Functionalized Nanomaterials for Catalytic Application

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With the rapid development in nanotechnology, it is now possible to modulate the physical and chemical properties of nanomaterials with molecular recognition and catalytic functional applications. Such research efforts have resulted in a huge number of catalytic platforms for a broad range of analytes ranging from metal ions, small molecules, ionic liquid and nucleic acids down to proteins. Functionalized nanomaterials (FNMs) have important applications in the environmental, energy and healthcare sectors. Strategies for the synthesis of FNMs have contributed immensely to the textile, construction, cosmetics, biomedical and environmental industries among others.
This book highlights the design of functionalized nanomaterials with respect to recent progress in the industrial arena and their respective applications. It presents an inclusive overview encapsulating FNMs and their applications to give the reader a systematic and coherent picture of nearly all relevant up-to-date advancements. Herein, functionalization techniques and processes are presented to enhance nanomaterials that can substantially affect the performance of procedures already in use and can deliver exciting consumer products to match the current lifestyle of modern society.

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The potent essential energy provides vitamins for our present fast-moving lifestyles for easy and quick mobility together with prosperity [111]. Photocatalytic processes aid in conversion of the powerful solar energy to chemical and thus in degradation of unwanted variables [112–114]. Controllable target-oriented reactions of FMNs photocatalysis are productive, yielding positive segments. FMNs’ photocatalytic mechanistic reactions primarily depend upon the interactions between the light energy and the FMNs in question. The interfaces between the valence band (VB) and conduction band (CB) of a specific band energy initiate the utilization of photocatalytic activity for degrading the active toxins [115]. Generally, photocatalytic FMNs belong to a special group of semiconducting materials with a potency to destroy the organic/inorganic/biological pollutants present persistent in filthy water puddles [116, 117].

Significantly, photocatalytic activity pertains to the absorption of photons by the semiconducting material that initiates the photogeneration of energetic negative (e −) electrons and positive (h +) holes between the CB and VB to begin a photo-redox reaction [118, 119]. The band energy gap is either same or more than that semiconducting material and often is on surface of these conducting materials, to generate highly active surface sites required for photocatalysis [120, 121]. A simple operative module is found to be effective for photocatalysis even in low concentration for semiconducting FNMs. Ample literatures are available for the synthesis of FNM PC and their versatile applications in remediation technologies, where the potency depends on methodologies adopted, morphological size, bandgap energy, effective dose, concentration of contaminant, temperature, and pH [122–124]. Reaction kinetics, parametric thermodynamics, and significant reaction mechanism provide a concrete base for further procedures [125, 126].

Authors Bagheri, S. et al . in their review suggested that one of the major setbacks while using UV light as source in heterogenous semiconductor with single carbon derivative as PC can be overcome by FNMs when employed for water treatment [127]. Photocatalytic activity of NMs is deprived due to reconfiguration of photoelectron. Loss of photoelectrons can be reduced by composites and functionalization of NMs (Pd, Pt, Au, Ag, ZnO, ZnSe, ZnS, Cds, SnO 2, TiO 2, and Fe 2O 3) [128]. Other remarkable introductions to conserve the water bodies using PCs as bifurcated units have been pinned up in segments to come. Similar trials have been unfolded in Table 1.3. Photocatalytic action with plausible mechanism is portrayed in Figure 1.5.

Table 1.3 Photocatalyst (PC) as FNMs.

FNMs as catalyst | Year | Scheme Process Irradiation | Parametric expressions Probe | Solution evolved | Reusable cycles Remarks Ref.
3D-Hem/GH | 2017 Self-assembly Visible light pH (3.82–8.99) | (variable) min. Rh B | MB | 5 Contributors ·O 2−| π - π interaction [185]
MIL-100(Fe)/PANI | 2020 | Z-Scheme Ball-milling White light pH (2–8) | 120 min TC (84%) | Cr (VI) (100%) | 5 Attributors ·OH, ·O 2−| π-conjugation [186]
rGO@ZnO | 2020 Facile synthesis UV light pH (5–9) | 300 min OFX | (99%) | 6 Reactive ( ·O 2−| ·OH), rGO (−4.42 eV) | ZnO (−4.05 eV) [187]
Co-MIL-53-NH-BT | 2020 Hydrothermal | Step-by-step - assembly Visible light | > 400 nm pH (2–8) | 120 min BPA (99.9%) | OFX (99.8%) Activators ·OH + H ++ e −→ H 2O O 2−, ·OH, Co 3+/Co 2+: redox mode [188]
Pt/g-C 3N 4/Bi 2MoO 6| 2019 Hydrothermal Visible light -| 150 min MB (50%) VB (2.34V) | CB (-0.86V) Supporters: ·OH, e −, h +, ·O 2− [189]
Bi-TiO 2NT/graphene NT | 2017 Hydrothermal Visible light -| 60 min MB |Herbicide-Dinoseb | 95% |5 Contributors ·OH [190]
Ni/TiO 2| Ru/TiO 2| 2019 | Sol-gel | Wet-Impregnation Sun light | Visible light pH (natural)| 330 min (IMI) | 480 min (ATP, TMX) IMI | ATP | TMX | 100% (Insecticides) Solar (UV) > visible | Degraded products CO 2| H 2O | ·OH [191]
ZnO/G/TiO 2(ZGT) | 2016 Solvothermal Ultrasonic pH (9) | 120 min MB | TBAC-L | TBBU-L TNFW-L | 4 Contributors: ·O 2−, ·OH | π - π interaction [192]
Zn-TCPP/Ag-TiO 2| 2016 Sol-gel UV | Visible -| 30 min MB | PNP | 4 Enhancer-Porphyrin | 3.28 eV (bandgap) [193]
Bi 2S 3/TiO 2-Mt | 2018 Ion exchange | Impregnation Near UV–Vis-light pH (11) | 120 min KP (80%) | - Langmuir-Hinshelwood | pseudo-1 st-order | ·O 2−| ·OH [194]
3D-g-C 3N 4-NS/TiO 2-NF | 2018 Electrospinning | Thermal redox Visible light >420nm - | 120 min Rh B (~93%) | 3 Activator ·O 2−| pseudo-1 st-order | [195]
FeNi 3@SiO 2@TiO 2| 2018 Sol-gel UV-light pH (9) | 200 min TC (100%) | 5 Contributor ·OH |pseudo-1 st-order | [196]
Co 3O 4/TiO 2/GO/amine | 2017 Sol-gel | Hydrothermal Solar | Visible light - | 90 min | OTC (91%) |CR (91%) |5 Contributors e ·OH, ·O 2−CB, h + VB, − [197]
CuInS 2/Bi 2WO 6| 2019 Hydrothermal Visible light | 120 min TCH (92.4%) | 4 Activators: ·O 2−, ·OH | Z-scheme [198]
3D RGO-based hydrogel Self-assembly | Reduction UV-VIS pH (2/3/(acidic) | 120 min NPX | IBP | DFC | (70-80%) | Langmuir | Freundlich | π-π interaction | pseudo-2 nd-order [199]
CQDs/TCNCs Hydrothermal | Adsorption-polymerization Visible light pH (basic) | 30 min TOC (22%) | CBZ (100 - 87.6%) | 4 5 times > pure TCN | Fukui index ( fo = 0.108) olefinic (double bond) [200]
P M-CQD/TiO 2(M: Ag/Au) Green synthesis | Reduction UV-VIS (MB) | Solar light (Drug) - | 20 min | M: Ag 60 min | M: Au 108 min MB (~96%) | Erythromycin (~100%) | Several Superoxide ·O 2−, | pseudo-1 st-order [201]
BiVO 4/N-CQDs/Ag 3PO 4 Solvothermal precipitation Visible light - | 30 min | 90 min TC (88.9%) | TOC (59.8%) | 5 ·O 2−> h +> ·OH | pseudo-1 st-order | pseudo-2 ndorder | Z-scheme [202]
ZnO/N, S-CQDs | (Capping agent: (Try/Glu)) Hydrothermal Visible |near-IR | Sun-light - | 20–180 min MB | RhB | MG | CEL | CIP (92.9%, 85.8%) | 5 Activator: ·O 2−|pseudo-1 st-order | [203]
3D CQDs/TiO 2/GO - PUF Hydrothermal Visible light - | 1–6 h MB | RhB | 5 Contributors: ·O 2−, ·OH [204]
r-Mg-N-CD Green Synthesis Sun light - | 120 min MB (99.1%) | 4 ·O 2−, h +, ·OH | Langmuir Hinshelwood| 1 st- order [205]
ZnS QD (Capping agent: (L-Cys/2-ME)) Sonochemical | Chemical precipitation UV light 11 | 90 min CV (98.5%, 97.0%) | 5 Langmuir-Hinshelwood | pseudo-1 st-order [206]
f -MWCNTS-CdS QDs | f -MWCNTS-Ag 2S QDs | (Capping agent - PAMAM) Sonochemical | Grafting UV - | 1h MO | - Langmuir-Hinshelwood | 1 st-order rate constant [207]
NH 2-functionalized GQD-TiO 2 Molecular fusion | Hydrothermal Visible light - | 120 min MO (96.0%) | 4 Contributors: h +(44.7%), ·O 2−(38.0%,), ·OH (17.3%) [208]
M-ZnS QDs (M: Cu 2+, Mn 2+, Ag +) Sono assisted | Chemical precipitation UV pH (10.5) | 90 min VBR (> 95%) | 6 Langmuir-Hinshelwood | pseudo-1 st-order [209]
ZnS: Fe QDs (Capping agent: 2-ME) Chemical precipitation UV pH (8.0) | 90 min MG (98%) | 6 Langmuir-Hinshelwood | pseudo-1 st-order [210]

Figure 15 Photocatalytic action with plausible mechanism 151 CarbonBased - фото 6

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