Over the course of time, research on relevance of cleaner fuels, alternate potential energy sources as well as tools to alleviate pollution, have been gainful. Research on visible light photocatalysis over the past decade draws much attention in this line. Semiconductor heterogeneous nanotechnology based photocatalysts lasted long enough and showcased their prominence in this specialty. At present, material chemists are busy preparing competent monometallic or hybrid entities by combining conventional semiconductors with suitable pre-catalyst/co-catalysts to bring about the best results in photocatalysis. Metal NCs have proved their supremacy in multiple economical and sustainable processes of photocatalysis such as photodegradation of organic pollutants, photocatalytic H2 splitting, photoreduction of CO2, oxidation and hydrogenation reactions etc.,
ROS e-/h+ fast recombination of e-/h+ of semiconductors, noble metal/metallic/non-metallic moieties on semiconductors support extending photocatalytic activity towards visible range.
The following section discusses about the role of metal NCs in photocatalytic as cocatalyst as well as catalyst in various light conversion processes.
2.1. Photodegradation of organic pollutants
Globalization led industrialization, to satisfy the needs of world’s population, has led to the steep rise in harmful pollutants in the environment at an alarming rate. The organic pollutants from textile industries majorly constitute azo dyes while inorganic pollutants hold oxidized heavy metals. These under-treated materials containing carcinogenic effluents are being dumped into the soil and water, have already created damages beyond repair to humans as well as to the aquatic flora and fauna. Initiating action plans to safely remove them without the formation of other stable secondary pollutants demanded scrutiny. Methyl Orange (MO), Rhodamine B (RB), Malachite Green (MG) and Methylene blue (MB), some of the commonly found dyes, that have been present in industrial effluents. Reactive oxygen species (ROS) such as superoxide radicals (O
2-.) and hydroxyl radicals (OH
-.) are the prime contributors and starting materials in the degradation of these toxic materials [
86].
Titania (TiO
2), ZnO, SiO
2, Nb
2O
5 and so on have been reported widely as a solution for pollution initiated by organic pollutants through photodegradation [
87,
88]. These semiconductor systems ensure photostability, low cost, mere toxicity and essential level of oxidative ability. However, the disadvantages of these semiconductors remain a barrier to photocatalytic reactions due to the large bandgap that they offer and it indeed requires UV irradiation for the electron-hole generation, this restricts their use as effective catalyst. As the research studies progressed, metal nanoparticle incorporated versions semiconductors became the focal point. Metal NCs linked to semiconductor systems as support have profoundly influenced the works in photocatalytic degradation of cationic and anionic dye pollutants as they could enable us to engineer the bandgap width [
89]
Zhu and co-workers prepared AuNCs coupled with toroid structured per-6-thio-β-cyclodextrins placed on TiO
2 surface (TiO
2-Au NCs@β-CD) provided a better space for the Au cores to interact with the incoming pollutants through a host-guest interaction trap [
90]. This synergistic effect between the nanocluster metallic core, peculiar ligand cavities and support system increased the photodegradation rate of methyl orange (MO) to 98% in 10 minutes. Concurrently, the integrated material’s rate constant values for photodegradation (1st cycle=0.31min-1, 5th cycle= 0.15min-1) was phenomenal in comparison with TiO
2(1st cycle= 0.12min
-1) even after five cycles. Sharma and coworkers studied of Au-TiO
2 conjugated nano assembly were used as light harvester under visible light [
91].
The mechanism for photocatalytic degradation of dyes using Au-TiO2 can explained by following reaction pathways
Au + hν → Au•
Au• + TiO2 → h+(Au) + e-(TiO2)
e-(TiO2) + O2 → TiO2 + •O2-
•O2- + H+ → HOO•
HOO• + e-(TiO2) + H+ → H2O2 + TiO2
H2O2 + e-(TiO2) → •OH + OH- + TiO2
h+(Au) + H2O → Au + H+ + •OH
h+(Au) + OH- → Au + • OH-
Organic pollutants + O2-• or •OH- → CO2 + H2O +….
Gowswami et.al created colloidal nanocomposite material with TiO
2/Nb
2O
5 conjugated to silver NCs with captopril as ligand. They have varied the niobium loading in the incorporated product, to investigate the adhesion of the material towards cationic and anionic dyes as well as their photodegradation capability [
92]. As per the analysis, the mentioned nanocomposite with 48.1% niobium loading and Ag NCs resulted in ternary junction which narrowed down the recombination rates and the surface acidity caused the Ag NCs ligands end groups to polarize COO
-, thereby attracting the cationic dyes for effective 100% degradation with high photostability. Spectroscopic techniques validate the fact that Ag NCs are the reason behind absorption in visible light region and themselves act as oxidative sites, also initiates electron transfer from valence band of the NCs to conduction band of nanocomposites. Samai’s group made polyethelene imine template Ag NCs incorporated with CeO
2 nanoparticle for degrading Acridin Red dye photocatalytically [
93] (
Figure 10). XPS mechanistic work and radical experiments pin down their radical pathway leading to 42% to 80% degradation in 2 hours with 1.07% and 3.10% Ag NCs loading respectively. The reduction potential and two oxidational potential vs NHE values were recorded with Cyclic Voltammogram to be -0.64V, 0.07V and 1.03V respectively (
Figure 10).
ZnO nanoparticle decorated with Ag NCs were established as a prospective candidate for Orange II (OII) dye degradation under both UV and white light by Rodriguez and coworkers [
94]. Atomic Force Microscopy (AFM) confirmed the deposition of NCs moiety on ZnO rather than substitution of metallic core itself. Additionally, the optimal loading range of Ag on ZnO was found to be 1.3% w/w and it certainly ensures ample number of interaction sites for the pollutants to approach ZnO nanoparticles (
Figure 11).
Figure 11 shows the spectroscopic and morphological characterization of AgNC decorated ZnO nanoparticle. Vilar-Vidal et.al formulated green emitting stable closed shell electronic structured and recyclable CuNCs to degrade MB under UV and Visible light irradiation [
95]. UV-Vis data and administered multiple photoluminescence emission peaks were an indication of mixture of clusters and LDI-TOF spectrometry approves proposed structural formulas of Cu NCs: [Cu
18(CH
3COO)(OH)]
-2 and [Cu
34O
2(CH
3COO)
3N(C
4H
9)
3Na]
-2.
Light steered preparation of 3-Mercaptopropyl trimethoxy silane (MPTS) stabilized Au NCs and their performance in photodegradation of MB were examined by Zhou et.al [
96]. It was observed that the nanoclusters decolorizes the dye progressively and color fades completely in 60 mins.
Man Cao and his coworkers synthesized a self-assembled silver nanocluster for photocatalytic degradation of sulphur mustard simulant (2-chloroethyl ethyl sulfide, CEES), a toxic vesicant against human proteins and DNA, can cause skin blisters, eye and respiratory system irritation, and even fatal damage. The silver cluster assembled material is prepared using a photosensitizer (5,10,15,20-tetra(4-pyridyl)porphyrin (TPyP) as the organic linker and which linked with 12-core silver chalcogenolate cluster to form [Ag
12(St Bu)
6(CF
3COO)
3(TPyP)]n, (designated as Ag
12TPyP). They reported 98 % degradation of CEES with 1% loading [
97,
98].
Wen and co-workers developed a highly stable core-shell type catalyst for photo redox reactions. The photostability of nanocluster were improved by loading it on SiO2 sphere by utilizing multifunctional branched poly-ethylenimine (BPEI) as a surface charge modifying, reducing and stabilizing agent. Then TiO
2 were coted SiO
2-Au GSH clusters-BPEI to form SiO
2-Au GSH clusters-BPEI@TiO
2 core- shell structure further significantly improve the photocatalytic efficiency for dye degradation of organic dye (Rh B) [
99].
2.2. Oxidation and hydrogenation processes
Application of NCs on oxidation and reduction processes are still underway. Oxidation and hydrogenation reactions in most reported cases specifically depend on their electronic structures as electron-hole separation remains the key to it. Researchers have carried out typical oxidation-reduction reactions like high selectivity styrene oxidation [
100], aerobic oxidation of amines to imines [
101], cyclohexane or phenol derivatives [
102], water splitting [
103], catalytic hydrogenation [
104], pollutants treatment [
105], in the presence of metal NCs, especially gold NCs (AuNCs). In 1987, Haruta and co-workers were the first to initiate oxidation of CO with few atom AuNCs along with α-Fe
2O
3, NiO and Co
3O
4 at low temperatures[
106]. After two decades, mechanistic view of photocatalysis of Au
25 nanoclusters with TiO
2 as support under visible and near infrared emissions were illustrated by Kogo and co-workers [
107]. They attached AuNCs to TiO
2 so that the excited electrons could be transferred to the conduction band of TiO
2 with ease and can aid in reduction of Ag+ in the counter electrode and the generated holes (h+) could perform oxidation of donors (phenol derivatives or formic acid) in working electrode (
Figure 12).
Similarly, Zhu et.al did a comparative study to figure out the capabilities of a set of superatoms to oxidize styrene- Au
25(SR)
18, Au
38(SR)
24 and Au
144(SR)
60 with diameters of 1nm, 1.3nm and 1.6nm respectively [
108]. However, their studies reassured the size and electronic structure dependence of photocatalytic abilities and Au
25 NCs gave the highest average of ~27 ± 1.0% as smaller the superatom, higher is the HOMO- LUMO gap (1.3eV). Later, Chen & group loaded [Au
25(PPh
3)
10(SR)
5Cl
2] on P
25 to covert benzylamines to imines, TOF was recorded to be 152 2h
-1 for 4-methylbenzamine and other amines too showed appreciable conversions (73-99%) [
101]. The attempts to learn the possible conversion route using Time Dependent Density Functional Theory (TD-DFT) calculations, Fourier-transform ion cyclotron resonance mass spectrometry (FT-IC-MS) with Electrospray ioinization (ESI) and trapping intermediates with scavengers (K
2S
2O
8 and ammonium oxalate) confirmed the presence of +2 charge on the cluster. Hence the photocatalytically induced electron could lead to oxygen radical formation and thereby persuade conversions. Studies with organic supports too have gained momentum over the years. Gold nanocluster with organic supports (Polyvinylpyrrolidone (PVP) & Polyperoxyacetic acid (PAA)) were analyzed by H.Tsunoyama and co-workers and X-ray photoelectron spectroscopy (XPS) & X-ray absorption near edge structure (XANES) reinforced the existence of negatively charged cluster which led to the production of superoxo- or peroxo- radicals required to jump start the photocatalytic reactions [
109]. Their activities and recyclability were keenly observed for CO oxidation. In addition, these set of reactions enlightened research community about the prime role of nanoclusters in oxidation and reduction reactions.
Hamoud and co-workers studied photocatalytic activity Ag NCs encapsulated into zeolite ( ZX-Bi zeolite) for photooxidation of methanol under visible light. They have found that the Ag/ZX-Bi exhibits very low activity, compared to activated sample at 200 °C (Ag/ZX-Bi_200) [
110].
2.3. Photocatalytic H2 production
The demand for green energy sources better suited for the environment is rising due to the reduction and environmental pollution generated by conventional energy resources. While the distinct qualities shape, Hydrogen gas as an acceptable renewable energy source for a sustainable future [
111]. Ahluwalia and coworkers studied the fuel economy of Hydrogen-fuelled fuel cell (H
2-FCV) vehicles and common gasoline-fuelled passenger cars in 2003 [
112]. In 1972, Honda and Fujishima et al. first time discovered that water can be divided into H
2 and O
2 in presence of light. There after various photocatalyst were developed and studied for photocatalytic water splitting reaction. A. Fujishima and K. Honda, Nature, 1972, 238, [
36,
37].
Catalyst based on the metals such as Ti, Cobalt, Nickel, Iron, Molybdenum are widely used for as catalyse for the electrochemical H2 production [
113]. Thereafter, the catalytic efficiency of metal oxides, metal nitrides were enhanced by incorporating suitable cocatalyst on these semiconducting materials. The Co-catalytic activity of metal nanoclusters was studied in the recent past due to its excellent optical, electronic and catalytic activity. The nanoclusters were incorporated into various semiconductors to enhance the catalytic activity by suppressing the electron-hole recombination rate.
Kamat et al studied the photoelectrochemical and photocatalytic production of H
2 using GSH stabilised AuNCs-TiO
2 film hybrid system under visible light irradiation [
113].
Liu et al carried out a detailed investigation on the photocatalytic activity of AuNCs as cocatalyst in highly ordered nanoporous layer-covered TiO
2 nanotube arrays (NP-TNTAs). The photocatalytic activity of NP-TNTAs/AuNCs analysed by monitoring photodegradation of organic dyes, photocatalytic reduction of aromatic nitro compounds and photoelectrochemical water splitting [
114].
The quantum confinement of MNCs enables the charge transfer, easy adsorption and desorption of intermediates and thereby fastens the photocatalytic hydrogen evolution reactions (HER) [
29].
Glutathione stabilised AuNCs (Au
25(SG)
18) were incorporated on BaLa
4Ti
4O
15 used for photocatalytic water splitting. The catalytic activity of sub nanometer sized Au- BaLa4Ti4O15 of compared with larger sized gold nanoparticle and found 2.6 times higher catalytic activity for AuNC composite [
115]. Similarly, AuNCs loaded on SrTiO
3 were studied for HER and found the enhanced catalytic activity of SrTiO3 in presence AuNCs as Cocatalyst [
116]. Recently Hanieh Mousavi and Co-workers studied the photocatalytic production of H2 using AuNCs as Co-catalyst. They have prepared a nanocomposite (Au
101NC-AlSrTiO
3 -rGO) containing AuNCs, RGO and AlSrTiO
3 and the composite showed enhanced photocatalytic water splitting under UV light irradiation [
117].
Sub-nanosized clusters of silver adsorbed on specific sites of Gold nanorods (GNRs) disturb the growth symmetry of Au facets and leads to anisotropy [
118]. In the presence of hole scavenger namely ethanol and in the absence of electron scavengers like O
2, the photoelectrons accumulate in GNRs with Ag clusters. Moreover, on low UV light irradiation, Ag3 clusters at a concentration of 0.43µg within the GNRs shows high H2 production efficiency of 10%. Similarly, loading of 1 wt% of sub- nm Au clusters in CdS uplifts the photocatalytic H2 production about 35 times than the unmodified CdS under visible light [
119]. The comparison of sub-nm Au loaded CdS with Pd/CdS and Rh/CdS of similar size revealed that the 3-nm sized Au/CdS as a better co-catalyst.
Likewise monolayer niobate (HTi
2NbO
7) nanosheets with Pt nanoclusters proved themselves as potential photocatalysts for high H2 production [
120]. Monolayer niobate nanosheets enable the charge separation between photoelectron and holes and displays 5 times higher photocatalytic H
2 production than that observed in its layered form. 1 wt% Pt nanoclusters loaded to niobate nanosheets via photoreduction presented increased activity due to the close contact between the HTi
2NbO
7 nanosheets and Pt nanocluster. On light irradiation electrons migrated to the conduction band moves to surface of nanosheets. Since Pt have a higher work function than niobate nanosheets, these electrons in the surface of nanosheets transfers to Pt and form H
2.
Moreover, by monitoring nanocluster size, the photocatalytic activity of the whole system can be varied. Heiz, Feldmann and co-workers modified cadmium sulfide (CdS) nanorod with a series of Pt NCs such as Pt
8NC, Pt
22NC, Pt
34NC, Pt
46NC, Pt
68NC and found that, Pt
46/CdS exhibits the highest activity for photocatalytic water splitting, due to the well-known quantum confinement effect., were the bandgap increases with a decrease of the NC size [
121]. Rongchao Jin and his coworkers reported a detailed review on the effect of size of nanocluster in photocatalysis [
122] While Cheng and co-workers[
118] revealed the effective co-catalytic effect of sub nano sized Pt-Au alloy clusters in photocatalytic H2 evolution. The synergistic effect of 0.5 wt% of both Pt and Au clusters dispersed in TiO
2 (Pt-Au/T) creates increased charge separation and 80.1 µmol h
-1 of H
2 is evolved with a quantum efficiency 50% at 365nm. As like HER, similar strategy have been established for enhanced efficiency for OER, by using nanocluster as cocatalyst [
123]. Au
25 NC- CoSe
2 composite were studied for OER activity found enhanced OER activity in presence of Au
25/CoSe
2 obtained current density of 10 mA cm
–2 at small overpotential of ∼0.43 V (cf. CoSe
2: ∼0.52 V). The ligand and gold cluster size can also tune the catalytic performance of the composites.
The photocatalytic activity of Co-catalyst was studied by monitoring doping of heteroatom on the nanoclusters. Negishi et al. demonstrated that doping of Pt on Au
25 NC enhances the water splitting activity, while Pd doping reduces the water splitting activity. They proposed that the doping position plays the role in the catalytic activity. The doped Pd is located at the surface of the metal-cluster cocatalyst, whereas Pt is located at the interface between the metal-cluster cocatalyst and the photocatalyst [
124]. Yang et al. also illustrated the effect of heteroatom doping on the photocatalytic activity of PtAg
24-loaded graphitic carbon nitride (PtAg
24/g-C
3N
4) and found that PtAg
24/g-C
3N
4 shows higher efficiency for photocatalytic H
2 production than Ag
25/g-C
3N
4 alone [
125]. In addition to the above studies, scientist are exploring the efficiency of photocatalytic water using composites including metal NCs with g-C
3N
4 nanosheets,TiO
2, etc [
126].
2.4. Photocatalytic CO2 reduction
Nowadays, reducing greenhouse gas emissions from various Photovoltaic (PV) systems has become one of the scientific community's primary concerns [
127]. Carbon dioxide is one of the chief greenhouse gases that influence the heat content of earth’s atmosphere [
1]. With a focus on reducing carbon dioxide emission, novel technologies are adopted for the production of commodity chemicals by using carbon dioxide as feedstock [
128].The conversion of carbon dioxide to value-added chemicals or to other hydrocarbon fuels such as methane, ethylene and carbon monoxide by utilizing energy from non-fossil resources such as solar energy not only increases the carbon recycling but also assists in fuel production [
129,
130]. Solar-driven transformation of carbon dioxide to useful products could be achieved through two major approaches such as photocatalytic and electrochemical CO2 reduction processes [
131]. In 1978, M. Halmann utilized p-type semiconductors for photo-electrochemical reduction of carbon dioxide [
132]. Methanol and Carbon monoxide obtained from the conversion of carbon dioxide are identified as useful feedstocks [
133]. The former is utilized for synthesising other hydrocarbon fuels while latter is used for Fischer–Tropsch syntheses.
CO2 is a thermodynamically stable molecule and catalysts assist the electrochemical CO2 reduction reactions and aid in achieving desired product [
134]. MNCs possess ultrafine structure, electronic and optical properties [
34] and function both as electrocatalyst and photocatalysts [
27]. Various features of MNCs such as size, core, composition, surface ligands, charge state, geometry influences its electro and photocatalytic behaviors [
27]. Colombo Jr and coworkers studied femtosecond electron-hole recombination in TiO2- nanoclusters and explained the intracluster dynamics [
135]. The study demonstrates the steps involved in electron trapping, recombination and formation of long-lived species. Kauffman et. al studied the reversible weak interaction between CO
2 and Au
25(SC
2H
4Ph)
18- clusters [
136]. The electrochemical reduction of CO
2 using Au
25 catalyst in aqueous 0.1 M KHCO
3 showed maximum CO production at -1.0 V with 100% Faradaic efficiency. The electrochemical CO
2 reduction performance of silver nanoclusters confined in bovine serum albumin (AgNC@BSA) is enhanced via polyoxometalates [α-SiW
12O
40]
4- [
137].
The presence of suitable photocatalyst possessing features such as high light absorptive power, convenient catalytic sites and low activation energy enhances the photocatalytic reduction of CO2 [
138]. The small-scale size of MNCs of about 2nm, interfacial surface, energy gap, tunable chemical properties, quantum confinement are the advantages of ultrafine MNCs for CO
2 reduction over metal nanoparticles [
139]. Titanium dioxides or titania are widely used semiconductors and have broad range of applications including photoreduction of CO
2 [
140]. Doping and decoration with other elements or metal ions strengthens its photocatalytic activity by reducing its band gap. In addition to these elements, attaching nanoclusters to TiO
2 makes it a potent visible light photocatalyst [
141]. Inserting Ti3+ ions into the TiO
2 creates isolated states in the presence of UV and visible light. The electrons are trapped in these states and due to recombination with charge carriers’ photocatalytic activity is decreased. On combining Ti
3+ introduced TiO
2 with nanoclusters of Cu (II) oxides (i.e., Cu (II)-TiO
2@Ti
3+), electrons from the isolated states of Ti
3+ moves to surface of Cu (II) nanoclusters. Hence, the photocatalytic activity of Cu (II)-TiO
2@Ti
3+ under visible light is raised and decomposed gaseous 2-propanol (IPA) completely to yield ~18 µmol CO
2 generation. On UV irradiation, copper oxide (CuxO) nanoclusters incorporated in strontium titanate nanorod thin film [
142] and niobate sheets [
143] showed selective CO production form photocatalytic CO
2 reduction.
Product selectivity towards CH
4 and CO is shown by brookite TiO
2 quasi nanocubes (BTN) on surface decoration with Cu-nanoclusters (Cu-BTN) under xenon lamp irradiation [
144]. XRD diffraction peaks exhibits the presence of Cu-nanoclusters only on the surface of BTN. The total consumed electron number (TCEN) is utilized for examining overall photocatalytic CO
2 reduction. At a 1.5 % optimum concentration of Cu-nanoclusters in BTN, maximum photoactivity with TCEN of 150.9 µmolg
-1h
-1 and highest production rate of 4.23 µmolg
-1h
-1 CO and 17.81 µmolg
-1h
-1 CH
4 is observed (
Figure 13).
In situ DRIFTS IR spectra suggested CO
32- intermediate for CO formation and HCO
3- for CH
4 (
Figure 14a). Cui at.el worked on the role of bridging ligand and metal ions grafted to Au nanoclusters in photocatalytic conversion of CO
2 to CO [
145]. The functionalization of L-cysteine with glutathione protected Au nanocluster (Au-GSH NCs) helps in binding of metal cations such as Fe
2+ Co
2+ Ni
2+ and Cu
2+ and thus improves the selective CO production. Under visible light along with CO
2 and H
2O, Co
2+ cation within Au nanocluster (Auc-C-Co) at optimum concentration of 4 µmol exhibited maximum CO production of 3.45 µmol.gcat
-1h
-1. Similarly, via 3-mercaptopropionic acid (MPA), Co
2+ is grafted to surface of Au nanocluster (Au
c-MPA-Co) and exhibited high-rise in photocatalytic activity compared to (Au
c-C-Co) through strong interlinkage between S-metal cation (
Figure 15).
Zhang and co-workers [
143] developed a quasi-ternary complex consisting of polymethacrylic acid stabilized Ag nanoclusters (AgNCs-PMAA), carbon monoxide dehydrogenase (CODH) and TiO
2 nanoparticles and under visible light CO2 reduction results generation of CO with 20 s
-1 turnover frequency at 25℃ . Jiang, Y et. al [
146] upgraded the chemical stability of gold nanoclusters (Au-NCs) by combining with metal organic framework (UiO-68) through N-Heterocyclic carbene stabilizing ligands (NHC) and denoted as AuNC@UiO-68-NHC. The photocatalytic activity AuNC@UiO-68-NHC is observed to be enhanced as a result of strong covalent bond formation between AuNCs and UiO-68 facilitated by Au-NHC bridges. This enabled easy movement of excited electrons from the Fermi levels of Au-NCs to conduction band of UiO-68-NHC and thus the recombination of photogenerated electrons and holes are reduced (
Figure 16) [
146].
The selective production of CO and presence of CH
4 and H
2 as side product is observed. Billo and coworkers developed effective photocatalyst with dual sites by making oxygen vacancies in Ni-nanoclusters loaded in black TiO
2 (Ni/TiO
2[Vo]) [
147]. Ni and oxygen defective sites acts as dual sites, lessen the C-O bond strength and supports the separation of charge carriers (
Figure 17). On light irradiation from halogen lamp, Ni/TiO2[Vo] produced 10 µmol.g-cat-1 of acetaldehyde which is 18 times higher than TiO
2. Thus the study refers to a different approach for enhancing photocatalytic CO
2 reduction by introducing active dual sites in photocatalyst.
Recently, Mohamad El-Roz et al de prepared a silver nanocluster-based catalyst for the conversion of formic acid to CO2 and H2 under visible light irradiation. Here the nanocluster was incorporated into nano sized zeolite crystal 145.
Table 1.
Summary of Literature Reports on the use of nanocluster in Catalysis.
Table 1.
Summary of Literature Reports on the use of nanocluster in Catalysis.
Sl No |
Photocatalyst |
Co catalyst |
Application |
Efficiency |
Reference |
1 |
TiO2
|
AuNC |
Photodegradation of dyes |
98% degradation in 10 minutes exposure. |
[90] |
2 |
TiO2/Nb2O5
|
AgNC |
Photodegradation of dyes. |
100% degradation |
[92] |
3 |
CeO2
|
AgNC |
Photodegradation of dyes. |
80% degradation in 2 hours |
[93] |
4 |
ZnO nanoparticle |
AgNC |
Photodegradation of dyes. |
100% degradation in 1 hr |
[94] |
5 |
CuNC |
No Cocatalyst |
Photodegradation of dyes. |
100% degradation in 1 69hr |
[95] |
6 |
AuNC |
No cocatalyst |
Photodegradation of dyes. |
100% degradation in 1 hr |
[96] |
7 |
AgNC-assembled materials |
No cocatalyst |
Photodegradation of dyes. |
98% degradation |
[98] |
8 |
TiO2 core- shell |
SiO2-Au GSH clusters |
Photodegradation of organic dyes. |
99.1% degradation in 0.5 hr |
[99] |
9 |
TiO2
|
Au25 NC |
Oxidation of phenol derivatives and ferrocyanide and reduction of Ag+, Cu2+ and oxygen |
|
[107] |
10 |
Au25NC |
No Catalyst |
oxidation of styrene and hydrogenation of α,β-unsaturated ketone |
27 ± 1.0% |
[108] |
11 |
TiO2
|
AuNC |
Oxidation of benzylamines to imines |
73-99% |
[101] |
12 |
Zeolite (ZX-Bi zeolite) |
Ag NC |
Photooxidation of methanol |
49.60 mmol·g–1·cm–2 after 12 h of reaction |
[110] |
13 |
TiO2
|
AuNC |
Production of H2 |
0.3 mmol of hydrogen/h/g |
[148] |
14 |
TiO2 nanotube arrays (NP-TNTAs). |
AuNC |
Photodegradation of organic dyes, photocatalytic reduction of aromatic nitro compounds and photoelectrochemical water splitting. |
|
[114] |
15 |
BaLa4Ti4O15
|
AuNCs |
Photocatalytic water splitting |
190 µmol/h |
[115] |
16 |
SrTiO3
|
AuNC |
Hydrogen evolution reaction |
41.2 µmol/h of H |
[116] |
17 |
AlSrTiO3 and rGO |
AuNCs |
photocatalytic production of H2, photocatalytic water splitting |
385 ± 22 nmol h−1
|
[117] |
18 |
Gold nanorods (GNRs) |
AgNCs |
Hydrogen evolution reaction |
10% |
[118] |
19 |
Monolayer niobate (HTi2NbO7) |
Pt NC |
Higher H2 production |
10 μmol h−1
|
[120] |
20 |
Modified cadmium sulfide (CdS) nanorod |
Pt NC |
Photocatalytic water splitting |
1.5‰ h−1
|
[121] |
21 |
BaLa4Ti4O15
|
Au24Pd NCs and Au24Pt NCs |
photocatalytic H2 evolution |
100-150 µmolh-1
|
[124] |
22 |
Graphitic carbon nitride (g-C3N4) |
PtAg NC |
photocatalytic H2 production |
39.7 µmolh-1
|
[125] |
23 |
Brookite TiO2 quasi nanocubes |
CuNCS |
Photocatalytic CO2 reduction |
150.9 μmol g−1 h−1
|
[144] |
24 |
Metal cations -Fe2+, Co2+, Ni2+ and Cu2+ |
Au NCs |
Photocatalytic CO2 reduction |
3.54 µmol⋅gcat−1⋅h−1
|
[145] |
25 |
carbon monoxide dehydrogenase (CODH) and TiO2 nanoparticles |
Ag NC |
Photocatalytic CO2 reduction |
turnover frequency of 20 s−1
|
[149] |
26 |
Au-NCs |
|
Photocatalytic CO2 reduction |
57.6 μmol g-1h-1
|
[146] |
27 |
TiO2
|
Ni-NCs |
photocatalytic CO2 reduction |
10 µmol g-cat−1
|
[147] |
28 |
AgNC |
No Cocatalyst |
reforming of formic acid to H2 and CO2 |
99% selectivity |
[150] |