Synthesis method | Precursors and concentrations | Concentration of solvent | Reaction key parameters | Morphology and dimensions (nm) | Phase | Ref. | |||
---|---|---|---|---|---|---|---|---|---|
Cd | S | pH | T (°C) | t (h) | |||||
a CBD = chemical bath deposition, CVD = chemical vapour deposition, CC = colloidal chemistry, Zb = zinc blende, Wz = wurtzite Ac = acetate (CH3COO), TAA = thioacetamide (C2H5NS), EN = ethylenediamine [C2H4(NH2)2], EG = ethylene glycol [(CH2OH)2], DAA = dodecylamine (C12H27N), Na(DDTC) = sodium diethyldithiocarbamate (C5H10NS2Na), OM = Oleylamine, OTA = ctylamine, TU = thiourea [(NH)2CS], HMT = hexamethylenetetramine [(CH2)6N4], ET = ethanol (C2H5OH), NMA = N-methylaniline [C6H5NH(CH3)], TSC = thiosemicarbazide [(NH2)2NHCS)], PVP = polyvinylpyrrolidone, DETA = diethylenetriamine [HN(CH2CH2NH2)2], TEA = triethanolamine (C6H15NO3), CTAB = cetyltrimethylammonium bromide (C19H42BrN), HAD = hexadecylamine (C16H35N). | |||||||||
Hydrothermal | Cd(NO3)2 3 mmol | TU 1 mmol | CA = HMT DI | 200 | 12 | NFs (d = 250) | Wz | 63 | |
Cd:S | 200 | 12 | Spheres approx. NFs branched (5 to 8 pods) (l = 150, d = 100) NFs | ||||||
1:0.5 | |||||||||
1:1 | |||||||||
1:2 | |||||||||
1:3 | |||||||||
Cd:S = 3:1 | 120 | 12 | Ball-like (400) imperfect NFs perfect NFs | ||||||
160 | |||||||||
200 | |||||||||
CdCl2 1 g | TAA 0.75 g | CA = NMA ET (50 ml) | 120 | 1 | Nanopetal | Wz | 65 | ||
150 | 4 | ||||||||
Cd(NO3)2 | TU | DI (50 ml) CA = PVP | 150 | 1 | NFs | ||||
180 | 6 | ||||||||
[Cd (TSC)2]Cl2 0.8 g | DI (50 ml) | 150 | 12 | NFs | Wz | 137 | |||
CdCl2 3 mmol | TU 6 mmol + EN | DI | 100 | 5 | Nanospheres | Zb | 71 | ||
3 mmol | |||||||||
6 mmol | Flower | ||||||||
9 mmol | |||||||||
12 mmol | Flower | ||||||||
TU + EN + SDBS | Flower surface collapses | ||||||||
3.3 mg ml−1 | |||||||||
Flower | |||||||||
6.7 mg ml−1 | Flower | ||||||||
10 mg ml−1 | Flower (d = 10 μm) | ||||||||
1.3 mg ml−1 | Flower (d = 13 μm) | ||||||||
Cd(NO3)2 0.01 mol | Na2S 0.03 mol | 160 | 12 | NPs | Wz | ||||
Cd(NO3)2 1 mmol | TU 3 mmol | DI | 200 | 4 | Wz | 119 | |||
CA (0.3 mmol) | Dendritic (4–6 μm) | ||||||||
l-Valin | Dendritic | ||||||||
Proline | Spindle | ||||||||
Serine | NPs (40–50) | ||||||||
Cysteine | Flower-like | ||||||||
Methionine | Hierarchical | ||||||||
Histidine | Branched | ||||||||
Tryptoplan | Cauliflower | ||||||||
DI | 200 | 2 | Dendritic with short and irregular trunk and braches | ||||||
CA (0.3 mmol) | 4 | Dendritic with very long and regular trunk and braches | |||||||
l-Valin | 8 | Dendritic with reduced regularity | |||||||
12 | Dendritic with reduced regularity further | ||||||||
160 | 4 | Urchin-sphere | |||||||
180 | Urchin-sphere | ||||||||
200 | Dendrites | ||||||||
220 | Dendrites | ||||||||
DI | 200 | 4 | |||||||
CA = l-Valin | |||||||||
0.0 mmol | Irregular crys | ||||||||
0.3 mmol | Dendrites | ||||||||
0.9 mmol | Leaf | ||||||||
1.8 mmol | Flower | ||||||||
Cd(NO3)2 2 g | Lawesson's reagent 0.7 g | DI 100 ml | 90 | 10 | Porous petal twin puffy flowers | Wz | 113 | ||
15 | |||||||||
Solvothermal | Cd(Ac)2 1.4 mmol | TAA 2 mmol | EN (%):EG (%) | 150 | 5 | NPs (8) | Zb | 128 | |
0:100 | 0.5 | NPs (13) | Wz | ||||||
50:1 | 1 | Multi rods (l = 20, d = 10) | |||||||
5:95 | 180 | 1.5 | Multi rods (l = 40, d = 15) | ||||||
15:85 | 5 | Tetrahedrons and spheres (64) | |||||||
50:50 | 5 | pencil-shaped rods (l = 49, d = 20) | |||||||
65:35 | 160 | Tetrapod (l = 206, d = 22.5) prickly spheres | |||||||
100:0 | 180 | Hexagonal nanoprisms (l = 748, w = 35) | |||||||
65:35 | 210 | Tetrapod (l = 100–600, d = 20) prickly spheres nanorods | |||||||
Cd(Ac)2 18 mmol | TAA 25 mmol | EN 30 ml | 140 | 24 | Nanorods (d = 10) | Zb-centre (80 nm) with wz-arms (200 nm) W | 129 | ||
160 | Nanorods with multipods | ||||||||
180 | Tetrapods | ||||||||
200 | Tetrapods (large dimensions) | ||||||||
220 | Nanorods | ||||||||
Cd(Ac)2 | S powder | DAA (15 ml) | 220 | 4 | 130 | ||||
3 mmol | 3 mmol | Irregular shape nanorods (l = 13, d = 6) | Wz + Zb | ||||||
3 mmol | 3.75 mmol | Multipods (d = 10) | Wz | ||||||
3 mmol | 4.5 mmol | Multipods (d = 40) | Wz | ||||||
3 mmol | 5.25 mmol | Multipods (d = 60) | Wz | ||||||
3 mmol | 6 mmol | Multipods (d = 60) | Wz | ||||||
3 mmol | 9 mmol | Nanorods (l = 45, d = 15) | Wz + Zb | ||||||
1.5 mmol | 2.25 mmol | Irregular shape (90) | Wz | ||||||
6 mmol | 9 mmol | Triangular | Wz + Zb | ||||||
6 mmol | 3 mmol | ||||||||
1.5 mmol | 2.25 mmol | 100 | 4 | Nanorods (l = 25, d = 5) | Wz | ||||
3 mmol | 4.5 mmol | 140 | Multipods | Wz | |||||
180 | Nanorods | Wz | |||||||
100 | Nanorods (l = 35, d = 5) | Wz | |||||||
140 | Multipods | Wz | |||||||
180 | Multipods | Wz | |||||||
1.5 mmol | 2.25 mmol | 220 | 24 | Multipods (l = 70, d = 10) | Wz | ||||
3 mmol | 4.5 mmol | 60 | Multipods (l = 100, d = 10) | Wz | |||||
24 | Nanorods | Wz | |||||||
60 | Nanorods | Wz | |||||||
Cd(Ac)2 10 mmol | TAA 15 mmol | DAA (50 ml) | 100 | 12 | Multi-armed rods | Wz | 131 | ||
DI (50 ml) | 140 | Multi-armed rods (l = 70–100, d = 13) | Wz | ||||||
180 | Multi-armed rods | Wz | |||||||
100 | NPs (20) | Wz + Zb | |||||||
140 | NPs | Wz + Zb | |||||||
180 | NPs (50) | Wz + Zb | |||||||
CdCl2 1.14 g | TU 0.38 g | DI (10 ml)+ EN (20 ml) | 60 | 12 | Hierarchical | Wz | 117 | ||
CdCl2 1.5 mmol | S powder | OM:OTA | 90 | 16 | Tetrapod (l = 21.9, d = 10) | Wz | 138 | ||
TAA | 1:1 | Tetrapod (l = 84, d = 11.8) | Wz | ||||||
Na (DDTC) | Tetrapod (l = 20.9, d = 6.8) | Wz | |||||||
4.5 mmol | |||||||||
Cd(Ac)2 2 mmol | TU 10 mmol | DETA:ET:DI | 92 | ||||||
2:1:0 | 80 | 48 | Flower | Wz | |||||
2:1:0.2 | Porous flower | Wz + Zb | |||||||
2:1:0.5 | Belt-like | Wz + Zb | |||||||
2:0:1 | Net-like | Wz + Zb | |||||||
Cd(Ac)2 1 mmol | TU 1 mmol | DETA:DI | 180 | 12 | Branched NWs | Wz | 93 | ||
6:1 | Cage-microspheres | ||||||||
1:1 | Urchin like NFs (3.5 μm) | ||||||||
2:5 | Microspheres | ||||||||
1:6 | |||||||||
DETA:DI | Micro-trees | ||||||||
6:1 | |||||||||
CA = HAD | |||||||||
CdS NPs (6 nm) 0.1 g | EN (18 ml) | 140 | 2 h | Nanorods (l = 400, d = 40) | Wz | 121 | |||
0.2 g | 150 | 5 h | Nanorods (l = 2900, d = 40) | Wz | |||||
0.5 g | Nanorods (l = 1400, d = 40) | Wz | |||||||
0.2 g | Nanorods (l = 800, d = 40) | Wz | |||||||
CdS NPs (6 nm) | S powder | 180 | Twinrod (l = 10–50, d < 6) tetrapod | Wz | |||||
0.3 g CdS | CdS:S = 1:6 | Wz | |||||||
Others | |||||||||
CVD | CdS powder | Ar flow (150 sscm) | 800 | 15 | NPs (μm) | Wz | 97 | ||
1 | Flowers | Wz | |||||||
CBD | Cd(NO3)2 0.05 M | TU 0.06 M | TEA (0.04 M) + HCL (0.01 M) | 60 | 3 | NFs (3 μm) | Wz + Zb | 96 | |
8 | NFs (700–2000) | Wz + Zb | |||||||
12 | NFs + Cube | Wz + Zb | |||||||
CC | Cd(Ac)2 0.05 mol L−1 | TAA 0.05 mol L−1 | CTAB 0.05 mol L−1 | 90 | 0.5 | NFs (d = 30) | Wz | 23 |
CdS + hν → CdS + e− +h+ |
e− + O2→ ˙O2− |
˙O2− + 2H2O + e−→ 2˙OH + 2OH− |
˙O2− + organic pollutants → degradation products |
h+ + organic pollutants → degradation products |
Firstly, there are the generation of electron–hole pairs in CdS semiconductors under visible light irradiation. After absorption of photon energy, equal to or larger than the band gap energy of CdS nanostructures, the holes (h+) are generated in the valence band (VB) and electrons (e−) are generated in the conduction band (CB). The photogenerated charge carriers react with absorbed oxygen (O2) or water (H2O) molecules on the surface of the photocatalysts from the environment resulting in the formation of reactive oxygen species. Generally, photogenerated electrons reduce (O2) to superoxide anion radicals (˙O2−), which were then partially transformed into hydroxyl radicals (˙OH). These hydroxyl radicals (˙OH), can decompose organic pollutants effectively into carbon dioxide (CO2), water (H2O), and simple inorganic by-products.21,139 The mechanism behind the photocatalytic action of the CdS semiconductor has been shown schematically in Fig. 10.
It has been reported that the optical and photocatalytic properties of CdS nanostructures and their corresponding applications significantly depend on the morphology including shape and size, i.e. nano-architecturing of the nanostructures.23,25 3D CdS nanoarchitectures as compared to other morphologies have shown promising applications in the field of photocatalytic degradation of emerging organic pollutants. Iqbal et al.65 fabricated CdS nanoflowers and CdS nanopetals via the hydrothermal process which were confirmed by SEM micrographs as shown in Fig. 11a–d. The compositional and structural analyses were confirmed by EDS and XRD (Fig. 11e and f respectively). The EDS showed the presence of Cd and S elements whereas the XRD patterns exhibited the formation hexagonal phase in both structures. Furthermore, their optical and electrical properties were studied along with photocatalytic activities against Rhodamine B (RhB) dye molecules. The optical properties exhibited that the CdS nanoflower had a lower band gap (2.3 eV) as compared to the nanopetal (2.39 eV) as shown in Fig. 11g and h attributed to the quantum confinement effects. The photocatalytic degradation of RhB was found to be more effective in the case of CdS nanoflowers (78%) as compared to that of nanopetals (Fig. 11i and j). The higher photodegradation efficiency of CdS nanoflowers was explained by greater charge separation as studied by electrochemical impedance spectroscopy which confirmed that the 3D nanoarchitecture of CdS nanoflowers facilitated the separation of the photogenerated.
Fig. 11 SEM image of CdS nanopetals (a, b) and nanoflowers (c, d). (e, f) EDX analysis (e) and XRD pattern (f) of CdS nanopetal and nanoflower respectively. (g) UV-visible absorption spectra of CdS nanostructures and (h) Band gap of CdS nanostructure using the Tauc equation. (i) Photocatalytic decomposition of RhB over CdS nanoflower and nanopetal under visible light irradiation. (j) The rate constants determination of CdS nanoflower and nanopetal for RhB degradation.65 |
Yang et al.71 demonstrated that 3D flower-like CdS nanostructures with cubic phase and CdS NPs with hexagonal phase as determined by field emission SEM (FESEM) micrographs and XRD patterns showed excellent photocatalytic degradation ability. However, it was shown that 3D flower-like CdS nanostructures with a band gap of 2.25 eV exhibited greater photocatalytic activity as compared to CdS NPs. The highest degradation rate of flower-like CdS was found to be 90.4% for MB, whereas in the case of CdS NPs degradation rate was found to be around 88% showing the promising optical and photocatalytic behavior of CdS nanoflowers structures. These CdS 3D nanostructures are also very effective in thin film coating on various surfaces for photocatalytic degradation. Recently, it was shown by Aboud et al.140 that CdS nanoflower-based thin films exhibited unprecedented photocatalytic activities for the decomposition of MB and methyl violet (MV) dyes which were attributed to the high surface area, low energy band gap, and efficient charge separation properties for prepared CdS films.
Ganesh et al.95 synthesized polyvinylpyrrolidone (PVP) capped CdS flower-like morphology consisting of sword-like nanorods as shown in Fig. 12a. Structural investigation was carried out using XRD pattern and bright field TEM as well as HR-TEM images of the CdS nanostructures which indicated a phase transition from the cubic zinc blend to the hexagonal phase of CdS powder when reaction time was increased during the synthesis. The photocatalytic activity of PVP-capped CdS flowers exhibited fast degradation of RhB dye (95% for 120 min) under visible light as shown in Fig. 12b. Similarly, Mao et al.23 reported porous CdS nanoflowers with good photocatalytic properties against RhB. In this work, authors used the cationic ligand protection effect and the template effect of CTAB for the obtaining of uniform 3D porous CdS nanoflowers which not only served as the stabilizing surfactant for CdS but also as the organic template for the formation of 3D CdS mesoporous nanoarchitecture. The morphology was investigated by means of TEM an scanning TEM (STEM) which indicates spherical nanostructures of diameter around 30 nm. Further, SAED pattern exhibited the polycrystalline nature with high crystallinity of the CdS nanostructures. These CdS nanoflowers showed much better efficiency in the degradation of RhB compared with P25 due to the porous structure, and high photo stability with the protection of CTAB (Fig. 12c).
Fig. 12 (a and b) PVP-capped CdS flowers and degradation of RhB dye (95% for 120 min) by irradiation of visible light. Reprinted with permission from ref. 95. (c) Photocatalytic degradation of RhB in the presence of the CdS nanoflowers and P25. Reprinted with permission from ref. 23. |
It is clear from the above discussion that the morphology of the CdS nanostructures is very important for tailoring the optical properties to harness the visible light for real practical applications. 3D nano-architecturing of CdS nanostructures is promising for tuning the various morphologies with the desired properties and has the potential to apply for various applications in the field of energy and environment. Furthermore, coupling these 3D CdS nanostructures with other functional nanomaterials or nanocomposite formation could enhance their optical and photocatalytic activities along with their stability which have been discussed in the next sections.
The conducting polymers are one of the promising materials that consists of π conjugated system that involves the delocalization of π electrons and provides excellent conducting properties. Sharma et al.141 synthesized CdS/polyaniline (PANI) nanocomposite with different CdS morphologies like nanoflowers and nanorods. Through photoluminescence analysis, it was found that coupling of these CdS nanostructures with PANI showed better charge transfer producing more photogenerated e− and h+ pairs as compared to CdS nanostructures. It was concluded that introducing PANI in CdS nanostructures facilitated the charge transfer at the interface and reduced the recombination rate of the photogenerated charge carriers. CdS nanoflowers/PANI nanocomposite exhibited better photocatalytic activity towards photodegradation of MB dye molecules as compared to only CdS nanoflowers and nanocomposites with nanorods which were attributed to the formation of higher interfacial sites between CdS nanoflowers and PANI. Recently, 3D hierarchical PANI/CdS nanocomposite, synthesized by hydrothermal and chemical route forming heterojunction photoanode system, were shown to exhibit significantly enhanced visible light driven photocatalytic and photoelectrochemical (PEC) activity.146
Fig. 13 shows the SEM, TEM, and HRTEM micrographs of the 3D CdS and PANI/CdS nanocomposite nanoarchitectures. 3D CdS nanoflowers were formed with a length of a few microns (Fig. 13a and c) which consisted of several interconnected primary branches originating from a common center. Further growth of many secondary branches led to the formation of nanocorn-like structures (Fig. 13c). Fig. 13b and d show the SEM micrographs of PANI/CdS nanocomposite showing the presence of CdS backbone with the covering of PANI over its surface and boundaries. The corresponding TEM images as shown in Fig. 13e and f show similar morphology to SEM images. The photocatalytic performance of the nanostructures was investigated by conducting photodegradation experiments against rhodamine B (RhB) as the model pollutant under visible light irradiation. After the completion of each photodegradation cycle, the concentration of the degraded dye is measured by recording the absorbance spectrum of the collected dye solution. Fig. 13g and h show the absorbance spectra of RhB solution over CdS and PANI/CdS nanocomposite, respectively after regular intervals of visible light illumination with the inset showing the RhB decoloration after 60 min of light exposure. A gradual decrease in the intensity of the absorption maxima with an increase in the time intervals of visible light illumination was observed suggesting the degradation of RhB over photocatalyst samples. However, the rate of decrement in the RhB absorption peak intensity over PANI/CdS was found to be higher as compared to the pristine CdS nanostructures. Fig. 13i illustrates a comparison of the relative concentration of RhB over CdS and PANI/CdS nanocomposite with time before and after visible light irradiation. A slight decrease in the concentration of RhB in the presence of both CdS and PANI/CdS samples in the dark for 20 min was observed indicating negligible adsorption of RhB on these nanostructures after attaining the adsorption–desorption equilibrium. The CdS/polymer nanocomposites showed a better photodegradation rate (Fig. 13j) as compared to only CdS nanostructures (∼8 times higher) attributed to the occurrence of the faster rate of photocatalytic reactions at the surface and interfaces of the PANI/CdS photocatalysts. The PL spectra of the CdS and CdS/polymer nanocomposites as shown in Fig. 13k exhibited decreased PL intensity for the nanocomposite attributed to the interfacial contacts between CdS and PANI which facilitated the faster separation of the photoinduced charge carriers. It demonstrates the importance of polymer, i.e. PANI, that plays a significant role in separation and transportation of the photogenerated charge carriers enhancing the photocatalytic efficiency of the nanocomposites. Furthermore, the photocatalytic kinetic mechanism was also investigated by performing trapping photocatalytic activity using various scavengers such as benzoquinone (BQ), ammonium oxalate (AO), silver nitrate (AgNO3), and tert-butyl alcohol (t-BuOH). Through this experiment, the photodegradation efficiency of PANI/CdS was studied as shown in Fig. 13l and it was concluded that holes were not the main active species responsible for dye RhB degradation.146
Fig. 13 SEM images of (a, c) CdS NFs and (b, d) PANI/CdS nanostructured samples, TEM images of (e) CdS NFs and (f) PANI/CdS nanostructured samples. UV-vis absorption spectral changes of aqueous RhB solution over (g) pristine CdS NFs and (h) PANI/CdS nanocomposite under equal time intervals of visible light irradiation with inset depicting RhB decoloration after light illumination for 60 min, (i) degradation rate of RhB over CdS NFs and PANI/CdS nanostructured samples, (j) analysis of rate constants of CdS NFs and PANI/CdS nanostructured samples, (k) PL spectra of CdS NFs and PANI/CdS nanostructured samples, and (l) various active species trapping tests during the photodegradation of RhB over PANI/CdS under visible light illumination. Reprinted with permission from ref. 146. |
Zhang et al.143 studied the CdS and graphene-based nanocomposite as visible-light-driven photocatalysts for selective oxidation of alcohols to corresponding aldehydes. It was found that the CdS NPs uniformly overspread on the graphene scaffold resulting in tunable characteristics, such as morphology and pore structure, and optical and electronic nature were found to be tailored and dependent on the amount of graphene. The resulting high photoactivity of CdS and graphene-based nanocomposite was attributed to enhanced light absorption intensity, high electron conductivity of graphene, and its significant influence on the morphology and structure of the nanocomposites. 3D CdS and graphene nanocomposite-based aerogels with superior adsorption capacity and photocatalytic activity were investigated by Wei et al.147 for water purification. It has been demonstrated in the literature that graphene nanostructures participate as a charge carrier transporter in the photocatalysis process in combination with semiconductors inhibiting the rapid recombination of photoexcited electrons and holes resulting in the improved photocatalytic efficiency of semiconductor catalysts.147 The CdS and graphene-based 3D hybrid hierarchical aerogels showed enhanced adsorption capacity and photocatalytic activity for several organic and pharmaceutical compounds under visible light conditions due to the strong electronic interaction of the counterparts.
Similarly, CdS microspheres and reduced graphene oxide (rGO) based core–shell structures synthesized via a two-step hydrothermal method have been reported with enhanced photocatalytic activity.148 The core–shell structure was characterized by FESEM, Raman, XRD analyses. It was found that such core–shell nanocomposites structures with uniform size and morphology (as shown in Fig. 14a–d) exhibited multifunctional characteristics due to the presence of graphene such as enhanced photocatalytic activity, the effective protection of the internal CdS, enhanced absorption capability of dye molecules and facilitated the separation of photogenerated charges (as shown in Fig. 14e and f). Furthermore, the core–shell structure exhibited recyclable properties as compared to the pure CdS microsphere. Similarly, several 3D nanoarchitectures based on CdS and carbon quantum dots (CQDs) have been shown to exhibit superior photocatalytic activities in the field of water purification degrading harmful and toxic organic pollutants as well as in the energy field.149,150
Fig. 14 FESEM images of (a) GO, (b) CdS and (c) CdS@RGO microspheres (in low magnification) and (d), CdS@RGO microspheres (in high magnification), (e) the degradation rate of RhB, (C/C0) as the function of irradiation time. (f) Schematic diagram of the charge transfer between RGO and CdS with photodegradation of RhB molecules under visible light irradiation. Reprinted with permission from ref. 148. |
The combination of 3D CdS nanoflowers with graphene and polymer-forming multicomponent nanocomposites has not been investigated so extensively. Ahmad et al.5 explored the 3D CdS-based rGO and polymer i.e. polypyrrole (Ppy) nanocomposite visible light photocatalysts for the degradation of organic pollutants such as RhB, reactive blue-171 and toluene under the influence of visible light irradiation. Since Ppy is known to be a visible-light active conducting polymer catalyst, it provided a synergic effect with rGO and 3D CdS nanostructures in enhancing the photocatalytic activity of the nanocomposite. The excellent photocatalytic degradation of dyes was attributed to the formation of more interfacial reaction sites between Ppy and 3D CdS nanoflower structures. Furthermore, the introduction of rGO in the CdS/Ppy matrix enhanced the surface area and provided more reactive sites resulting in excellent nanocomposite photocatalysts for adsorption as well as photodegradation. Fig. 15a and b show the SEM images of 3D CdS nanostructures and their nanocomposites with Ppy as shown in Fig. 15c and d, indicating the uniform distribution of CdS nanoflowers covered on the Ppy sheet. Fig. 15e and f show the SEM micrographs of the nanocomposites i.e. Ppy/CdS/rGO exhibiting the scattered CdS NPs and Ppy matrix on the entire sheet of rGO. Fig. 15g and h show the photodegradation activities and kinetics of CdS, Ppy and Ppy/CdS/rGO nanocomposites by monitoring the degradation of RhB in visible light irradiation measuring the absorbance of the degraded aliquots using UV-vis spectroscopy. It was found that after the addition of rGO to the Ppy/CdS nanocomposite, enhanced photocatalytic degradation with more than 99% degradation of RhB dyes in an aqueous solution was achieved in about 180 min. The enhanced photodegradation was explained on the basis of excellent transport properties of rGO sheets that provided the best pathway for the electron transfer useful in ROS generation and further photodegradation. The rGO sheets not only increased the surface area of the nanocomposite photocatalyst but also provided a less hindered path which improved the adsorption of the dye through the π–π stacking between dye and rGO as shown in Fig. 15i. Similarly, various CdS nanostructures have been employed with many other graphene-like 2D nanomaterials such as MoS2,151,152 metal carbides,153etc. exhibiting greater photocatalytic activity as compared to the alone CdS nanostructures due to their synergistic effect.
Fig. 15 SEM images of the CdS Nanoflower (a, b), Ppy/CdS (c, d) and Ppy/CdS/rGO (e, f). (g) UV-vis spectra of the degraded sample and (h) kinetics of photodegradation of the various photocatalyst, (here PC is Ppy/CdS, PCG-1, and PCG-2 are Ppy/CdS nanocomposites with 10 and 20% rGO respectively.). (i) Proposed mechanism of the photodegradation of the RhB dye. Reprinted with permission from ref. 5. |
Polydopamine (PDA) functionalized CdS nanostructures have also been studied owing to owing to its unique advantages in surface modification resulting in enhanced photocatalytic properties.154 Yang et al.155 reported on fabrication of high performance g-C3N4/PDA/CdS nanophotocatalyst and its visible light activity towards degradation of organic pollutants. It exhibited 97% photodegradation of RhB dye molecules in 80 min under visible light irradiation attributed to the strong visible-light absorption and interfacial charge transfer facilitated by the PDA layer. A core/shell nanostructure composed of CdS/PDA/TiO2 was produced by nanocoating of PDA plus TiO2 on CdS nanospheres resulting in 3D nanosphere morphology.156 The remarkably enhanced photocatalytic performance was observed attributed to enhanced light absorption and charge carrier separation efficiency due to the PDA layer on the surface of the CdS nanospheres. PDA is a kind of emerging biopolymer material and very effective in surface modification which can find better applications in the field of photocatalysts.
Zhao et al.157 demonstrated the role of CdS NPs in enhancing the photocatalytic activity of hierarchically meso- and macroporous TiO2 photocatalysts forming hierarchically meso- and macroporous TiO2/CdS (HMTC) heterostructure materials. It was found that the textural mesopores/interconnected pore framework of TiO2 photocatalysts enabled a better opportunity to absorb maximum light radiation and heterojunction formation with CdS NPs provided visible light photocatalytic activity as well as better charge separation efficiency resulting in excellent photodegradation efficiency of RhB dye molecules (Fig. 16a). Similarly, Li et al.158 demonstrated the formation hierarchical TiO2 pinecone-like structure decorated with CdS NPs forming a heterojunction and that could be rationally tailored by optimizing the annealing temperature, which significantly enhanced photocatalytic activity. It was found that the heterojunction nanocomposite optimized at 500 °C annealing temperature exhibited excellent photodegradation activity of MO (85% degradation in 180 minutes) under sunlight irradiation attributed to the synergic effects of the CdS, special surface structure, excellent crystallinity, higher electrical conductivity, and band structure matching. Tian et al.26 demonstrated that ternary rGO/TiO2/CdS nanocomposites consisting of TiO2 spheres (∼1 μm), rGO framework uniformly decorated with CdS NPs (∼30 nm) exhibited photodegradation of MB (more than 90%) and parachlorophenol (4-CP) (more than 60%) in 60 minutes under visible-light irradiation. The photodegradation activities were higher as compared to the TiO2/rGO nanocomposites which showed that the photocatalytic activity was improved due to the presence of CdS NPs (Fig. 16b). Similarly, Zhang et al.160 proposed the ternary CdS/graphene/TiO2 hybrid nanocomposites which exhibited enhanced photocatalytic activity as compared to the CdS/graphene nanocomposite attributed to the combined interaction of the longer lifetime of photogenerated electron–hole pairs, faster interfacial charge transfer rate, and larger surface area. They proposed the interfacial charge transfer as shown in Fig. 16c.
Fig. 16 (a) Hierarchically meso- and macroporous TiO2/CdS i.e. HMTC heterostructure materials and its visible light photocatalytic activity for the degradation of RhB. HMTC1, HMTC2, HMTC3 show different concentrations of CdS and HMTC2 is the optimized concentration. Reprinted with permission from ref. 157 (b) rGO/TiO2/CdS nanocomposites and degradation efficiency of towards MB aqueous solution, reprinted with permission from ref. 26 (c) a possible reaction mechanism of charge transfer in CdS/graphene/TiO2 hybrid nanocomposites for excellent photocatalytic activity. Reprinted with permission from ref. 160 (d–f) FESEM micrographs of ZnO and ZnO/CdS hybrid nanostructures and UV-visible absorption spectra respectively. Reprinted with permission from ref. 161. |
ZnO, another most extensively used photocatalyst with a bandgap of 3.37 eV, is known for its high photosensitivity and stability, however, the photocatalytic efficiency is not promising as it is UV light activated photocatalysts and also because of the fast recombination of the photogenerated electron–hole pairs. It has been reported that the energy band structures of CdS and ZnO are adequate for promoting the charge transfer process where photogenerated electrons can flow from CdS to ZnO.161,162 Xu et al.162 synthesized hierarchical ZnO composed of ultrathin nanosheets decorated with CdS NPs (50–100 nm). These hybrid 3D ZnO/CdS nanostructures exhibited better photodegradation efficiency as compared to pure ZnO nanostructures under natural sunlight. CdS NPs were found to serve as photo-sensitizers extending the absorption spectrum in the visible region. Similarly, Li et al.161 fabricated ZnO/CdS nano-heterostructure with flower-like morphology and enhanced visible light activity as well as photocatalytic properties as shown in Fig. 16d–f. Self-assembled flower-like CdS–ZnO nanocomposite with excellent charge transfer characteristics was fabricated by Jana et al.163 Firstly, CdS NPs were synthesized followed by the formation of petal-like ZnO structures producing a flower-like nanostructure as shown in Fig. 17a. It was found that due to the formation of such hybrid flower-like structures, there was an excellent coupling of the two semiconductors resulting in the greater charge separation capability leading to better photocatalytic activity. Similarly, highly stable and surface-decorated Zn0.15Cd0.85S nanoflowers with TiO2 were demonstrated to be highly effective visible light active photocatalysts towards the degradation of RhB.164Fig. 17b–f shows the SEM images of CdS, Zn0.15Cd0.85S and TiO2/Zn0.15Cd0.85S nanoflowers nanocomposites. It was found that TiO2/Zn0.15Cd0.85S nanoflowers composite with P25:Cd ratio of 1:5 exhibited better photocatalytic performance towards the photo-degradation of RhB under visible light irradiation as shown in Fig. 17g. It was explained based on the formation of heterojunction between TiO2 and Zn0.15Cd0.85S nanoflowers leading to the greater separation of the photogenerated charge carriers and charge transport. Similarly, synthesized ZnO hierarchical nanoneedle structures sensitized by CdS NPs deposited on copper fiber (CF) that showed greater photocatalytic activity. The CF played an important role in supporting and transporting the charge carriers of CdS NPs/ZnO hybrid nanoneedles presenting the excellent photocatalytic performance under visible light, enabling the decomposition of organic dyes such as RhB within 60 min, with desirable cycling ability.
Fig. 17 (a) Schematic of the growth mechanism of flowerlike CdS–ZnO nanostructures.163 SEM images of (b) pure CdS NPs, (c) Zn0.15Cd0.85S nanoflowers and (d) TiO2/Zn0.15Cd0.85S nanocomposite with P25:Cd of 1:10, (e) 1:5 and (f) 1:3. (g) Photo-degradation of RhB using TiO2/Zn0.15Cd0.85S nanocomposite with P25:Cd of 1:5.164 |
Various oxide semiconductor photocatalysts such as BiOBr, Bi2WO6, La2Ti2O7, and Bi4Ti3O12 have been studied coupled with CdS forming 3D heterostructures with excellent photocatalytic activities.165–169 The CdS/BiOBr 3D hybrid nanocomposite photocatalyst was found to exhibit 97% photodegradation of RhB under visible light irradiation and showed no apparent decrease in activity after five cycles.165 The Bi2WO6/CdS hybrid 3D nanocomposite films based photocatalyst showed stable catalytic performance until seven successive runs with 92% of MB degradation166 whereas, CdS QDs/Bi2WO6 heterojunction exhibited 94.5% photocatalytic efficiency. Recently, Cheng et al.169 developed 3D core–shell heterojunction photocatalysts by coating CdS NPs onto Bi4Ti3O12 hierarchical microspheres and studied their photocatalytic activities towards the removal of organic pollutants and photocatalytically reduction of Cr(VI) ions.
Interestingly, Wang et al.70 demonstrated the formation of flower-like Au@CdS-CdS NPs with hierarchical heterostructures composed of epitaxially grown 1D CdS nanorods on the surfaces of Au@CdS core–shell NPs as shown in Fig. 18. It was found that these Au and CdS-based 3D hybrid nanoflowers exhibited absorption covering the whole visible region with enhanced photocatalytic activity as compared to only core–shell or CdS nanostructures. SEM micrographs in Fig. 18a–c show the uniform and well-dispersed Au NPs, Au@CdS core–shell NPs and Au@CdS-CdS NPs respectively. The SEM image of Au@CdS-CdS NPs shows clear flower-like nanostructures. Furthermore, TEM and HR-TEM images (Fig. 18d–f) show clearly the Au@CdS core–shell NPs with a thick CdS shell and nanoflowers structures of Au@CdS-CdS NPs with epitaxially grown 1D CdS nanorods on the surface of Au@CdS core–shell NPs. The diameter and the length of the CdS nanorod were found to be about 16 nm and 40 nm, respectively. The EDS spectrum as shown in Fig. 18g confirms the presence of various elements i.e. Au, Cd, S. The CdS nanocrystals are shown in Fig. 18h. In addition, the colors of the solution of Au colloids, Au@CdS core–shell NPs, Au@CdS-CdS nanoflowers NPs, CdS counterparts, are shown in Fig. 18i. These CdS–Au hybrid nanoflowers structures were used for the photocatalytic degradation of R6G dye molecules under visible light which showed excellent photodegradation activity and recyclability as shown in Fig. 18j and corresponding mechanism including two different charge transfer routes has been shown in Fig. 18k. Here, the constituent elements i.e. both Au and CdS are visible light active materials and can generate photoinduced charge carriers. As shown in Fig. 18k, there might be two charge separation processes of excitations of individual Au and CdS and transfer of photoexcited electrons from one to another. In case, when CdS would be excited, the photoexcited electrons would jump from the CB of CdS to the Au and in the case when Au would be excited, photoexcited electrons would jump from the surface plasmon state of Au to the CB of CdS. There might be another case when both the elements would be excited, then both the mechanism of photoexcited electrons would be possible. However, it has been reported that the transfer of photoexcited electrons from semiconductor to metal is more probable.70 Similarly, CdS nanosheets/NPs on Ag nanowires, i.e. Ag@CdS core–shell NPs with Ag nanowire structures, were produced by a wet-chemistry approach at low temperatures. These hierarchical nanostructures were found to be excellent photocatalysts as exhibited efficient photocatalytic performance in photodegradation of MO i.e. 96% of MO within 240 min due to the broad absorbance from the UV to the near-infrared region leading to the enhance the photocatalytic performance.177
Fig. 18 (a, b and h) SEM images of Au nanoparticles, Au@CdS with a thin shell, and CdS counterparts, respectively. (d) TEM images of Au@CdS with a thick shell. (c, e, f and g) SEM, TEM, HR-TEM image, and EDS profile of Au@CdS-CdS nanoflowers. (i) Photographs of their solution colors. (j) The cycling runs for the photocatalytic degradation of R6G dye over the Au@CdS-CdS nanoflowers under visible light irradiation (400–780 nm). (k) Two charge separation mechanisms for Au@CdS-CdS nanoflowers under 400–780 nm and 600–780 nm irradiation, respectively.70 |
In addition to the hybrid 3D photocatalysts of CdS-based nanoflower structures with noble metals, there are several multicomponent plasmonic hybrid CdS nanostructures including other photocatalyst nanomaterials.178,179 For example, Zhang et al.180 synthesized BiOX(Cl, Br)-Au-CdS photocatalysts exhibiting excellent visible-light-driven photocatalytic activity as compared to BiOX or BiOX(Cl, Br)-Au only toward the degradation of RhB dye molecules. These multi-element photocatalysts with the inclusion of CdS and also with Z-scheme showed improved charge separation efficiency of photogenerated charge carriers. Similarly, Li et al.178 reported on Z-scheme CdS/Au/TiO2 nanobelt hybrid photocatalyst for eliminating norfloxacin from water. For such architecture, it was concluded that TiO2 nanostructures provided mainly the absorption/reaction sites, CdS NPs enhanced the overall light harvesting, whereas Au NPs played the role of an electron transfer mediator. All these contributed to the fast interfacial charge transfer leading to the efficient photoexcited charge carrier separation.
Fig. 19 Low and high-magnification SEM image of (a) CdS, (b) CdS/Cu7S4. (c) UV-vis diffuse reflectance spectra for the CdS and various compositions of CdS/Cu7S4 nanomaterials, (d) Kubelka–Munk-transformed diffuse reflectance spectra for the CdS and various compositions of CdS/Cu7S4 nanomaterials along with estimated band gap, (e) a schematic of the synergistic catalytic mechanism of CdS/Cu7S4 catalysts.182 |
Huang et al.149 fabricated carbon QDs (CQDs) based flower spherical-like CQDs@CdIn2S4/CdS 3D nanostructures with up-conversion properties by the microwave-assisted method. These 3D hybrid nanostructures with up-conversion properties were able to convert long-wavelength light into short wavelength and showed excellent photodegradation ability where CQDs played an important role of spectral converters, electron transport mediators and acceptors. Shi et al.183 prepared hierarchical Z-scheme Bi2S3/CdS heterojunctions with dandelion-like structures which showed efficient bacteria-killing activity under visible light irradiation. A hybrid CdS-based flower-like 3D structure with excellent visible light activity composed of hexagonal pencil-shaped nanorod CdS and flower-like morphology SnS2 was proposed by Huang et al.184 It was found that such nanocomposite exhibited high separation of photoinduced charge carriers along with faster interfacial charge transfer under the influence of sunlight irradiation. These CdS/SnS2 3D nanocomposite photocatalysts showed better photodegradation of MO dye molecules with 85.3% degradation within 120 min with reaction rate constant 9.2 times and 5.32 times higher that of pure CdS and SnS2 samples, respectively.
The above discussion on various 3D CdS based nanostructures and their photocatalytic activity towards photodegradation of organic pollutants shows that the morphology plays an important role in degradation efficiency/process. The tailoring of morphology tunes the optical properties of nanostructures and in turn provide tunable characteristics to the materials for enhancing the photodegradation efficiency. Some important CdS based photocatalysts, their optical properties, degradation of various pollutants and photodegradation efficiencies have been summarized in Table 2.
Catalysts | Optical properties (band gap) | Pollutants | Light source | Photodegradation results/efficiency | Ref. |
---|---|---|---|---|---|
CdS nanoflower & CdS nanopetals | Band gap −2.3 eV for nanoflower and (2.39 eV for nanopetal) | RhB | Simulated sunlight | 78% (nanoflowers) and 63% (nanopetal) in 4 h with rate constant 2.6 × 10−3 and 4.05 × 10−3 min−1 respectively | 65 |
3D flower-like CdS nanostructures | 2.25 eV | MB | Simulated visible light | 90.4% | 71 |
CdS nanoflower-based thin films | 2.34 to 2.17 eV | MB, MV | 40 mW xenon light | 96% for MB and 84% for MV in 260 min | 140 |
CdS flower-like morphology composed of word-like nanorods | Red shift in UV visible absorption spectra | RhB | Visible light | 95% in 120 min | 95 |
Porous CdS nanoflowers | Absorption in visible range | RhB | Visible light | 90% (in 10 min) and complete degradation in 30 min | 23 |
Activated carbon-loaded CdS nanoflower | Varies between 1.85 to 2.51 eV for different compositions | RhB | Visible light | 98.12% in 150 min | 145 |
PANI/CdS-composite nanoflowers | 2.53 eV | MB | Visible light | Rate constant of PANI/CdS-nanoflower was found to be enhanced by ∼1.9 times over pure CdS-nanoflower | 141 |
3D hierarchical PANI/CdS nanocomposite | 2.48 eV | RhB | Visible light, halogen lamp (150 W) | Rate constant of CdS was enhanced by 8 times after coupling with PANI | 146 |
3D hierarchical CdS and graphene nanocomposite | Visible light absorption | RhB, MB, MO | 300 W xenon lamp | 99.4% (RhB), 88.3% (MB), 73.0% (MO) in 60 minutes | 147 |
CdS@rGO microspheres | Visible light absorption | RhB | 500 W xenon lamp | 95.2% in 50 min | 148 |
Flower spherical-like composites CQDs@CdIn2S4/CdS | Visible light absorption and band gap <2.4 eV | MO | Ultraviolet and simulated visible light | 97% in 20 min and better in visible light | 149 |
Z-scheme CdS/CQDs/BiOCl heterojunction | Visible light absorption | RhB and phenol | 500 W xenon lamp and 500 W mercury lamp | 99.5% within 105 min under UV light irradiation | 150 |
PpyCdS-nanoflower/rGO | Visible light absorption | RhB | Visible lamp (power 500 W) | 99.1% in 180 min | 5 |
TiO2/CdS pinecone-like structure heterojunction | — | MO | Sunlight | 85% degradation in 180 minutes | 158 |
rGO/TiO2/CdS | (More than 90%) and parachlorophenol (4-CP) (more than 60%) in 60 minutes under | MB, 4-CP | Visible-light | MB more than 90% and (4-CP) more than 60% in 60 minutes | 26 |
Hierarchically meso-macroporous TiO2/CdS heterojunction | Visible light absorption | RhB | 300 W Xe lamp | 87% in 60 min | 157 |
Ternary CdS/graphene/TiO2 hybrid nanocomposites | Visible light absorption | Alcohols | 300 W Xe arc lamp | Enhanced photocatalytic activities as compared to individual catalysts | 160 |
ZnO/CdS nanoflower-heterostructure | 2.37 eV | RhB | 300 W Xe lamp | 100% in 90 min | 161 |
ZnO/CdS nanoflower- | — | RhB | 1000 W halogen lamp | 90% in min | 163 |
P25/Zn0.15Cd0.85S nanoflower | 2.23 eV | RhB | 350 W xenon lamp | 100% in 60 min | 164 |
Flower-like Au@CdS-CdS NPs | Visible light absorption | R6G | Visible light | 86% in 40 min | |
Ag@CdS core–shell NPs | Uv-visible to NIR absorption | MO | LSC-100 solar simulator | 96% in 240 min | 177 |
BiOX(Cl,Br)-Au-CdS | Visible light absorption | RhB | 300 W xenon lamp | 100% in 40 min | 180 |
Z-scheme CdS/Au/TiO2 nanobelt | — | Norfloxacin | 35 W xenon lamp | 65% | 178 |
3D hierarchical CdS/Cu7S4 lily like nanoflower | 2.44 eV to 1.61 eV | MB | Visible light | 98% in 20 min (MB) | 182 |
CQDs@CdIn2S4/CdS 3D nanostructures | Visible light absorption | MO | Ultraviolet light, visible light and simulated sunlight | 97% in 20 min | 149 |
As per the discussion above, it seems that CdS based 3D nanomaterials are very interesting photocatalysts with attractive optoelectronic properties in the field of photocatalytic degradation of organic pollutants. The sole CdS as well as its hybrid composite nano-architectures are very promising with ease of modification and tunability of their morphological, structural and optical properties. In recent years, these nano-architectures have shown great interest in other fields of photocatalytic applications such as photocatalytic hydrogen production and CO2 reduction which have been discussed in the next sections.
2γ → 2eCB− + 2ehv + photon induced e−/h+ generation |
2H2O + 4h+ → O2 + 4H+ water oxidation half reaction EoOX = −1.23 eV |
4H+ + 4e− → H2 water reduction half reaction EoRed = 0 eV |
2H2O + 2γ → 2H2 + O2 overall water splitting ΔEo = 1.23 eV |
Fig. 20 Schematic illustration of the main processes for photocatalytic water splitting over a semiconductor photocatalyst. Reprinted with permission from ref. 193. |
In detail, the basic process of a semiconductor photocatalyst for hydrogen evolution from water splitting includes the following steps: first, light energy is converted into chemical energy, and electrons will transfer from the VB to the CB, creating photoproduced electron–hole pairs. Then, the electrons and holes can drive the H2O to H2 and O2, respectively. The minimum energy required to drive the reaction referred to that of two moles of impinging photons is 1.23 eV. It is worth noting that the band gap for CdS is ∼2.4 eV, and the CB position of CdS is more negative than the redox potential of EH2/H2O, while the VB position is more positive than the redox potential of EO2/H2O.89,194 In other words, CdS is an appropriate photocatalyst for catalytic hydrogen generation.188
As mentioned above, CdS has emerged as one of the most promising photocatalysts for catalytic hydrogen generation under visible light. However, monovalent CdS possess low photocatalytic activity, due to its suffering from several vital disadvantages, such as, low stability in a wide pH range, serious photo-corrosion, fast recombination of photogenerated electron–hole pairs, etc. Therefore, in order to enhance the photocatalytic hydrogen generation activity of monovalent CdS, a variety of strategies have been developed. The first one consists of adjusting the morphology, size, crystallinity, etc. of CdS. The second way consists of coupling the CdS with other materials (such as carbon materials, noble/non-noble metal-based materials, etc.), creating CdS-based heterostructures that can form a Schottky barrier and overcoming the disadvantages of monovalent CdS.
Fig. 21 The SEM images of (a) CdS-nanosphere, (b) CdS-nanorod and (c) CdS nanosheet. (d) Photocatalytic hydrogen evolution rates in 12 h for CdS-based nanosphere, nanorod, and nanosheet. Reprinted with permission from ref. 196. (e) Schematic diagram showing the formation of CdS structures with various morphologies by the solvothermal method using different solvents. (f) Comparison of rate of hydrogen production over CdS photocatalysts with different morphologies. Reprinted with permission from ref. 197. (g) Schematic illustration of the preparation process of the 3D sponge-like microporous CdS thin-film photoelectrode. (h) The photoinduced i–t curves at 0 V (vs. Ag/AgCl) of the prepared CdS photoelectrodes. Reprinted with permission from ref. 136. |
Up to now, despite changing the morphology, structure, and crystallinity to promote the photocatalytic H2 generation activity of CdS, further large-scale applications of CdS photocatalysts are still restricted due to their unstable chemical properties and serious photocorrosion under visible light irradiation for a long time. To solve these problems, it can be demonstrated to be useful that combine CdS with other stable materials (such as, noble metal, metal oxides, sulfides, carbon, organic materials, etc.) to fabricate CdS-based nanohybrids.61
Fig. 22 (a) Optical photograph of Morpho didius. SEM images of the (b) wing scales and (c) CdS/Au-M. (d) Photocatalytic activities of different samples for H2 production under 320–780 nm. Reprinted with permission from ref. 201. (e) TEM and HR-TEM images of AgCdS-120 sample. (f) Schematic diagram showing the combination of factors that operates in the AgCdS-T photocatalysts. (g) Relationship between H2 evolution for AgCdS-T with respect to the Ag2S surface concentration and concentration of quantum dots.202 (h) Graphical illustration for the synthesis of CdS, CdS/Au, and (c) CdS/Au-SCN. (i) FESEM/EDX of CdS/Au-SCN (0.5 mM). (j) The photocatalytic H2-evolution activity performance of different samples. Reprinted with permission from ref. 203. |
In addition, it is reported that the H2-production rate on the sample surface plays an important role for the noble metal cocatalyst-modified photocatalysts. To confirm this phenomenon, Wang et al.203 demonstrated that the selective modification of SCN− on the Au surface can obviously enhance the photocatalytic activity of CdS/Au due to the possible synergistic effect of Au as an electron-transfer mediator and SCN− as the interfacial catalytic active-sites (Fig. 22h and i). Specifically, the CdS/Au-SCN exhibited better photocatalytic activity (109.60 μmol h−1) than that of CdS/Au (73.70 μmol h−1) as shown in Fig. 22j.
Fig. 23 (a and b) SEM and HRTEM images of the CBT-50. (c) The average rate of photocatalytic H2 generation over all the CBT-x samples. Reprinted with permission from ref. 210. (d, e) SEM and TEM images of the NiS/CdS NFs HSNC. (f) Photocatalytic activity of the optimal NiS/CdS NFs HSNC. Reprinted with permission from ref. 211. (g) Schematic diagram illustrating the synthesis process of the Co9S8@Cd/CdS heterostructure. (h) Photocatalytic H2 evolution rates over the prepared samples. Reprinted with permission from ref. 212. |
In addition, Zhang et al.211 reported a novel β-NiS film modified CdS nanoflowers (NiS/CdS NFs) heterostructure by one-pot hydrothermal method. Because the surface of CdS nanoflowers has been covered by the highly conductive β-NiS film, it could benefit the transfer of photogenerated e− and facilitate the separation of e−–h+ pairs. As a consequence, the NiS/CdS NFs can achieve a recorded value for an H2 production rate of about 30.1 mmol h−1 g−1 (Fig. 23d–f).
In addition to the metal oxides/sulfides/selenides-CdS based binary nanocomposites could be used as a co-catalyst to enhance the photocatalytic H2 production efficiency for CdS. Recently, some studies have tried to combine CdS with two or more other co-catalysts to form a multicomponent such as CdS/Au/ZnO, Ti3CN@TiO2/CdS-based photocatalysts, which further showed that the photocatalytic performance of CdS-based multicomponent nanocomposites was obviously enhanced.213 For example, a hollow Co9S8/Cd/CdS Z-scheme tubular hybrid heterostructure has been reported by Zhang et al.212 (Fig. 23g). Based on the high-density catalytic sites, good solar light capture by small band gap Co9S8/CdS, and incorporation of Cd in Co9S8/CdS could offer a fast charge separation and smooth transfer, the obtained Co9S8/Cd/CdS nanocomposite shows an H2 production rate about 10.42 μmol h−1 without an obvious decrease in activity after several cycles (Fig. 23h).212
Fig. 24 (a) The synthetic illustration of CdS/DETA hybrids. (b) Fourier-transform infrared spectroscopy (FT-IR) spectra of CdS NRs and CdS/DETA. (c) The cycling test of PHE over CdS and CdS/DETA composites. Reprinted with permission from ref. 214 (d) schematic illustration of PANI shell coating on the CdS nanospheres surface. SEM images of the (e) porous CdS nanospheres and (f) PANI@CdS core–shell nanospheres. (g) The photocatalytic hydrogen production rates of porous CdS nanospheres and PANI@CdS core–shell nanospheres. (h) Schematic energy level diagram of the component materials used in the inverted configuration. Reprinted with permission from ref. 215. |
Fig. 25 (a) TEM and (b) HRTEM images of CdS/graphene sample. (c) The photocatalytic activity for H2-production and (d) the schematic illustration for the charge separation and transfer in the CdS/graphene system under visible light. Reprinted with permission from ref. 27. (e) The schematic illustration for the proposed g-C3N4-cocatalyst modified CdS heterostructure. (f) Graphical illustration for the synthesis of g-C3N4/CdS composite photocatalysts. (g and h) TEM images of the CdS/g-C3N4. (i) The photocatalytic H2-production activities of the CdS/g-C3N4 samples. Reprinted with permission from ref. 216. |
As discussed in last Section 3.1, PDA as an emerging polymeric materials has great efficiency to boost the photocatalytic properties of the photocatalysts by providing a thin layer on their surface that facilitates the tunneling of photoelectrons which further improves the wettability of catalysts, and provides a passivating surface.217,218 Wang et al.218 demonstrated that PDA possessed a good photothermal effect in boosting photocatalytic H2 production by studying the photocatalytic activity of PDA/CdS nanocomposites under the xenon lamp irradiation. Interestingly, it was observed that PDA layer prevented the CdS nanostructures from photo corrosion and served as a photothermal matrix resulting in increasing the reaction temperature which improved the H2 production as compared to the production obtained at room temperature. Similarly, Liu et al.219 demonstrated that CdS@PDA@SnO2 nanostructures exhibited enhanced photocatalytic H2 production and inhibited photo-corrosion of CdS nanostructures.
In recent years, the photocatalytic hydrogen production using CdS-based materials, especially 3D hierarchical nano-architectures, has shown great progress with better production efficiency and seems to be a potential alternative in the field of semiconductor photocatalysts. Table 3 lists the photocatalytic hydrogen evolution activities of the CdS-based catalysts. However, much more research is still required to make it more successful for commercial applications.
Catalyst | Light source | H2 evolution rates | Solar-to-hydrogen (STH) efficiency/quantum efficiency | Ref. |
---|---|---|---|---|
Hexagonal CdS | 300 W Xe lamp | 5.4 mmol g−1 h−1 | 3.23% | 183 |
CdS nanorods | Visible light | 24.94 μmol h−1 | — | 184 |
CdS branched TiO2 | Simulated sunlight | 11.9 μmol cm−2 h−1 | 1.5% | 129 |
CdS nanoplates | 300 W Xe lamp | 1.61 mmol gCdS−1 h−1 | — | 126 |
NiS loaded on CdS nanoplates | 300 W Xe lamp | 22.3 mmol gCdS−1 h−1 | 18% | 126 |
RhP/CdS | Visible light (λ > 420 nm) | 32.54 μmol mg−1 h−1 | — | 185 |
Ru-CdS–ZnO–CdO | Visible light | ∼22.5 μmol g−1 h−1 | — | 187 |
3D CdS/Au | Visible light | 221.8 μmol h−1 | — | 188 |
Ag-CdS | Xenon arc lamp (150 W | ∼1.60 mmol gCdS−1 h−1 | — | 189 |
CdS/Au-SCN | 350 W xenon lamp (λ ≥ 420 nm) | 109.60 μmol h−1 | ∼11.25% | 190 |
CQDs@CdIn2S4/CdS | UV-vis | 397.2 μmol g−1 h−1 | — | 140 |
CuS/CdS(H)/CdS(C) | Visible-light irradiation (>420 nm) | 2042 mmol g−1 h−1 | — | 192 |
TiO2/CdS | 51.4 mol h−1 | — | 193 | |
ZnO/CdS | 350 W xenon lamp | 4134 μmol g−1 h−1 | — | 194 |
In2Se3/CdS | 300 W Xe lamp | 1.632 mmol g−1 h−1 | — | 196 |
CdS branched TiO2 nanoarrays | Solar light | 11.9 μmol cm−2 h−1 | — | 197 |
NiS/CdS NFs | 300 W Xe lamp (>420 nm) | 30.1 mmol h−1 g−1 | 43% | 198 |
Co9S8/Cd/CdS | Visible-light | 10.42 μmol h−1 | — | 199 |
CdS/Au/ZnO | 300 W Xe lamp with a 420 nm | 102.9 mmol h−1 | 9.6% | 200 |
CdS/DETA | Solar light | 8059 μmol g−1 h−1 | — | 201 |
PANI@CdS | Visible-light | 310 mol h−1 g−1 | — | 202 |
G–CdS | Visible-light | 1.12 mmol h−1 | 22.5% | 27 |
g-C3N4/CdS | UV cutoff filter (≥420 nm) | 5303 μmol h−1 g−1 | — | 203 |
Cat. + hν → Cat. + e− +h+ |
H2O + h+ → ˙OH + H+ |
COOH* + H+ + e−→ CO* + H2O |
CO* → CO |
As illustrated in the equations above, many steps in the photoreduction of CO2 require large energy inputs. The energy of the photo-induced electrons should be more negative than the redox potential of the CO2 reduction reactions (e.g. −0.53 V for CO2 + 2H+ + 2e− → CO + H2O at pH 7 in an aqueous solution versus a Normal Hydrogen Electrode (NHE)),222 while the energy of the photo-induced holes should be more positive than the redox potential of the H2O oxidation. It demands that the photocatalysts applied in the CO2 reduction provide at least equivalent CB and VB positions to proceed with the reduction processes. CdS with the ability to harvest visible light (bandgap of around 2.4 eV) while affording suitable CB and VB potentials attracts much attention in the field.59,75,78
Fig. 26 (a) The illustration of the 2D/2D α-Fe2O3@CdS heterostructure. (b) The illustration of the energy band offsets and the heterointerface electronic property of the 2D/2D α-Fe2O3@CdS heterostructure. (c) The CO production of photocatalytic CO2 conversion changes along with the time of simulated solar light irradiation. Comparison of photocatalytic activity over different samples in the first hour. (Inset) The Z-scheme charge transfer pathway for the photocatalytic CO2 conversion and H2O oxidation.223 |
Fig. 27 (a) The schematic of the synthetic procedure of CdS QDs/ZIS NFs composites, (b)–(d) SEM, (e)–(g) TEM, and HR-TEM images of the CdS QDs/ZIS NFs composites. (h) The photocatalytic CO2 reduction rates for ZnIn2S4-CdS, ZnIn2S4, and CdS catalysts, (i) the ultrafast kinetics and the global fitting results (probing in the range 1050–1090 nm using a 10 nm interval) for ZnIn2S4-CdS, ZnIn2S4. (j) The schematic illustration of the photogenerated electrons. Reprinted with permission from ref. 224. |
Xu et al.221 fabricated a CdS/Ni-MOF catalyst with the 3D hierarchical heterostructure for the photoreduction of CO2 into CO. The flower-shaped Ni-MOF was prepared through a simple hydrothermal method. Then, CdS particles were grown on the hierarchical Ni-MOF substrate to form the 3D heterostructure (Fig. 28a). The CB and VB values of Ni-MOF and CdS are −1.37 eV and +1.93 eV, −0.94 eV, and +1.06 eV, respectively. It meets the requirements of CO2 reduction. The 3D hierarchical heterostructure prevented the aggregation of CdS, increased the active surface area, and improved light-harvesting while promoting the separation of the photogenerated electron–hole pairs. The synergy of these benefits resulted in enhanced photocatalytic CO2 reduction performance (Fig. 28b). The CdS/Ni-MOF catalysts inhibited the H2 production but promoted the CO and CH4 yields (Fig. 28c, e and f). The catalyst of 20%-CdS/Ni-MOF exhibited the best performance for photocatalytic reduction of CO2 to CO with the CO yield of 7.47 μmol g−1 in the fourth hour, which was almost 16 times and 7 times that of the Ni-MOF and pure CdS (Fig. 28c and d). The CO yield of 30%-CdS/Ni-MOF and 40%-CdS/Ni-MOF decreased quickly. This may be due to the excessive loading of CdS, damaging the hierarchical structure of the CdS/Ni-MOF catalyst, which resulted in a severe decrease in photocatalytic activity. The 3D hierarchical heterostructure of CdS/Ni-MOF is essential to the enhancement of photocatalytic performance.221 Hollow structures also allow the catalysts to exhibit a big surface area for the abundant active sites for the catalytic reactions. Besides, hollow-structured photocatalysts can further enhance their catalytic performance with the high utilization efficiency of light harvesting by the scattering and reflection effects.227
Fig. 28 (a) The schematic of the synthetic procedure of CdS/Ni-MOF. (b) The schematic of CdS/Ni-MOF for photocatalytic reduction of CO2. (c) CO yield; (d) repeat experiment diagram; (e and f) yields of H2 and CH4. Reprinted with permission from ref. 221. |
Zhang et al.227 fabricated CdS hierarchical multi-cavity hollow particles (HMCHPs) through a Zn-based zeolitic imidazolate framework (ZIF-8)-template method. ZIF-8 was first grown on the cobalt glycerate solid spheres (Co-G SSs) to construct Co-G@ZIF-8 hierarchical solid spheres. Followed by a sulfidation reaction, CoSx@ZnS HMCHPs were prepared (Fig. 29a). TEM revealed that the CoSx@ZnS HMCHPs particles were made of a central spherical chamber covered by interconnected small cavities. The shell of the hollow-structured particles was composed of small cavities generated from the transformation from quasi-spherical ZIF-8 particles to sulfide materials (Fig. 29b–g). CdS HMCHPs had the best catalytic performance with a CO yield rate of around 1337 μmol h−1 g−1 among all the comparisons (Fig. 29h). With the addition of Au particles to the catalysts, the CO generation rate could be further promoted (Fig. 29i) with excellent stability (Fig. 29j) and visible light response (Fig. 29k).
Fig. 29 (a) The schematic of the synthetic process of CdS HMCHPs. (I) Synthesis of Co-G@ZIF-8 HSSs by growing ZIF-8 onto Co-G SSs through a solution growth approach. (II) Conversion of Co-G@ZIF-8 HSSs into CoSx@ZnS HMCHPs via a sulfidation treatment. (III) Conversion of CoSx@ZnS HMCHPs into CdS HMCHPs through a cation-exchange reaction. (b–d) The FESEM images and (e and f) TEM images of the CdS HMCHPs. (g) The HRTEM image of the CdS HMCHP (inset: the SAED pattern). (h) The photocatalytic CO2 reduction performance of HMCHPs, CdS SSs, and HSs. (i) The photocatalytic CO2reduction performance of the CdS HMCHPs with different loadings of Au. (j) The CO and H2 stability tests for Au(25)@CdS HMCHPs. (k) The wavelength-dependent yields of CO and H2 for Au(25)@CdS HMCHPs. Reprinted with permission from ref. 227. |
The CdS-based hierarchical 3D nano-architectures have the potential to be promising visible light active materials with better stability and corrosion-resistant capability. The application of such nanomaterials especially CO2 reduction has been an emerging area and great efforts are being done in the field, as listed in Table 4 below.
Catalyst | Light source | Production rate | Stability | Ref. |
---|---|---|---|---|
CdS-S2- | 340 nm > λ > 450 nm | CO: 2130 μmol g−1 h−1 | 6 h | 228 |
CdS/NC | Visible light (λ > 420 nm) | CO: 2130 μmol g−1 h−1 | 5 h | 229 |
α-Fe2O3/CdS | AM 1.5G light | CO: 9.3 μmol g−1 h−1 | 6 h | 223 |
ZnIn2S4-CdS | Visible light (λ > 420 nm) | CO: 2182.5 μmol g−1 h−1 | 20 h | 224 |
CdS/Ni-MOF | 300 W xenon lamp | CO: 7.47 μmol g−1 h−1 | 16 h | 221 |
CoSx@ZnS HMCHPs | Visible light (λ > 400 nm) | CO: 1337 μmol h−1 g−1 | 4 h | 227 |
• CdS is a toxic element and exposure to it can negatively affect the environment and human health. Due to this, it is essential to develop more efficient ways to recover and recycle CdS. Furthermore, the potential release of CdS nanoparticles into the environment can adversely affect wildlife, plants, and human health. Therefore, toxicity and environmental studies are needed to assess the risk of CdS-based nanomaterials.230,231
• Photocorrosion is a general phenomenon during the photocatalytic process for CdS-based photocatalysts resulting in its limited application in the industrial sector. The causes of the photocorrosion are: (i) the oxidation of sulfur ions into sulfur by photogenerated holes and (ii) the occurrence of redox reactions on the surface of CdS under anaerobic environment. Therefore, more investigation is required to determine the cause of the photocorrosion of CdS and increased lattice stress–strain when exposed to an air environment during photocatalysis.18
• It has been found that the size and shape of nanostructures show significant influence on their physical/chemical properties and further on their functionality. Hence, morphology is an important parameter that influences photocatalytic activity. However, fabricating such nanostructures or hybrid nanostructures with complex morphology is challenging as they require high preparation skills. Therefore, synthesizing CdS nanoparticles is challenging and not well-controlled yet, making it difficult to produce large quantities of efficient CdS-based nanomaterials.232
• CdS-based photocatalysts can be made in a variety of ways, but it is still challenging to produce them on a large scale with high quality. In addition, the CdS-based photocatalysts should exhibit high performance with excellent properties such as desired size and ideal morphology.
• The photocatalytic reaction mechanism of CdS-based photocatalysts is still unclear; however, most reports suggest that the separation of charger carriers and the interaction of reactive oxygen species (ROS) like hydroxyl radicals were responsible for the enhanced photocatalytic activity. It appears that additional parameters, such as crystal size, morphology, and shape, can also affect the performance of CdS-based photocatalysts. It is important to continue researching and developing new methods to fully address these challenges to fully realize the potential of CdS-based nanomaterials.
In the current review, we have given a broad overview of the different morphologies of CdS nanostructures, as well as their photocatalytic characteristics and mechanisms under varied morphologies. Additionally, particular focus has been placed on several photocatalytic applications for CdS-based 3D nanoarchitectures, including the degradation of complex organic pollutants, the production of H2 by water splitting, and the photoreduction of CO2. Based on their intended uses, CdS-based nanomaterials are further divided into polymer-based, carbon-based, metal oxide-based, nanocomposites-based, transition metal-based, organic material-based, and MOF-based categories.
Even though CdS-based catalysts have already made considerable progress, more work needs to be done before they can be used in competitive and realistic industrial-scale applications. Exploring research areas like:
• Charge transfer properties for CdS-based photocatalysts are an area that has not been sufficiently researched. Therefore, further modification is required to improve the charge separation and transfer. This can be achieved by using advanced materials and structures such as quantum dots, core–shell structures, and doped CdS photocatalysts. For instance, Li et al., synthesized Ti3CN@TiO2/CdS heterojunction, which showed excellent stability and photocatalytic performance.233 To effectively prevent photo-corrosion of CdS-based structures, interface engineering can be used to avoid recombining produced electron–hole pairs and accelerate charge separation.
• It is desirable to design Z-scheme structures for CdS-based nanomaterials, which ensures close contact between CdS and other materials resulting in high H2 production efficiency. For instance, Meng et al. created Z-scheme CdS/TiO2 hierarchical systems for photocatalytic hydrogen generation through water splitting under solar irradiation, and the H2 production rate could reach 51.4 mol h−1.206
• A deep understanding of reaction mechanisms and the transfer of electrons between the interfaces could result in significant improvement in the process efficiency. In the future, more significant effort should be put into examining the linkages between the structures, functions, and mechanisms of photocatalytic processes.234 Further other factors of CdS-based photocatalysts also affect the overall activity, such as morphological properties, crystal size, shape, etc. Therefore, more attention should be given to this aspect as these factors are also crucial for controlling and designing of CdS based photocatalytic nanomaterials.
• New strategies must be used to create new CdS-based catalysts, including selective doping, defect engineering, nanostructural modification, increased porosity, conductivity management, and temperature control. Using an alternative way to increase the activity of CdS and CdS-based photocatalysts can be highly beneficial by decorating them with single atoms. The individual atoms may be placed into the CdS layer or onto the interior or exterior of CdS nanorods, nanowires, hollow shells, and nanotubes, resulting in outstanding photocatalytic performance in surface reactions, extensive atomic exploitation, and charge trapping. PDA based surface modification could be promising which also helps in inhibiting photocorrosion.
• The stability of CdS-based photocatalysts is still far from the essential requirement of practical application. The construction of an anti-photocorrosion layer over a CdS photocatalyst and a more effective oxygen separation technology should be the focus of future research to remove nascent oxygen and prevent oxygen-related photocorrosion.235 It has been shown that adding the right dual cocatalysts to CdS and creating heterojunctions can speed up the transfer and migration of photogenerated charge carriers and, to some extent, inhibit the photo-corrosion process.
• There aren't many microscopic investigations of CO2 photoreduction over CdS-based photocatalysts. Theoretical information can be obtained via DFT calculations, an essential academic research tool, to examine the electron excitation process, energy band structure, adsorption properties, and reaction mechanism. Studying the mechanism of CO2 conversion can be aided by examining the adsorption energy of intermediates on photocatalytic materials and the related activation energy.
Furthermore, the study of dimensional anisotropy of CdS-based nanomaterials is a new subject that needs to be explored, since it may offer fresh insight into the formation of the functional heterostructure. These new research directions can increase the photocatalytic efficiencies and therefore the use of CdS-based nanomaterials in photocatalytic processes for energy and environmental applications along with other fields of applications.
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