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Keywords = photocatalytic degradation

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32 pages, 44965 KiB  
Article
Hybrid Cellulosic Substrates Impregnated with Meta-PBI-Stabilized Carbon Nanotubes/Plant Extract-Synthesized Zinc Oxide—Antibacterial and Photocatalytic Dye Degradation Study
by Hristo Penchev, Katerina Zaharieva, Silvia Dimova, Georgy Grancharov, Petar D. Petrov, Maria Shipochka, Ognian Dimitrov, Irina Lazarkevich, Stephan Engibarov and Rumyana Eneva
Nanomaterials 2024, 14(16), 1346; https://doi.org/10.3390/nano14161346 (registering DOI) - 14 Aug 2024
Abstract
Novel fibrous cellulosic substrates impregnated with meta-polybenzimidazole (PBI)-stabilized carbon nanotubes/zinc oxide with different weight content of ZnO and with the use of dimethylacetamide as dispersant media. The pristine ZnO nanoparticle powder was prepared by plant extract-mediated synthesis using Vaccinium vitis-idaea L. The green [...] Read more.
Novel fibrous cellulosic substrates impregnated with meta-polybenzimidazole (PBI)-stabilized carbon nanotubes/zinc oxide with different weight content of ZnO and with the use of dimethylacetamide as dispersant media. The pristine ZnO nanoparticle powder was prepared by plant extract-mediated synthesis using Vaccinium vitis-idaea L. The green synthesized ZnO possesses an average crystallite size of 15 nm. The formation of agglomerates from ZnO NPs with size 250 nm–350 nm in the m-PBI@CNTs/ZnO was determined. The prepared materials were investigated by PXRD analysis, XPS, SEM, EDS, AFM, and TEM in order to establish the phase and surface composition, structure, and morphology of the hybrids. The potential of the synthesized hybrid composites to degrade methylene blue (MB) dye as a model contaminant in aqueous solutions under UV illumination was studied. The photocatalytic results show that in the course of the photocatalytic reaction, the m-PBI@CNTs/ZnO 1:3 photocatalyst leads to the highest degree of degradation of the methylene blue dye (67%) in comparison with the other two studied m-PBI@CNTs/ZnO 1:1 and 1:2 composites (48% and 41%). The antibacterial activity of ZnO nanoparticles and the hybrid CNT materials was evaluated by the RMDA and the dynamic contact method, respectively. The profound antibacterial effect of the m-PBI@CNTs/ZnO hybrids was monitored for 120 h of exposition in dark and UV illumination regimes. The photocatalytic property of ZnO nanoparticles significantly shortens the time for bactericidal action of the composites in both regimes. The m-PBI@CNTs/ZnO 1:2 combination achieved complete elimination of 5.105 CFU/mL E. coli cells after 10 min of UV irradiation. Full article
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Figure 1

Figure 1
<p>Schematic representation of m-PBI surface wrapping stabilization of MWCNTs. Pictures of the hybrid dispersions from left to right: pristine ZnO NPs dispersed in DMAc; m-PBI@ZnO; m-PBI@CNTs; m-PBI@CNTs/ZnO 1:1 and m-PBI@CNTs/ZnO 3:1 (<b>A</b>); time stability comparison of the bare plant extract ZnO NPs and m-PBI@ZnO dispersions in DMAc before (left) and after 60 min stay (right) (<b>B</b>).</p>
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<p>Size distribution plot of PBI-modified MWCNTs dispersions in DMAc (<b>A</b>). Size distribution plots of PBI-modified MWCNTs/ZnO dispersions in DMAA at different CNTs/ZnO mass ratios (<b>B</b>).</p>
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<p>Digital pictures of 1 mL free drop spread of m-PBI@CNT and m-PBI@CNTs/ZnO 1:1 suspensions (<b>top</b>) and light microscopy pictures of these two dispersions after 1 mL deposition onto cellulose filter substrate (<b>bottom</b>).</p>
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<p>PXRD patterns of green synthesized ZnO, m-PBI/CNTs, and m-PBI@CNTs/ZnO 1:3.</p>
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<p>Deconvoluted photoelectron spectra of C1s, O1s, and N1s and core level spectra of Zn2p and ZnLMM of m-PBI/ZnO; m-PBI/CNTs; m-PBI@CNTs/ZnO 1:1; and m-PBI@CNTs/ZnO 1:3.</p>
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<p>SEM images of microfibrous cellulose substrates impregnated with (<b>A</b>) m-PBI@CNTs; (<b>B</b>) m-PBI@CNTs/ZnO 1:1; (<b>C</b>) m-PBI@CNTs/ZnO 1:2; and (<b>D</b>) m-PBI@CNTs/ZnO 1:3.</p>
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<p>EDS mapping of cellulose substrate impregnated with m-PBI@CNTs/ZnO 1:1 (<b>A</b>); m-PBI@CNTs/ZnO 1:2 (<b>B</b>); and m-PBI@CNTs/ZnO 1:3 (<b>C</b>).</p>
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<p>EDS mapping of cellulose substrate impregnated with m-PBI@CNTs/ZnO 1:1 (<b>A</b>); m-PBI@CNTs/ZnO 1:2 (<b>B</b>); and m-PBI@CNTs/ZnO 1:3 (<b>C</b>).</p>
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<p>EDS spectra of m-PBI/CNTs, m-PBI@CNTs/ZnO 1:1, PBI@CNTs/ZnO 1:2, and m-PBI@CNTs/ZnO 1:3.</p>
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<p>(<b>A</b>) AFM 2D image of CNTs; (<b>B</b>) AFM 3D image of CNTs; (<b>C</b>) AFM 2D image of green synthesized ZnO nanoparticles; (<b>D</b>) AFM 3D image of green synthesized ZnO nanoparticles; (<b>E</b>) AFM 2D image of m-PBI/ZnO; (<b>F</b>) AFM 3D image of m-PBI/ZnO; (<b>G</b>) AFM 2D image of m-PBI@CNTs/ZnO; (<b>H</b>) AFM 3D image of m-CNTs/ZnO.</p>
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<p>TEM images of (<b>A</b>) green synthesized ZnO nanoparticles; (<b>B</b>) m-PBI/ZnO; (<b>C</b>) m-PBI/CNTs; (<b>D</b>) m-PBI@CNTs/ZnO 1:1; and (<b>E</b>) m-PBI@CNTs/ZnO 1:3.</p>
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<p>HR TEM images of images of green synthesized ZnO nanoparticles (<b>A</b>). m-PBI@CNTs hybrid (<b>B</b>).</p>
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<p>HR TEM images of images of green synthesized ZnO nanoparticles (<b>A</b>). m-PBI@CNTs hybrid (<b>B</b>).</p>
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<p>Digital pictures of preliminary experiment for 15 min UV light illumination of hybrid catalytic m-PBI@CNT/ZnO 1:1 cellulose substrate in contact with diluted MB solution.</p>
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<p>(<b>a</b>) The concentration ratio C/C<sub>0</sub> and (<b>b</b>) degree of degradation of Methylene Blue dye with time of UV illumination using prepared hybrid materials as photocatalysts.</p>
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<p>(<b>a</b>) The concentration ratio C/C<sub>0</sub> and (<b>b</b>) degree of degradation of Methylene Blue dye with time of UV illumination using m-PBI/ZnO and bare green synthesized ZnO as photocatalysts.</p>
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<p>(<b>a</b>) The concentration ratio C/C<sub>0</sub> and (<b>b</b>) degree of degradation of Methylene Blue dye with time of UV illumination using prepared hybrid materials as photocatalysts in the presence of H<sub>2</sub>O<sub>2</sub>.</p>
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<p>Degree of degradation of MB dye after 180 min under UV light using (<b>a</b>) m-PBI@CNTs/ZnO 1:2; (<b>b</b>) m-PBI@CNTs/ZnO 1:1; and (<b>c</b>) m-PBI@CNTs/ZnO 1:3 photocatalysts in three photocatalytic runs.</p>
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<p>RMDA method for evaluation of MIC in 96-well plate. Wells in the rectangles are inoculated with a bacterial culture of 5 × 10<sup>5</sup> CFU/mL. (<b>a</b>) MIC of MWCNTs, lines A, B: a sector from 96-well plate kept in static condition. Lines F–H: a sector from another 96-well plate incubated on a wrist shaker. Legend between B and F lines shows the concentration of MWCNTs in each column of wells. Well G12—positive control. (<b>b</b>) MIC of ZnO nanoparticles, column 6: positive control, column 10: control wells of resazurin dye for each ZnO concentration.</p>
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<p>ASTM Standard Test Method E 2149–10. Data are presented as lg of the CFU/mL. (<b>a</b>,<b>b</b>) Antibacterial effect of the tested hybrid materials, their constituents, and combinations of constituents tested on <span class="html-italic">E. coli</span>. © Effect of the combination of cellulose and PBIs, tested on <span class="html-italic">B. subtilis</span>.</p>
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<p>(<b>a</b>). Effect of UV irradiation on standard <span class="html-italic">E. coli</span> suspension with 0.5 mg/mL ZnO NPs. Samples were taken before the 15′ incubation in the dark, at the start of UV irradiation, and at 10′, 20′, and 30′: (1) a beaker irradiated with UV light; (2) a beaker kept in the dark throughout the whole experiment; (<b>b</b>) effect of the tested hybrid materials: left—without irradiation; right—after UV irradiation; K—control, 1—Cell/PBI, 2—Cell/PBI/ZnO, 3—Cell/PBI@CNT, 4—Cell/PBI@CNT/ZnO 1:1, 5—Cell/PBI@CNT/ZnO 1:2, 6—Cell/PBI@CNT/ZnO 1:3. Sample 5 displays bactericidal effect.</p>
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<p>SEM images of the hybrid material Cell/PBI@CNT incubated with <span class="html-italic">E. coli</span> suspension overnight. Putative effusions of cell contents are indicated by arrows. Areas marked in rectangles were observed at higher magnification and shown below: (<b>a</b>) a specimen kept in the dark; (<b>b</b>) a specimen irradiated by UV light.</p>
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18 pages, 9848 KiB  
Article
Degradation of Methyl Orange from Aqueous Solution Using Fe-Ni-Co-Based Trimetallic Nanocomposites: Optimization by Response Surface Methodology
by Areeba Riaz, Bibi Saba Ibrar, Khansa Bibi, Zunaira Habib, Sadaf Ikram, Hafiz Muhammad Aamir Shahzad, Pin Zhao and Zahra Zahra
Sustainability 2024, 16(16), 6958; https://doi.org/10.3390/su16166958 - 14 Aug 2024
Abstract
Effluent-containing dye molecules is a significant environmental hazard. An economical and energy-saving solution is needed to combat this issue for the purpose of environmental sustainability. In this study, Fe-Ni-Co-based trimetallic nanocomposite was synthesized using the coprecipitation method. Scanning Electron Microscopy (SEM), X-ray diffraction [...] Read more.
Effluent-containing dye molecules is a significant environmental hazard. An economical and energy-saving solution is needed to combat this issue for the purpose of environmental sustainability. In this study, Fe-Ni-Co-based trimetallic nanocomposite was synthesized using the coprecipitation method. Scanning Electron Microscopy (SEM), X-ray diffraction (XRD), and Fourier Transform Infra-Red spectroscopy were conducted to explore the physical morphology, phase structure and functional groups of the synthesized catalyst. Among dyes, methyl orange is considered as a major contaminant in textile effluent. The current study focused on the degradation of methyl orange using a trimetallic Fe-Ni-Co-based nanocomposite. A central composite design in response surface methodology was employed to analyze the independent variables including dye concentration, catalyst dose, temperature, hydrogen peroxide, irradiation time, and pH. Dye degradation has been achieved up to 81% in 20 min at the lowest initial concentration (5 mg/L) in optimized conditions. Based on ANOVA, the predicted values were in great agreement with the actual values, signifying the applicability of response surface methodology in the photocatalytic decolorization of dyeing effluents. The results gained from this research demonstrated that the synthesis method of trimetallic nanocomposite (Iron Triad) is a cost-effective and energy efficient method that can be scaled up to a higher level for industrial application. Full article
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Figure 1
<p>Synthesis of Fe-Ni-Co nanocomposite.</p>
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<p>SEM images of trimetallic nanocomposites at different magnification (<b>a</b>) 200 µm, (<b>b</b>) 100 µm, (<b>c</b>) 5 µm and (<b>d</b>) 1 µm.</p>
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<p>(<b>a</b>) The EDS-layered image shows the uniform distribution of the metals Fe, Ni and Co in nanocomposites. The separate diagram for each element including Fe, Ni, and Co is shown in (<b>b</b>), (<b>c</b>) and (<b>d</b>), respectively. (<b>e</b>) shows the EDS spectra and (<b>f</b>) illustrates the composition of the trimetallic nanocomposite.</p>
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<p>XRD pattern of trimetallic (Fe-Ni-Co) nanocomposite.</p>
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<p>FTIR spectra of trimetallic nanocomposite (<b>a</b>) and expended FTIR spectral region from 800 to 400 cm<sup>−1</sup> (<b>b</b>).</p>
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<p>Schematic overview of photocatalysis.</p>
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<p>RSM plots showing the percentage degradation of MO and the interaction between selected variables. (<b>a</b>) The effect of dye concentration and time; (<b>b</b>) the effect of dye concentration and pH; (<b>c</b>) effect of dye concentration and dose; (<b>d</b>) effect of dye concentration and hydrogen peroxide; (<b>e</b>) effect of dye concentration and temperature; (<b>f</b>) effect of time and pH; (<b>g</b>) effect of time and dose; (<b>h</b>) effect of time and hydrogen peroxide; (<b>i</b>) effect of time and temperature; (<b>j</b>) effect of pH and dose; (<b>k</b>) effect of pH and hydrogen peroxide; (<b>l</b>) effect of pH and temperature; (<b>m</b>) effect of dose and hydrogen peroxide; (<b>n</b>) effect of dose and temperature; (<b>o</b>) effect of hydrogen peroxide and temperature.</p>
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<p>Comparison between the predicted and actual degradation of MO.</p>
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24 pages, 2122 KiB  
Article
Morphology-Dependent Photocatalytic Activity of Nanostructured Titanium Dioxide Coatings with Silver Nanoparticles
by Nasir Shakeel, Ireneusz Piwoński, Aneta Kisielewska, Maciej Krzywiecki, Damian Batory and Michał Cichomski
Int. J. Mol. Sci. 2024, 25(16), 8824; https://doi.org/10.3390/ijms25168824 - 13 Aug 2024
Viewed by 223
Abstract
This study aims to improve the photocatalytic properties of titanium dioxide nanorods (TNRs) and other related nanostructures (dense nanorods, needle-like nanorods, nanoballs, and nanoflowers) by modifying them with silver nanoparticles (AgNPs). This preparation is carried out using a two-step method: sol–gel dip-coating deposition [...] Read more.
This study aims to improve the photocatalytic properties of titanium dioxide nanorods (TNRs) and other related nanostructures (dense nanorods, needle-like nanorods, nanoballs, and nanoflowers) by modifying them with silver nanoparticles (AgNPs). This preparation is carried out using a two-step method: sol–gel dip-coating deposition combined with hydrothermal crystal growth. Further modification with AgNPs was achieved through the photoreduction of Ag+ ions under UV illumination. The investigation explores the impact of different growth factors on the morphological development of TiO2 nanostructures by modulating (i) the chemical composition, the water:acid ratio, (ii) the precursor concentration involved in the hydrothermal process, and (iii) the duration of the hydrothermal reaction. Morphological characteristics, including the length, diameter, and nanorod density of the nanostructures, were analyzed using scanning electron microscope (SEM). The chemical states were determined through use of the X-ray photoelectron spectroscopy (XPS) technique, while phase composition and crystalline structure analysis was performed using the Grazing Incidence X-ray Diffraction (GIXRD) method. The results indicate that various nanostructures (dense nanorods, needle-like nanorods, nanoballs, and nanoflowers) can be obtained by modifying these parameters. The photocatalytic efficiency of these nanostructures and Ag-coated nanostructures was assessed by measuring the degradation of the organic dye rhodamine B (RhB) under both ultraviolet (UV) irradiation and visible light. The results clearly show that UV light causes the RhB solution to lose its color, whereas under visible light RhB changes into rhodamine 110, indicating a successful photocatalytic transformation. The nanoball-like structures’ modification with the active metal silver (TNRs 4 Ag) exhibited high photocatalytic efficiency under both ultraviolet (UV) and visible light for different chemical composition parameters. The nanorod structure (TNRs 2 Ag) is more efficient under UV, but under visible-light photocatalyst, the TNRs 6 Ag (dense nanorods) sample is more effective. Full article
(This article belongs to the Special Issue Application of Nanomaterials in Novel Thin Films and Coatings)
16 pages, 11271 KiB  
Review
The Role of Solar Concentrators in Photocatalytic Wastewater Treatment
by Joy Sankar Roy and Younès Messaddeq
Energies 2024, 17(16), 4001; https://doi.org/10.3390/en17164001 - 13 Aug 2024
Viewed by 246
Abstract
The global challenge of sustainable and affordable wastewater treatment technology looms large as water pollution escalates steadily with the rapid pace of industrialization and population growth. The photocatalytic wastewater treatment is a cutting-edge and environmentally friendly technology that uses photons from light source [...] Read more.
The global challenge of sustainable and affordable wastewater treatment technology looms large as water pollution escalates steadily with the rapid pace of industrialization and population growth. The photocatalytic wastewater treatment is a cutting-edge and environmentally friendly technology that uses photons from light source to degrade and remove organic and inorganic contaminants from water. Thus, utilizing solar energy for photocatalytic wastewater treatment holds great promise as a renewable solution to alleviate pressures on the global water crisis. Employing solar concentrators to intensify sunlight for photocatalysis represents a promising avenue for future applications of a low-cost and rapid sustainable wastewater purification process. This groundbreaking approach will unveil fresh technological avenues for a cost-effective, sustainable, and swift wastewater purification process utilizing sunlight. This review article explores diverse solar concentrating systems and their potential applications in the wastewater treatment process. Full article
(This article belongs to the Special Issue Advances in Wastewater Treatment 2024)
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Figure 1
<p>Schematic ray diagram for sunlight concentration by a parabolic mirror.</p>
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<p>Picture of the 500 m<sup>2</sup> paraboloid solar concentrator built by The Australian National University [<a href="#B15-energies-17-04001" class="html-bibr">15</a>].</p>
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<p>The schematic ray diagram of a solar concentrator based on a primary paraboloid mirror and a secondary flat mirror (Reprinted with permission from Ref. [<a href="#B8-energies-17-04001" class="html-bibr">8</a>]. 2021, Elsevier).</p>
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<p>The picture of the ECoSEnDS (Reprinted with permission from Ref. [<a href="#B8-energies-17-04001" class="html-bibr">8</a>]. 2021, Elsevier).</p>
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<p>Schematic ray diagram for sunlight concentration by a Fresnel lens.</p>
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<p>Solar concentrator employing Fresnel lenses coupled with optical fiber (Reprinted with permission from Ref. [<a href="#B17-energies-17-04001" class="html-bibr">17</a>]. 2019, Elsevier]).</p>
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<p>Schematic representation of the heterogeneous photocatalytic organic pollutant’s degradation mechanism.</p>
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<p>Schematic depiction of three distinct heterojunction photocatalyst types: (<b>a</b>) type-I, (<b>b</b>) type-II, and (<b>c</b>) type-III heterojunctions (Reprinted with permission from Ref. [<a href="#B52-energies-17-04001" class="html-bibr">52</a>]. 2014, Royal Society of Chemistry).</p>
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<p>The water pasteurization system using a parabolic solar concentrator (Reprinted with permission from Ref. [<a href="#B20-energies-17-04001" class="html-bibr">20</a>]. 2014, Elsevier).</p>
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<p>Experimental setup for photocatalytic dye degradation under concentrated sunlight irradiation using Fresnel lens (Reprinted with permission from Ref. [<a href="#B21-energies-17-04001" class="html-bibr">21</a>]. 2006, Elsevier).</p>
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<p>Parabolic dish solar concentrator-based water treatment setup (Reprinted with permission from Ref. [<a href="#B56-energies-17-04001" class="html-bibr">56</a>]. 2021, Elsevier).</p>
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<p>Photocatalytic reactor with concentrated sunlight delivered using ECoSEnDS.</p>
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<p>Photocatalytic MB dye degradation of BiVO<sub>4</sub> nanoparticles under concentrated sunlight irradiation: (<b>a</b>) relative degradation over time and (<b>b</b>) % degradation achieved (Reprinted with permission from Ref. [<a href="#B8-energies-17-04001" class="html-bibr">8</a>]. 2021, Elsevier).</p>
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<p>Photocatalytic MB dye degradation of BiVO<sub>4</sub> nanoflakes under concentrated sunlight irradiation: (<b>a</b>) relative degradation over time and (<b>b</b>) % degradation achieved (Reprinted with permission from Ref. [<a href="#B5-energies-17-04001" class="html-bibr">5</a>]. 2021, Elsevier).</p>
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12 pages, 5096 KiB  
Article
Theoretical Analysis of Superior Photodegradation of Methylene Blue by Cerium Oxide/Reduced Graphene Oxide vs. Graphene
by Nguyen Hoang Hao, Phung Thi Lan, Nguyen Ngoc Ha, Le Minh Cam and Nguyen Thi Thu Ha
Molecules 2024, 29(16), 3821; https://doi.org/10.3390/molecules29163821 - 12 Aug 2024
Viewed by 241
Abstract
Density functional theory and a semi-empirical quantum chemical approach were used to evaluate the photocatalytic efficiency of ceria (CeO2) combined with reduced graphene oxide (rGO) and graphene (GP) for degrading methylene blue (MB). Two main aspects were examined: the adsorption ability [...] Read more.
Density functional theory and a semi-empirical quantum chemical approach were used to evaluate the photocatalytic efficiency of ceria (CeO2) combined with reduced graphene oxide (rGO) and graphene (GP) for degrading methylene blue (MB). Two main aspects were examined: the adsorption ability of rGO and GP for MB, and the separation of photogenerated electrons and holes in CeO2/rGO and CeO2/GP. Our results, based on calculations of the adsorption energy, population analysis, bond strength index, and reduced density gradient, show favorable energetics for MB adsorption on both rGO and GP surfaces. The process is driven by weak, non-covalent interactions, with rGO showing better MB adsorption. A detailed analysis involving parameters like fractional occupation density, the centroid distance between molecular orbitals, and the Lewis acid index of the catalysts highlights the effective charge separation in CeO2/rGO compared to CeO2/GP. These findings are crucial for understanding photocatalytic degradation mechanisms of organic dyes and developing efficient photocatalysts. Full article
(This article belongs to the Topic Advances in Computational Materials Sciences)
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Graphical abstract
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<p>Models of GP (<b>a</b>) and rGO (<b>b</b>); color codes: brown—C; ivory—H; red—O.</p>
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<p>Optimized adsorption configurations of MB on GP (<b>a</b>) and rGO (<b>b</b>); color codes: brown—C; ivory—H, yellow—Ce; red—O; green—Cl; gray—N; light yellow—S.</p>
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<p>IBSI values corresponding to the interatomic interactions between atoms of MB and atoms of rGO.</p>
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<p>Scatter graph of RDG for MB/GP (<b>a</b>) and MB/rGO (<b>b</b>) systems.</p>
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<p>RDG isosurfaces (isovalue = 0.8) of MB/GP (<b>a</b>) and MB/rGO (<b>b</b>) systems.</p>
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<p>Optimized structures of CeO<sub>2</sub>/GP (<b>a</b>) and CeO<sub>2</sub>/rGO (<b>b</b>).</p>
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<p>Frontier molecular orbitals of CeO<sub>2</sub>/GP: HOMO (<b>a</b>) and LUMO (<b>b</b>); and CeO<sub>2</sub>/rGO: HOMO (<b>c</b>) and LUMO (<b>d</b>).</p>
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<p>The FOD maps of GP, rGO, CeO<sub>2</sub>/GP, and CeO<sub>2</sub>/rGO.</p>
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11 pages, 3054 KiB  
Article
Enhanced TiO2-Based Photocatalytic Volatile Organic Compound Decomposition Combined with Ultrasonic Atomization in the Co-Presence of Carbon Black and Heavy Metal Nanoparticles
by Zen Maeno, Mika Nishitani, Takehiro Saito, Kazuhiko Sekiguchi, Naoki Kagi and Norikazu Namiki
Molecules 2024, 29(16), 3819; https://doi.org/10.3390/molecules29163819 - 12 Aug 2024
Viewed by 217
Abstract
Volatile organic compounds (VOCs) are representative indoor air pollutants that negatively affect the human body owing to their toxicity. One of the most promising methods for VOC removal is photocatalytic degradation using TiO2. In this study, the addition of carbon black [...] Read more.
Volatile organic compounds (VOCs) are representative indoor air pollutants that negatively affect the human body owing to their toxicity. One of the most promising methods for VOC removal is photocatalytic degradation using TiO2. In this study, the addition of carbon black (CB) and heavy metal nanoparticles (NPs) was investigated to improve the efficiency of a TiO2-based photocatalytic VOC decomposition system combined with ultrasonic atomization and ultraviolet irradiation, as described previously. The addition of CB and Ag NPs significantly improved the degradation efficiency. A comparison with other heavy metal nanoparticles and their respective roles are discussed. Full article
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<p>Comparison of the toluene degradation efficiencies with and without the addition of different types of heavy metal nanoparticles to the TiO<sub>2</sub> suspension.</p>
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<p>Comparison of the toluene degradation efficiencies with and without addition of CB and/or heavy metal (Ag or Pd) nanoparticles to the TiO<sub>2</sub> suspension.</p>
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<p>Change in the WSOC concentration in the TiO<sub>2</sub> suspension with and without additives (CB or Ag).</p>
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<p>Comparison of the decomposed carbon amounts in fed toluene and generated WSOC in the TiO<sub>2</sub> suspension with and without additives.</p>
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<p>UV-vis spectra of the TiO<sub>2</sub> suspension in the presence or absence of Ag NPs under irradiation with US and/or UV.</p>
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<p>XPS spectrum of the Ti 2p peak for TiO<sub>2</sub> suspension samples with and without Ag particles before and after UV irradiation Blue and red line shows raw and fitted date. (<b>a</b>) TiO<sub>2</sub>, (<b>b</b>) TiO<sub>2</sub> after UV irradiation, (<b>c</b>) TiO<sub>2</sub>+Ag, and (<b>d</b>) TiO<sub>2</sub>+Ag after UV irradiation.</p>
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<p>Comparison of the full width at half maximum (WFHM) values of the Ti 2p<sub>3/2</sub> peak for TiO<sub>2</sub> suspension samples with and without Ag particles before after UV irradiation.</p>
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<p>Comparison of the WFHM values of the Ti 2p<sub>3/2</sub> peak for samples of TiO<sub>2</sub> suspension with the addition of different types of heavy metal nanoparticles after UV irradiation.</p>
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<p>Correlation between the degradation rate, <span class="html-italic">R</span><sub>d</sub>, and the WFHM values of the Ti 2p<sub>3/2</sub> peak for TiO<sub>2</sub> suspension samples with the addition of different heavy metal NPs after UV irradiation.</p>
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<p>Setup for the photocatalytic decomposition of toluene vapor by TiO<sub>2</sub>-containing droplets generated by the ultrasonic atomization technique.</p>
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18 pages, 3973 KiB  
Article
The Impact of Polymerization Atmosphere on the Microstructure and Photocatalytic Properties of Fe-Doped g-C3N4 Nanosheets
by Xiaoyu Peng, Xiufang Chen, Rui Pang, Lanlan Cheng, Fengtao Chen and Wangyang Lu
Catalysts 2024, 14(8), 520; https://doi.org/10.3390/catal14080520 - 11 Aug 2024
Viewed by 440
Abstract
Peroxymonosulfate (PMS, SO52−)-based oxidation is an efficient pathway for degrading organic pollutants, but it still suffers from slow degradation efficiency and low PMS utilization. In this work, we report the preparation of porous Fe-doped g-C3N4 catalysts by [...] Read more.
Peroxymonosulfate (PMS, SO52−)-based oxidation is an efficient pathway for degrading organic pollutants, but it still suffers from slow degradation efficiency and low PMS utilization. In this work, we report the preparation of porous Fe-doped g-C3N4 catalysts by one-step thermal polymerization using urea and transition metal salts as precursors and investigate the effect of atmosphere conditions (air and nitrogen) on the catalytic performance. Systematic characterizations show that Fe-doped g-C3N4 prepared in air (FeNx-CNO) has a larger specific surface area (136.2 m2 g−1) and more oxygen vacancies than that prepared in N2 (FeNx-CNN, 74.2 m2 g−1), giving it more active sites to participate in the reaction. Meanwhile, FeNx-CNO inhibits the recombination of photogenerated carriers and improves the light utilization. The redox cycling of Fe(III) and Fe(II) species in the photocatalytic system ensures the continuous generation of SO5 and SO4. Therefore, FeNx-CNO can remove CBZ up to 96% within 20 min, which is 3.4 times higher than that of CNO and 3.1 times higher than that of FeNx-CNN, and the degradation efficiency can still retain 93% after 10 cycles of reaction. This study provides an economical and efficient method for photocatalysis in the degradation of medicines in contaminated water. Full article
(This article belongs to the Special Issue Recent Advances in g-C3N4-Based Photocatalysts)
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<p>(<b>a</b>) XRD pattern and (<b>b</b>) FT-IR spectra of different catalysts.</p>
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<p>TEM and HRTEM images of (<b>a<sub>1</sub></b>–<b>a<sub>3</sub></b>) 1%FeN<sub>x</sub>-CNN, (<b>b<sub>1</sub></b>–<b>b<sub>3</sub></b>) 1%FeN<sub>x</sub>-CNO, and (<b>c<sub>1</sub></b>–<b>c<sub>5</sub></b>) STEM mapping images of 1%FeN<sub>x</sub>-CNO.</p>
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<p>XPS spectra of CNO, CNN, 1%FeN<sub>x</sub>-CNO, and 1%FeN<sub>x</sub>-CNN. (<b>a</b>) C 1s, (<b>b</b>) N 1s, (<b>c</b>) O 1s, and (<b>d</b>) Fe 2p high-resolution XPS spectra.</p>
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<p>(<b>a</b>) Ultraviolet–visible diffuse reflection spectrum; (<b>b</b>) Tauc curve; (<b>c</b>) XPS valence band; (<b>d</b>) scheme of band gap structures for CNO, CNN, 1%FeN<sub>x</sub>-CNO, and 1%FeN<sub>x</sub>-CNN; (<b>e</b>) TPC response; and (<b>f</b>) PL spectrum of g-C<sub>3</sub>N<sub>4</sub>, 1%FeN<sub>x</sub>-CNO, and 1%FeN<sub>x</sub>-CNN.</p>
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<p>(<b>a</b>) Photocatalytic degradation of CBZ by n%FeN<sub>x</sub>-CNO in PMS/light system and (<b>b</b>) their corresponding the pseudo-first-order kinetics; (<b>c</b>) photocatalytic degradation of CBZ by CNO, CNN, 1%FeN<sub>x</sub>-CNO, and 1%FeN<sub>x</sub>-CNN in PMS/light system and (<b>d</b>) their corresponding the pseudo-first-order kinetics; (<b>e</b>) the photocatalytic performance of 1%FeN<sub>x</sub>-CNO under different reaction conditions; (<b>f</b>) consecutive recycling runs over 1%FeN<sub>x</sub>-CNO. Conditions: [CBZ] = 2.5×10<sup>−5</sup> M; [catalyst] = 0.1 g L<sup>−1</sup>; [PMS] = 0.2 mM.</p>
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<p>(<b>a</b>) Photocatalytic degradation of CBZ by n%FeN<sub>x</sub>-CNO in PMS/light system and (<b>b</b>) their corresponding the pseudo-first-order kinetics; (<b>c</b>) photocatalytic degradation of CBZ by CNO, CNN, 1%FeN<sub>x</sub>-CNO, and 1%FeN<sub>x</sub>-CNN in PMS/light system and (<b>d</b>) their corresponding the pseudo-first-order kinetics; (<b>e</b>) the photocatalytic performance of 1%FeN<sub>x</sub>-CNO under different reaction conditions; (<b>f</b>) consecutive recycling runs over 1%FeN<sub>x</sub>-CNO. Conditions: [CBZ] = 2.5×10<sup>−5</sup> M; [catalyst] = 0.1 g L<sup>−1</sup>; [PMS] = 0.2 mM.</p>
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<p>Comparison of XRD patterns (<b>a</b>) and high-resolution XPS spectra of (<b>b</b>) C 1s, (<b>c</b>) N 1s, and (<b>d</b>) Fe 2p of 1%FeN<sub>x</sub>-CNO before and after recycle reaction.</p>
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<p>Effects of different trapping agents on the photocatalytic degradation efficiency of CBZ by (<b>a</b>) FeN<sub>x</sub>-CNO and (<b>b</b>) FeN<sub>x</sub>-CNN. [CBZ] = 2.5 × 10<sup>−5</sup> M; [FeN<sub>x</sub>-CNO] = [FeN<sub>x</sub>-CNN] = 0.1 g L<sup>−1</sup>; [PMS] = 0.2 mM; [EA] = [TBA]= 10 mM; [<span class="html-italic">p</span>-BQ] = [<span class="html-small-caps">l</span>-His]= 1 mM.</p>
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<p>(<b>a</b>) DMPO spin-trapping EPR spectra in aqueous solution; (<b>b</b>) DMPO spin-trapping EPR spectra in methanol solution; and (<b>c</b>) TEMP spin-trapping EPR spectra in aqueous solution in the presence of g-C<sub>3</sub>N<sub>4</sub>, FeN<sub>x</sub>-CNO, and FeN<sub>x</sub>-CNN under simulated sunlight irradiation. [DMPO] = [TEMP] = 0.25 mM; [PMS] = 0.2 mM.</p>
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<p>A possible pathway for the degradation of CBZ by FeN<sub>x</sub>-CNO/PMS under simulated sunlight.</p>
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<p>Schematic sketch of the FeN<sub>x</sub>-CN photocatalyst synthesis process.</p>
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<p>Schematic illustration of the photocatalytic degradation mechanism of CBZ by FeN<sub>x</sub>-CNO/PMS/light system.</p>
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18 pages, 3255 KiB  
Article
Exploring the Integration of a Novel Photocatalytic Air Purification Façade Component in Buildings
by Judit Lopez-Besora, Cristina Pardal, Antonio Isalgue and Oriol Roig
Buildings 2024, 14(8), 2481; https://doi.org/10.3390/buildings14082481 - 11 Aug 2024
Viewed by 321
Abstract
Indoor air quality determines the comfort, health, and wellbeing of people in buildings. Windows are the optimal elements for providing natural ventilation and fresh air, but the outside contains suspended particles that can be harmful in high concentrations. This work presents an openable [...] Read more.
Indoor air quality determines the comfort, health, and wellbeing of people in buildings. Windows are the optimal elements for providing natural ventilation and fresh air, but the outside contains suspended particles that can be harmful in high concentrations. This work presents an openable and double-glazed façade component with a cavity that includes a series of slats that filter the air and depurate it by means of a photocatalytic reaction (TiO2). This component integrates the functions of ventilation, solar protection, and air purification, which were analysed in the slat and the façade component to approve a preliminary design. To this end, it was applied to a specific case, a non-residential building at a latitude 41° N in a Mediterranean climate. The results show the optimal dimensions according to solar radiation and ventilation in this specific case and the method used to obtain them, along with the increase in the temperature of the incoming air with respect to the outside (10 °C). Finally, the results obtained from a photocatalytic coating sample show that the NOx degradation can be up to 9%. All these results confirm the applicability of this component in buildings and pave the way for further research. Full article
(This article belongs to the Section Architectural Design, Urban Science, and Real Estate)
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<p>(<b>a</b>) Cross section with the parts or the panel; (<b>b</b>) the panel with the air management zone and the purification zone; (<b>c</b>) the aspect of the component from indoor.</p>
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<p>Cross section of the slat which contains filters.</p>
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<p>Printed ceramic with different fretwork patterns.</p>
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<p>Scheme of a possible building ventilation strategy using an atrium with a draught-enhancing chimney.</p>
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<p>Conversion of NO and NOx obtained for sample AX-CLE, based on [<a href="#B47-buildings-14-02481" class="html-bibr">47</a>].</p>
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<p>(<b>a</b>) Section with solar altitude on the winter solstice, summer solstice, and equinox at latitude 41° N; (<b>b</b>) solar obstruction of the slats in the stereographic solar diagram.</p>
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<p>Temperatures at Barcelona airport: mean, mean maximum, and mean minimum (Source: AEMET). In grey, the period with total shading of the interior.</p>
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<p>Slats’ arrangement with 0°, 10°, 20°, 30° and 40° inclination.</p>
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<p>Dimensions of the mock-up used for preliminary temperature measurements.</p>
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19 pages, 400 KiB  
Review
Perspectives for Photocatalytic Decomposition of Environmental Pollutants on Photoactive Particles of Soil Minerals
by Agnieszka Sosnowska, Kinga I. Hęclik, Joanna B. Kisała, Monika Celuch and Dariusz Pogocki
Materials 2024, 17(16), 3975; https://doi.org/10.3390/ma17163975 - 9 Aug 2024
Viewed by 470
Abstract
The literature shows that both in laboratory and in industrial conditions, the photocatalytic oxidation method copes quite well with degradation of most environmental toxins and pathogenic microorganisms. However, the effective utilization of photocatalytic processes for environmental decontamination and disinfection requires significant technological advancement [...] Read more.
The literature shows that both in laboratory and in industrial conditions, the photocatalytic oxidation method copes quite well with degradation of most environmental toxins and pathogenic microorganisms. However, the effective utilization of photocatalytic processes for environmental decontamination and disinfection requires significant technological advancement in both the area of semiconductor material synthesis and its application. Here, we focused on the presence and “photocatalytic capability” of photocatalysts among soil minerals and their potential contributions to the environmental decontamination in vitro and in vivo. Reactions caused by sunlight on the soil surface are involved in its normal redox activity, taking part also in the soil decontamination. However, their importance for decontamination in vivo cannot be overstated, due to the diversity of soils on the Earth, which is caused by the environmental conditions, such as climate, parent material, relief, vegetation, etc. The sunlight-induced reactions are just a part of complicated soil chemistry processes dependent on a plethora of environmental determinates. The multiplicity of affecting factors, which we tried to sketch from the perspective of chemists and environmental scientists, makes us rather skeptical about the effectiveness of the photocatalytic decontamination in vivo. On the other hand, there is a huge potential of the soils as the alternative and probably cheaper source of useful photocatalytic materials of unique properties. In our opinion, establishing collaboration between experts from different disciplines is the most crucial opportunity, as well as a challenge, for the advancement of photocatalysis. Full article
(This article belongs to the Section Catalytic Materials)
13 pages, 6214 KiB  
Article
Polymeric Carbon Nitride-CNTs-Ferric Oxide All-Solid Z-Scheme Heterojunction with Improved Photocatalytic Activity towards Organic Dye Removal
by Xinxin Yang, Rongcai Gong, Zhaocen Dong, Guiqing Liu, Yunyi Han, Yuwei Hou, Yanjun Li, Meili Guan, Xuezhong Gong and Jianguo Tang
Catalysts 2024, 14(8), 516; https://doi.org/10.3390/catal14080516 - 9 Aug 2024
Viewed by 266
Abstract
Polymeric carbon nitride (PCN) is a kind of polymeric semiconductor that is widely popular in photocatalysis-related energy and environmental fields. However, the photocatalytic activity is still limited due to its poor conductivity and low charge separation efficiency. In this work, benzene rings were [...] Read more.
Polymeric carbon nitride (PCN) is a kind of polymeric semiconductor that is widely popular in photocatalysis-related energy and environmental fields. However, the photocatalytic activity is still limited due to its poor conductivity and low charge separation efficiency. In this work, benzene rings were introduced to adjust the electronic structure of PCN, and then a PCN-based all-solid Z-scheme heterojunction was fabricated by combing multiwall carbon nanotubes (CNTs) and ferric oxide through precipitation and the in situ deposit method. Upon optimizing the ratio between PCN, CNTs, and Fe2O3, (PCN:CNTs:Fe2O3 = 10:1:3 by weight), the composites expressed superior photocatalytic degradation activity towards methylene blue (MB) and crystal violet (CV) compared with pristine PCN and Fe2O3. The MB degradation percentage achieved 90% in 75 min, and the CV up to 99.6% within 50 min. The Z-scheme mechanism was verified by band alignment and metal selective deposition. The CNTs in the heterojunction played the role of an electron shuttling mediator and hence improved charge separation efficiency. This work provides ideas for the construction of polymer-inorganic all-solid Z-scheme photocatalysts for practical applications. Full article
(This article belongs to the Special Issue Recent Advances in g-C3N4-Based Photocatalysts)
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<p>(<b>a</b>) SEM and (<b>b</b>) TEM images of the CCF-10 (CF-3) sample, EDS mapping of the SEM region (<b>c</b>) showing the elemental distribution of (<b>d</b>) C, (<b>e</b>) N, (<b>f</b>) O, and (<b>g</b>) Fe.</p>
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<p>(<b>a</b>) XRD patterns and (<b>b</b>) FTIR spectrum of PCN, α-Fe<sub>2</sub>O<sub>3</sub>, and PCN/CNTs/α-Fe<sub>2</sub>O<sub>3</sub> samples.</p>
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<p>(<b>a</b>) UV-Vis absorption spectra and (<b>b</b>) PL emission spectra of PCN, α-Fe<sub>2</sub>O<sub>3</sub>, and PCN/CNTs/α-Fe<sub>2</sub>O<sub>3</sub> samples.</p>
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<p>(<b>a</b>) Transient photocurrent response curves and (<b>b</b>) electrical impedance spectra of PCN, α-Fe<sub>2</sub>O<sub>3</sub>, and CCF-X (CF-X) samples.</p>
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<p>Pseudo-first-order kinetic curves for visible light degradation of MB (<b>a</b>), CV (<b>b</b>), and photocatalytic degradation of MB (<b>c</b>) and CV (<b>d</b>) for g-C<sub>3</sub>N<sub>4</sub>, α-Fe<sub>2</sub>O<sub>3</sub>, and PCN/CNTs/α-Fe<sub>2</sub>O<sub>3</sub> samples.</p>
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<p>Photocatalytic degradation of (<b>a</b>) MB and (<b>b</b>) CV of CCF-10 (CF-3) sample and binary composite pseudo-first-order kinetic profiles of (<b>c</b>) MB and (<b>d</b>) CV.</p>
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<p>(<b>a</b>) N<sub>2</sub> adsorption–desorption isotherms and (<b>b</b>) Barrett–Joyner–Halenda (BJH) pore size distributions of PCN, α-Fe<sub>2</sub>O<sub>3</sub>, and CCF-10 (CF-3) samples.</p>
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<p>XPS-VB spectrum of (<b>a</b>) PCN and (<b>b</b>) α-Fe<sub>2</sub>O<sub>3</sub>, (<b>c</b>) Tauc plots, and (<b>d</b>) energy band structures of PCN and α-Fe<sub>2</sub>O<sub>3</sub>.</p>
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<p>(<b>a</b>) EPR spectra and (<b>b</b>) a TEM image of the CCF-10 (CF-3) sample after photodeposited Pt. The photocatalytic degradation efficiency of (<b>c</b>) MB and (<b>d</b>) CV in the presence of scavengers using the CCF-10 (CF3) as a catalyst.</p>
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<p>Proposed photocatalytic degradation mechanism of organic dyes by PCN/CNTs/α-Fe<sub>2</sub>O<sub>3</sub> all-solid Z heterojunction under light irradiation.</p>
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<p>Schematic diagram of synthetic procedure for PCN/CNTs/α-Fe<sub>2</sub>O<sub>3</sub>.</p>
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19 pages, 3534 KiB  
Article
Modulation of Electronic Availability in g-C3N4 Using Nickel (II), Manganese (II), and Copper (II) to Enhance the Disinfection and Photocatalytic Properties
by Angie V. Lasso-Escobar, Elkin Darío C. Castrillon, Jorge Acosta, Sandra Navarro, Estefanía Correa-Penagos, John Rojas and Yenny P. Ávila-Torres
Molecules 2024, 29(16), 3775; https://doi.org/10.3390/molecules29163775 - 9 Aug 2024
Viewed by 298
Abstract
Carbon nitrides can form coordination compounds or metallic oxides in the presence of transition metals, depending on the reaction conditions. By adjusting the pH to basic levels for mild synthesis with metals, composites like g-C3N4-M(OH)x (where M represents [...] Read more.
Carbon nitrides can form coordination compounds or metallic oxides in the presence of transition metals, depending on the reaction conditions. By adjusting the pH to basic levels for mild synthesis with metals, composites like g-C3N4-M(OH)x (where M represents metals) were obtained for nickel (II) and manganese (II), while copper (II) yielded coordination compounds such as Cu-g-C3N4. These materials underwent spectroscopic and electrochemical characterization, revealing their photocatalytic potential to generate superoxide anion radicals—a feature consistent across all metals. Notably, the copper coordination compound also produced significant hydroxyl radicals. Leveraging this catalytic advantage, with band gap energy in the visible region, all compounds were activated to disinfect E. coli bacteria, achieving total disinfection with Cu-g-C3N4. The textural properties influence the catalytic performance, with copper’s stabilization as a coordination compound enabling more efficient activity compared to the other metals. Additionally, the determination of radicals generated under light in the presence of dicloxacillin supported the proposed mechanism and highlighted the potential for degrading organic molecules with this new material, alongside its disinfectant properties. Full article
(This article belongs to the Special Issue Photocatalytic Materials and Photocatalytic Reactions)
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<p>Cyclic voltammetry curves for (<b>a</b>) Cu-g-C<sub>3</sub>N<sub>4</sub>, Ni-g-C<sub>3</sub>N<sub>4</sub>, (<b>b</b>) Mn-g-C<sub>3</sub>N<sub>4</sub>, and (<b>c</b>) Ni-g-C<sub>3</sub>N<sub>4</sub>. Experimental conditions: sweep rate = 20 mV/s; window potential = −1.5 V and 0.0 V, supporting electrolyte: [Na<sub>2</sub>SO<sub>4</sub>] = 0.1 M; and [H<sub>2</sub>O<sub>2</sub>] = 0.01 M. (<b>d</b>) Chronoamperometry curves for Cu-g-C<sub>3</sub>N<sub>4</sub>, Mn-g-C<sub>3</sub>N<sub>4</sub>, and Ni-g-C<sub>3</sub>N<sub>4</sub>. Experimental conditions: V = 0.5 V; time = 15 min; supporting electrolyte: [Na<sub>2</sub>SO<sub>4</sub>] = 0.1 M; and [H<sub>2</sub>O<sub>2</sub>] = 0.01 M. The ↓ corresponds to first oxidation process.</p>
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<p>Cyclic voltammetry curves for (<b>a</b>) Cu-g-C<sub>3</sub>N<sub>4</sub>, Ni-g-C<sub>3</sub>N<sub>4</sub>, (<b>b</b>) Mn-g-C<sub>3</sub>N<sub>4</sub>, and (<b>c</b>) Ni-g-C<sub>3</sub>N<sub>4</sub>. Experimental conditions: sweep rate = 20 mV/s; window potential = −1.5 V and 0.0 V, supporting electrolyte: [Na<sub>2</sub>SO<sub>4</sub>] = 0.1 M; and [H<sub>2</sub>O<sub>2</sub>] = 0.01 M. (<b>d</b>) Chronoamperometry curves for Cu-g-C<sub>3</sub>N<sub>4</sub>, Mn-g-C<sub>3</sub>N<sub>4</sub>, and Ni-g-C<sub>3</sub>N<sub>4</sub>. Experimental conditions: V = 0.5 V; time = 15 min; supporting electrolyte: [Na<sub>2</sub>SO<sub>4</sub>] = 0.1 M; and [H<sub>2</sub>O<sub>2</sub>] = 0.01 M. The ↓ corresponds to first oxidation process.</p>
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<p>(<b>a</b>) Photodisinfection using hydroxides of metal ions versus materials with g-C<sub>3</sub>N<sub>4</sub> after 20 min of exposure with a Xenon lamp. (<b>b</b>) Kinetic disinfection for g-C<sub>3</sub>N<sub>4</sub> and modified materials with copper, manganese, and nickel against <span class="html-italic">E. coli</span> 25922 (Time = −15–60 min).</p>
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<p>Electrochemical characterization of g- C<sub>3</sub>N<sub>4</sub> and modified materials with copper (II), manganese (II), and nickel (II), (<b>a</b>). Nyquist diagrams, (<b>b</b>). Mott–Schottky plot, (<b>c</b>). Bands (conduction and valence) diagram construed for authors.</p>
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<p>Electrochemical characterization of g- C<sub>3</sub>N<sub>4</sub> and modified materials with copper (II), manganese (II), and nickel (II), (<b>a</b>). Nyquist diagrams, (<b>b</b>). Mott–Schottky plot, (<b>c</b>). Bands (conduction and valence) diagram construed for authors.</p>
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<p>(<b>a</b>). Photolysis of DXC to Xenon Lamp, (<b>b</b>). Photodegradation using Cu-g-C<sub>3</sub>-N<sub>4</sub> and g-C<sub>3</sub>-N<sub>4</sub> with exposure to Xenon lamp, (<b>c</b>). Photodegradation using Cu-g-C<sub>3</sub>-N<sub>4</sub> and g-C<sub>3</sub>-N<sub>4</sub> with scavengers for <sup>•</sup>OH radical and h<sup>+</sup> activation.</p>
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<p>(<b>a</b>). Photolysis of DXC to Xenon Lamp, (<b>b</b>). Photodegradation using Cu-g-C<sub>3</sub>-N<sub>4</sub> and g-C<sub>3</sub>-N<sub>4</sub> with exposure to Xenon lamp, (<b>c</b>). Photodegradation using Cu-g-C<sub>3</sub>-N<sub>4</sub> and g-C<sub>3</sub>-N<sub>4</sub> with scavengers for <sup>•</sup>OH radical and h<sup>+</sup> activation.</p>
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<p>(<b>a</b>) Theoretical calculations for a system composed of g-C<sub>3</sub>-N<sub>4</sub>, Cu-g-C<sub>3</sub>-N<sub>4</sub> (physisorption), CuN-g-C<sub>3</sub>N<sub>4</sub> (Cu-coordinated N-triazine), and CuNH-g-C<sub>3</sub>N<sub>4</sub> (Cu-coordinated N-aliphatic). (<b>b</b>) CuNH-g-C<sub>3</sub>N<sub>4</sub> (Cu-coordinated, N-aliphatic-interacting DCX molecule). Color code structure: blue color (nitrogen atom), red (oxygen atom), grey (carbon atom), white (hydrogen atom), purple (negative density charge), green (positive density charge), and dark green (chlorine atom).</p>
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<p>(<b>a</b>) Theoretical calculations for a system composed of g-C<sub>3</sub>-N<sub>4</sub>, Cu-g-C<sub>3</sub>-N<sub>4</sub> (physisorption), CuN-g-C<sub>3</sub>N<sub>4</sub> (Cu-coordinated N-triazine), and CuNH-g-C<sub>3</sub>N<sub>4</sub> (Cu-coordinated N-aliphatic). (<b>b</b>) CuNH-g-C<sub>3</sub>N<sub>4</sub> (Cu-coordinated, N-aliphatic-interacting DCX molecule). Color code structure: blue color (nitrogen atom), red (oxygen atom), grey (carbon atom), white (hydrogen atom), purple (negative density charge), green (positive density charge), and dark green (chlorine atom).</p>
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<p>(<b>a</b>) Electronic effect of metal ions on electronic properties in g-C<sub>3</sub>N<sub>4</sub>. (<b>b</b>) Electronic condition of g-C<sub>3</sub>N<sub>4</sub> reported vs. generation of ROS.</p>
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13 pages, 6387 KiB  
Article
Construction of Ag3PO4/g-C3N4 Z-Scheme Heterojunction Composites with Visible Light Response for Enhanced Photocatalytic Degradation
by Xiangping Pan, Ying Meng, Qingwang Liu and Mai Xu
Molecules 2024, 29(16), 3774; https://doi.org/10.3390/molecules29163774 - 9 Aug 2024
Viewed by 361
Abstract
Ag3PO4/g-C3N4 photocatalytic composites were synthesized via calcination and hydrothermal synthesis for the degradation of rhodamine B (RhB) in wastewater, and characterized using X-ray diffraction (XRD), scanning electron microscopy (SEM), transmission electron microscopy (TEM), X-ray photoelectron spectroscopy [...] Read more.
Ag3PO4/g-C3N4 photocatalytic composites were synthesized via calcination and hydrothermal synthesis for the degradation of rhodamine B (RhB) in wastewater, and characterized using X-ray diffraction (XRD), scanning electron microscopy (SEM), transmission electron microscopy (TEM), X-ray photoelectron spectroscopy (XPS), and diffuse reflectance spectroscopy (DRS). The degradation of RhB by Ag3PO4/g-C3N4 composites was investigated to evaluate their photocatalytic performance and cyclic degradation stability. The experimental results showed that the composites demonstrated notable photocatalytic activity and stability during degradation. Their high degradation efficiency is attributed to the Z-scheme transfer mechanism, in which the electrons in the Ag3PO4 conduction band and the holes in the g-C3N4 valence band are annihilated by heterojunction recombination, which greatly limits the recombination of photogenerated electrons and holes in the catalyst and enhances the activity of the composite photocatalyst. In addition, measurements of photocurrent (PC) and electrochemical impedance spectroscopy (EIS) confirmed that the efficient charge separation of photo-generated charges stemmed from strong interactions at the close contact interface. Finally, the mechanism for catalytic enhancement in the composite photocatalysts was proposed based on hole and radical trapping experiments, electron paramagnetic resonance (EPR) analysis, and work function evaluation. Full article
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<p>(<b>a</b>) XRD patterns of the different samples. (<b>b</b>) EDS pattern of the Ag<sub>3</sub>PO<sub>4</sub>/g-C<sub>3</sub>N<sub>4</sub>. (<b>c</b>) N<sub>2</sub> adsorption and desorption isotherms of g-C<sub>3</sub>N<sub>4</sub> and Ag<sub>3</sub>PO<sub>4</sub>/g-C<sub>3</sub>N<sub>4</sub>.</p>
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<p>SEM images of (<b>a</b>) Ag<sub>3</sub>PO<sub>4</sub>, (<b>b</b>) g-C<sub>3</sub>N<sub>4</sub>, and (<b>c</b>) Ag<sub>3</sub>PO<sub>4</sub>/g-C<sub>3</sub>N<sub>4</sub>. (<b>d</b>) TEM images of Ag<sub>3</sub>PO<sub>4</sub>/g-C<sub>3</sub>N<sub>4</sub>.</p>
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<p>XPS spectra of the as-prepared samples. (<b>a</b>) The survey scan, (<b>b</b>) Ag 3d, (<b>c</b>) P 2p, (<b>d</b>) N 1s, (<b>e</b>) C 1s, and (<b>f</b>) O 1s.</p>
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<p>(<b>a</b>) UV–vis diffuse reflectance absorption spectra of samples. (<b>b</b>) Plots of (αhν)<sup>2</sup> versus hν of samples. VB-XPS curves of (<b>c</b>) g-C<sub>3</sub>N<sub>4</sub> and (<b>d</b>) Ag<sub>3</sub>PO<sub>4</sub>.</p>
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<p>(<b>a</b>) EIS plots, (<b>b</b>) photocurrent density versus potential curves, and (<b>c</b>) PL spectra for g-C<sub>3</sub>N<sub>4</sub>, Ag<sub>3</sub>PO<sub>4</sub>, and Ag<sub>3</sub>PO<sub>4</sub>/g-C<sub>3</sub>N<sub>4</sub>.</p>
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<p>(<b>a</b>) Degradation curves of RhB by samples under visible light irradiation. (<b>b</b>) Corresponding first-order kinetics of samples. (<b>c</b>) The concentration effects of RhB on the photodegradation efficiency of the composite sample. (<b>d</b>,<b>e</b>) Five cycling runs of the composite sample for RhB degradation. (<b>f</b>) XRD patterns of Ag<sub>3</sub>PO<sub>4</sub>/g-C<sub>3</sub>N<sub>4</sub> before and after the cyclic test.</p>
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<p>(<b>a</b>) Photocatalytic free radical capture degradation curves of Ag<sub>3</sub>PO<sub>4</sub>/g-C<sub>3</sub>N<sub>4</sub>. (<b>b</b>) Mott–Schottky curves of samples. VB-XPS curves of (<b>c</b>) g-C<sub>3</sub>N<sub>4</sub> and (<b>d</b>) Ag<sub>3</sub>PO<sub>4</sub>.</p>
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<p>Schematic illustration of the degradation mechanism.</p>
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14 pages, 4101 KiB  
Article
Preparation and Adsorption Photocatalytic Properties of PVA/TiO2 Colloidal Photonic Crystal Films
by Zhangyi Qian, Menghan Wang, Junling Li, Zhaoran Chu, Wenwei Tang and Cheng Chen
Gels 2024, 10(8), 520; https://doi.org/10.3390/gels10080520 - 7 Aug 2024
Viewed by 252
Abstract
Polyvinyl alcohol (PVA)/TiO2/colloidal photonic crystal (CPC) films with photocatalytic properties are presented, where TiO2 nanoparticles were introduced into the PVA gel network. Such PVA/TiO2/CPC films possess three-dimensional periodic structures that are supported with a PVA/TiO2 composite gel. [...] Read more.
Polyvinyl alcohol (PVA)/TiO2/colloidal photonic crystal (CPC) films with photocatalytic properties are presented, where TiO2 nanoparticles were introduced into the PVA gel network. Such PVA/TiO2/CPC films possess three-dimensional periodic structures that are supported with a PVA/TiO2 composite gel. The unique structural color of CPCs can indicate the process of material preparation, adsorption, and desorption. The shift of diffraction peaks of CPCs can be more accurately determined using fiber-optic spectroscopy. The effect of the PVA/TiO2/CPC catalyst films showed better properties as the degradation of methylene blue (MB) by the PVA/TiO2/CPC film catalyst in 4 h was 77~90%, while the degradation of MB by the PVA/TiO2 film was 33% in 4 h, indicating that the photonic crystal structure was 2.3~2.7 times more effective than that of the bulk structure. Full article
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<p>(<b>a</b>) Infrared spectra of the PVA, TiO<sub>2</sub>, and mixture of PVA/TiO<sub>2</sub>; (<b>b</b>) Scanning electron microscopy (SEM) image of PVA/TiO<sub>2</sub>. The inset is the optical photograph of the sample.</p>
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<p>SEM of the prepared samples: (<b>a</b>) CPC-186; (<b>b</b>) CPC-209; (<b>c</b>) CPC-252; (<b>d</b>) PVA/TiO<sub>2</sub>/CPC-186; (<b>e</b>) PVA/TiO<sub>2</sub>/CPC-209; (<b>f</b>) PVA/TiO<sub>2</sub>/CPC-252. The insets in the upper right corner are the corresponding structural colors of the samples, respectively. (<b>g</b>) Diffraction spectra comparison of CPC: before and after infiltration of PVA/TiO<sub>2</sub> (solid line: before infiltration; dashed line: after infiltration).</p>
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<p>(<b>a</b>) Thermogravimetric graphs of PVA, PVA/TiO<sub>2</sub>, and PVA/TiO<sub>2</sub>/CPC films; (<b>b</b>) Strain–stress graphs of PVA, PVA/TiO<sub>2</sub>, and PVA/TiO<sub>2</sub>/CPC films.</p>
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<p>(<b>a</b>,<b>b</b>) The equilibrium swelling and rate profiles of dark adsorption of PVA/TiO<sub>2</sub> and PVA/TiO<sub>2</sub>/CPC (186 nm, 209 nm, and 252 nm) films, respectively.</p>
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<p>(<b>a</b>) Physical diagrams of the dark adsorption (60 min)–photocatalytic (4 h) degradation of MB dye by PVA/TiO<sub>2</sub> and PVA/TiO<sub>2</sub>/CPC films; UV–visible absorption spectra of the degradation of MB dye by (<b>b</b>) PVA/TiO<sub>2</sub>, (<b>c</b>) PVA/TiO<sub>2</sub>/CPC-186, (<b>d</b>) PVA/TiO<sub>2</sub>/CPC-209, and (<b>e</b>) PVA/TiO<sub>2</sub>/CPC-252 films, respectively.</p>
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<p>(<b>a</b>) Repeated (4 times) experiments of adsorption–photocatalytic degradation of MB by PVA/TiO<sub>2</sub> and PVA/TiO<sub>2</sub>/CPC films; (<b>b</b>,<b>c</b>) Comparison of the removal rate of adsorption–photocatalytic degradation of MB by repeated use of PVA/TiO<sub>2</sub>, PVA/TiO<sub>2</sub>/CPC films.</p>
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<p>Schematic diagram of the preparation process of PVA/TiO<sub>2</sub>/CPC films.</p>
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<p>Standard curve of MB in a UV–vis experiment.</p>
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10 pages, 274 KiB  
Article
Multi-Criteria Decision-Making Approach for Pre-Synthesis Selection of the Optimal Physicochemical Properties of TiO2 Photocatalytic Nanoparticles for Biomedical and Environmental Applications
by Nefeli Lagopati, Georgios P. Trachanas and Haris Doukas
Molecules 2024, 29(16), 3726; https://doi.org/10.3390/molecules29163726 - 6 Aug 2024
Viewed by 408
Abstract
Nanomaterials are widely used in several biomedical and environmental applications, due to their ideal properties. However, the synthetic and characterization procedure requires significant costs and has a negative environmental impact. Various methods are available in order to control the pre-synthesis design of the [...] Read more.
Nanomaterials are widely used in several biomedical and environmental applications, due to their ideal properties. However, the synthetic and characterization procedure requires significant costs and has a negative environmental impact. Various methods are available in order to control the pre-synthesis design of the produced materials, predicting their behavior and minimizing the series of experiments. Multi-Criteria Decision-Making is proposed in this study in order to determine the best combination of the physicochemical parameters and to define the best alternative among fifteen different samples of nanostructured titanium dioxide. In particular, the Technique for Order of Preference by Similarity to Ideal Solution (TOPSIS) method was applied to achieve a final ranking of the available alternatives by avoiding several of the trials that would follow testing the biological effect and the photocatalytic degradation of organic pollutants. Thus, this approach helps us to stay environmentally and ethically correct, saving time, money, and energy and also providing an optimization of the nanomaterials that are developed. Full article
11 pages, 2261 KiB  
Article
Boosting Photocatalytic Performance of ZnO Nanowires via Building Heterojunction with Conjugated 2,4,6-Triaminopyrimidine-g-C3N4
by Jiahui Lou, Lihong Wang, Yaqiong Huang, Jun Xing and Xiaojie Yang
Molecules 2024, 29(16), 3716; https://doi.org/10.3390/molecules29163716 - 6 Aug 2024
Viewed by 359
Abstract
Photocatalysis is one of the most effective ways to solve environmental problems by solving pollutants. This article designed and prepared a conjugated system of 2,4,6-triaminopyrimidine-g-C3N4 (TAP-CN) to modify ZnO NWs. We systematically studied the photocatalytic performance of ZnO NWs modified [...] Read more.
Photocatalysis is one of the most effective ways to solve environmental problems by solving pollutants. This article designed and prepared a conjugated system of 2,4,6-triaminopyrimidine-g-C3N4 (TAP-CN) to modify ZnO NWs. We systematically studied the photocatalytic performance of ZnO NWs modified with different ratios of TAP-CN. The results showed that 9 wt% TAP-CN-30/ZnO NWs had the best degradation effect on Rhodamine B dye. The degradation rate was 99.36% in 80 min. The excellent degradation performance was attributed to the TAP-CN conjugated system promoting photo-generated charge transfer. This work provided guidance for designing efficient composite catalysts for application in other renewable energy fields. Full article
(This article belongs to the Special Issue Advanced Metal-Free Composites for Photocatalytic Application)
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<p>Schematic diagram of the experimental preparation process.</p>
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<p>(<b>a</b>) XRD patterns of ZnO, TAP-CN-30, g-C<sub>3</sub>N<sub>4</sub>, 9 wt% TAP-CN-30/ZnO; (<b>b</b>) infrared characterization of ZnO, TAP-CN-30, g-C<sub>3</sub>N<sub>4</sub>, 9 wt% TAP-CN-30/ZnO.</p>
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<p>XPS spectra of 9 wt% TAP-CN-30/ZnO: (<b>a</b>) survey; (<b>b</b>) Zn 2p; (<b>c</b>) N 1s; (<b>d</b>) C 1s; (<b>e</b>) O 1s.</p>
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<p>FESEM images: (<b>a</b>) SEM images of g-C<sub>3</sub>N<sub>4</sub>; (<b>b</b>) SEM images of TAP-CN-30; (<b>c</b>) SEM images of ZnO NWs; (<b>d</b>) SEM image of 9 wt% TAP-CN-30/ZnO; TEM images: (<b>e</b>,<b>f</b>) 9 wt% TAP-CN-30/ZnO; HRTEM images: (<b>g</b>,<b>h</b>) 9 wt% TAP-CN-30/ZnO; (<b>i</b>–<b>m</b>) EDS mapping images of 9 wt% TAP-CN-30/ZnO.</p>
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<p>(<b>a</b>) Photocatalytic activity of TAP-CN for photocatalytic degradation of RhB in visible light; (<b>b</b>) Reaction kinetic curve of RhB photocatalytic degradation by TAP-CN under visible light irradiation; (<b>c</b>) Photocatalytic activity of TAP-CN-30/ZnO for photocatalytic degradation of RhB in visible light; (<b>d</b>) Reaction kinetic curve of RhB photocatalytic degradation by TAP-CN-30/ZnO under visible light irradiation; (<b>e</b>) 9 wt% TAP-CN-30/ZnO degradation RhB cycle test diagram; (<b>f</b>) Capture experimental diagram of RhB related active substances degraded by 9 wt% TAP-CN-30/ZnO.</p>
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<p>Schematic diagram for the proposed photocatalytic reaction mechanism of 9 wt% TAP-CN-30/ZnO.</p>
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<p>(<b>a</b>) The SEM image of 9 wt% TAP-CN-30/ZnO; (<b>b</b>) The SEM image of 9 wt% TAP-CN-30/ZnO after cycles; (<b>c</b>) XRD patterns of 9 wt% TAP-CN-30/ZnO and 9 wt% TAP-CN-30/ZnO after cycles; (<b>d</b>) infrared characterization of 9 wt% TAP-CN-30/ZnO and 9 wt% TAP-CN-30/ZnO after cycles.</p>
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