| Literature DB >> 35910153 |
Soorya Sasi1, Akash Chandran2, Sunish K Sugunan3, Ardra C Krishna2, Pankajakshan Radhakrishnan Nair1, Aneena Peter2, Arsha N Shaji2, Kavasseri R V Subramanian4, Narendra Pai5, Suresh Mathew1,2.
Abstract
TiO2 nanoparticles surface-modified with silane moieties, which can be directly coated on a flexible substrate without the requirement of any binder materials and postsintering processes, are synthesized and characterized using X-ray diffraction, Fourier transform infrared spectroscopy, scanning electron microscopy, Brunauer-Emmett-Teller, X-ray photoelectron spectroscopy, Raman spectroscopy, photoluminescence spectroscopy, time-correlated single-photon counting, and transmission electron microscopy. The viability of the prepared surface-modified TiO2 (M-TiO2) sheets as a catalyst for the photo-induced degradation of a model dye, methylene blue, was checked using UV-visible absorption spectroscopy. The data suggest that, compared to unmodified TiO2, M-TiO2 sheets facilitate better dye-degradation, which leads to a remarkable photocatalytic activity that results in more than 95% degradation of the dye in the first 10 min and more than 99% of the degradation in the first 50 min of the photocatalytic experiments. We also demonstrate that M-TiO2 can be recycled with negligible reduction in photocatalytic activity. Further, the photovoltaic properties of the developed M-TiO2 sheets were assessed using UV-visible absorption spectroscopy, electrochemical impedance spectroscopy (EIS), and photochronoamperometry. Dye-sensitized solar cells (DSSC) fabricated using M-TiO2 as the photoanode exhibited a photoconversion efficiency of 4.1% under direct sunlight. These experiments suggested that M-TiO2 sheets show enhanced photovoltaic properties compared to unmodified TiO2 sheets, and that, when N-719 dye is incorporated, the dye-TiO2 interaction is more favorable for M-TiO2 than bare TiO2. The simple solution processing method demonstrated in this paper rendered a highly flexible photoanode made of M-TiO2 with superior charge-separation efficiency to an electrode made of bare TiO2. We propose that our findings on the photovoltaic properties of M-TiO2 open up arenas of further improvement and a wide scope for the large-scale production of flexible DSSCs on plastic substrates at room temperature in a cost-effective way.Entities:
Year: 2022 PMID: 35910153 PMCID: PMC9330195 DOI: 10.1021/acsomega.2c01425
Source DB: PubMed Journal: ACS Omega ISSN: 2470-1343
Summary of Silane-Modified TiO2 in Photocatalytic Wastewater Treatment and Environmental Applications
| coupling agent used | model pollutant | remarks | refs. no |
|---|---|---|---|
| APTES | Cr(VI) | pH plays a crucial role in the absorption of chromium. Optimization of pH, contact time, and concentration leads to maximum absorption | ( |
| APTES | MB | calcination plays a key role in tuning the photocatalytic ability of the silane-coupled TiO2 photocatalyst. The calcination changed the zeta potential of the modified TiO2 photocatalyst. Calcination above 300 °C increased the photocatalytic ability and stability of the material | ( |
| APTES | MB, orange II | the adsorption has a significant
impact on the photooxidation of dyes. The APTES/TiO2 photocatalysts calcined at 900 °C showed high degradation rates. Functionalization | ( |
| APTES | MB | the presence of Si and C in the APTES-modified TiO2 contributed to effective inhibition of the anatase-to-rutile phase transformation and the growth of the crystallite size of both polymorphous forms of TiO2 during calcination at high temperature | ( |
| vinyltriacetoxysilane | rhodamine B | a large amount of modifier in the silane-modified TiO2 reduced the photocatalytic ability of the TiO2 | ( |
| octadecyl trichlorosilane | rhodamine B | in the case of modified TiO2, a direct electron transfer to the conduction band of TiO2 upon absorption of UV light was facilitated by the organic chain with an optimum length | ( |
| APTES, 3-isocyanato propyl trimethoxy silane (IPTMS) | malachite green | a high silane modifier concentration negatively affected the photocatalytic ability | ( |
| propyltrimethoxysilane, triethoxy(octadecyl)silane, trimethylchlorosilane | nitric oxide | silane-modified TiO2 paint showed significant improvement in NO reduction than that of the unmodified sample and showed good self-cleaning properties | ( |
| γ-aminopropyltriethoxy silane (APTES), γ-amino propyltrimethoxy
silane (APTMS), | brilliant red X-3B | the degradation of the dye was 96.4% after 180 min of light irradiation. Doping of Si into the TiO2 effectively delayed the anatase-to-rutile phase transition, prevented the growth of titania grains, and increased surface area and UV light-induced photocatalytic activity | ( |
| 3–9(trimethoxysilyl)propylmethacrylate (KH570) | heavy metals, phenol, polybrominated diphenyl ethers (PBDEs) | Degradation of the dye was observed at 93% after 4 h of irradiation. Due to the self-condensation effect of the silane modifier, a considerable amount of silicon hydroxyl was provided as the hole trapping agent, thus improving the ability of the catalyst | ( |
| APTES | heavy metals like Cu2+, Cd2+, and Pb2+ | Adsorption capacities of APTES-modified hollow TiO2 nanospheres for Cu2+, Cd2+, and Pb2+ ions were found to be 12.7, 17.5, and 1.8 times more than those of unmodified samples respectively | ( |
Figure 1(A) M-TiO2 coated PET sheet bent and immersed in dye solution before and (B) after the dye degradation.
Figure 2(A) As prepared M-TiO2 coated ITO sheets and (B) after N-719 dye adsorption.
Figure 3XRD comparison of unmodified TiO2 (red curve) and M-TiO2 (black curve).
Figure 4TEM images of TiO2 (A–C) and M-TiO2 (D–F). (A,B) TEM images of TiO2 with different magnifications; (C) HRTEM image of TiO2, and inset of (C) is the SAED pattern of TiO2. (D,E) TEM images of M-TiO2 with different magnifications, (F) HRTEM image of M-TiO2, and inset of (F) is the SAED pattern of M-TiO2.
Figure 5X-ray photoelectron spectroscopy (XPS) spectrum of M-TiO2. (A) Wide spectrum, Core level spectra of (B) Si 2p, (C) C 1s, (D) Ti 2p, and (E) O 1s.
Figure 6(A) Absorption spectra and (B) Tauc plot comparison of TiO2, I-TiO2, and M-TiO2.
Figure 7(A) C/C0vs Time graph of TiO2 and M-TiO2, (B) percentage of degradation of the same after 10 min of irradiation.
Figure 8(A) C/C0vs time graph of M-TiO2 for four consecutive cycles and (B) pictorial representation of recycling using a flexible M-TiO2 sheet.
Figure 9Photo chronoamperometry curve comparison of N719 dye-adsorbed TiO2 and M-TiO2.
Figure 10(A) IV characteristics of DSSCs measured with different electrolyte and dye combinations under AM 1.5 light conditions (B) I–V measurement of the best-performing device (N719–I3–/I–) measured under direct sunlight conditions (with a device structure of ITO-N719 dye-adsorbed TiO2 photoanode–I3–/I– electrolyte–Pt counter electrode).
I–V Measurement Results Comparison of DSSCs
| DSSC | fill-factor | η (%) | ||
|---|---|---|---|---|
| N749–I3–/I– | 4.4 | 0.31 | 0.50 | 0.7 |
| N749–Co(II)/Co(III) | 0.5 | 0.67 | 0.82 | 0.28 |
| N719–I3–/I– | 3.0 | 0.58 | 0.63 | 1.1 |
| N719–Co(II)/Co(III) | 0.8 | 0.46 | 1.02 | 0.41 |