N-TiO2 Photonic and Quantum Photocatalytic Efficiency Determined by Monte Carlo Simulation

Patricio F. F. Carnelli , Estefanía B. Bracco , Orlando M. Alfano , Roberto J. Candal

Photocatal. Res. Potential ›› 2025, Vol. 2 ›› Issue (4) : 10019

PDF (1539KB)
Photocatal. Res. Potential ›› 2025, Vol. 2 ›› Issue (4) :10019 DOI: 10.70322/prp.2025.10019
Article
research-article
N-TiO2 Photonic and Quantum Photocatalytic Efficiency Determined by Monte Carlo Simulation
Author information +
History +
PDF (1539KB)

Abstract

Nitrogen-modified titanium dioxide (N-TiO2) is proposed as an alternative to improve solar light absorption in photocatalytic applications. Due to its high chemical stability and low toxicity, various synthesis methods have been developed, yielding materials with different properties. Evaluating its performance compared to other photocatalysts requires calculating the quantum efficiency, which involves appropriate mathematical models to interpret experimental data. This study used a Monte Carlo approach to determine the local volumetric rate of photon absorption (LVRPA). TiO2 and N-TiO2 were synthesized via the sol-gel method using urea as the nitrogen source, and commercial TiO2 P-25 was used as a reference. Formic acid and salicylic acid were chosen as model pollutants due to their differing adsorption behavior on TiO2. Three light sources were used: UVA, white, and blue light. Nitrogen doping increased quantum efficiency for formic acid degradation under UVA from 2.4 to 3.5 (46% increase) and salicylic acid from 1.0 to 2.1 (110% increase). P-25 showed the highest efficiencies under UVA, with 6.2 for formic acid and 5.2 for salicylic acid. Under white light, salicylic acid degradation efficiency doubled from 0.4 to 0.8 after nitrogen doping. No activity was observed for formic acid with undoped TiO2 under white light, but N-TiO2 achieved 1.1. Under blue light, no activity was detected for formic acid, while salicylic acid degradation showed efficiencies of 0.3 (N-TiO2) and 0.2 (P-25). Quantum efficiency was highest under UVA, indicating that nitrogen doping improves visible light response but does not surpass UVA performance.

Keywords

N-TiO2 / Photocatalysis / Quantum-efficiency / Photonic-efficiency / Monte Carlo simulation

Cite this article

Download citation ▾
Patricio F. F. Carnelli, Estefanía B. Bracco, Orlando M. Alfano, Roberto J. Candal. N-TiO2 Photonic and Quantum Photocatalytic Efficiency Determined by Monte Carlo Simulation. Photocatal. Res. Potential, 2025, 2(4): 10019 DOI:10.70322/prp.2025.10019

登录浏览全文

4963

注册一个新账户 忘记密码

Supplementary Materials

The following supporting information can be found at: https://www.sciepublish.com/article/pii/727, Figure S1: Emission spectra of the different lamps; Calculations and theory: Implementation of Monte Carlo simulations to calculate photon absorption efficiency; Figure S2: Transmittance spectrum of methacrylate cylindrical filter; Figure S3: SEM images an XRD pattern of TiO2 P-25; Figure S4: Flowchart of the Monte Carlo algorithm used for the simulation of the reactor, where n is the number of photons extinguished and nT is the total number of photons at the beginning of the simulation; Figure S5: Coefficients of extinction (a) and absorption (b) as a function of concentration for three different wavelengths, for the N-TiO2 photocatalyst. Also included are linear regressions for each dataset with their respective values for the coefficient of determination R2; Figure S6: temporal evolution of salicylic and formic acid during adsorption; Figure S7: Effect of UVA, WL and BL irradiation on aqueous solutions of formic or salicylic acid; Figure S8: Absorption spectra of salicylic acid after different photocatalytic treatment times. Photocatalyst: N-TiO2. Light source: UVA, white light (WL), filtered white light (FWL), and blue light (BL); Figure S9: Absorption spectra of salicylic acid after different photocatalytic treatment times. Photocatalyst: TiO2. Light source: UVA, white light (WL), filtered white light (FWL), and blue light (BL); Figure S10: Absorption spectra of salicylic acid after different photocatalytic treatment times. Photocatalyst: TiO2. Light source: UVA, white light (WL), filtered white light (FWL), and blue light (BL); Figure S11: Contaminant degradation as a function of time using the N-TiO2 photocatalyst for formic acid and white light (a), formic acid and UVA radiation (b), salicylic acid and white light (c), salicylic acid and UVA radiation (d). Data fits are included in the figures, using the pseudo-order zero (Ord 0), pseudo-order 1 (Ord 1), and Langmuir-Hinshelwood (L-H) models; Table S1: Sum of squared residuals (SSR) of the fits of the concentration vs. time curves for the different photocatalysts. The considered models were the pseudo-order zero (Ord 0), pseudo-order 1 (Ord 1), and Langmuir-Hinshelwood (L-H) (for some example plots, see Figure S11). The fitted values of the initial rate of reaction v0 {v}_{0} v0​ for the Ord 0 model are also included.

Acknowledgments

The authors gratefully acknowledge the support given by Universidad Nacional de San Martín, Universidad Nacional del Litoral and Consejo Nacional de Investigaciones Científicas y Técnicas (CONICET). OMA, PFFC and RJC are members of CONICET.

Author Contributions

Conceptualization, O.M.A., R.J.C. and P.F.F.C.; Methodology, E.B.B. and P.F.F.C.; Software, P.F.F.C.; Validation, O.M.A., R.J.C. and E.B.B.; Formal Analysis, E.B.B. and P.F.F.C.; Investigation, E.B.B., P.F.F.C. and R.J.C.; Resources, R.J.C.; Data Curation, O.M.A.; Writing—Original Draft Preparation, R.J.C. and P.F.F.C.; Writing—Review & Editing, R.J.C. and O.M.A.; Project Administration, R.J.C.; Funding Acquisition, R.J.C. and P.F.F.C.

Ethics Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data will be available under requirement.

Funding

This research was funded by Agencia Nacional de PromociónCientífica y Tecnológica, PICT 2019-3263, PICT 2014-750 and PICT 2014-2386 (Argentina).

Declaration of Competing Interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

References

[1]

Liao CH, Huang CW, Wu JC. Hydrogen production from semiconductor-based photocatalysis via water splitting. Catalysts 2012, 2, 490-516.

[2]

Garg S, Chandra A. (Eds.) Photocatalysis for Environmental Remediation and Energy Production: Recent Advances and Applications; Springer: Cham, Switzerland, 2023. doi:10.1007/978-3-031-27707-8.

[3]

Zhou R, Guzman MI. CO2 reduction under periodic illumination of ZnS. J. Phys. Chem. C 2014, 118, 11649-11656.

[4]

Aguirre ME, Zhou R, Eugene AJ, Guzman MI, Grela MA. Cu2O/TiO2 heterostructures for CO2 reduction through a direct Z-scheme: Protecting Cu2O from photocorrosion. Appl. Catal. B Environ. 2017, 217, 485-493.

[5]

Alam U. Role of Heterogeneous Semiconductor Photocatalysts in Green Organic Synthesis. In Photocatalysis for Environmental Remediation and Energy Production; Garg S, Chandra A, Eds.; Green Chemistry and Sustainable Technology; Springer: Cham, Switzerland, 2023. doi:10.1007/978-3-031-27707-8_11.

[6]

Guzman MI. Feature Papers in Photochemistry. Photochem 2024, 12, 511-517. doi:10.3390/photochem4040032.

[7]

Guo W, Guo T, Zhang Y, Yin L, Dai Y. Progress on simultaneous photocatalytic degradation of pollutants and production of clean energy: A review. Chemosphere 2023, 339, 139486. doi:10.1016/j.chemosphere.2023.139486.

[8]

Parwaiz S, Khan MM. Perovskites and perovskite-based heterostructures for photocatalytic energy and environmental applications. J. Environ. Chem. Eng. 2024, 12, 113175. doi:10.1016/j.jece.2024.113175.

[9]

Feng X, Yu Z, Sun Y, Long R, Shan M, Li X, et al. Review MXenes as a new type of nanomaterial for environmental applications in the photocatalytic degradation of water pollutants. Ceram. Int. 2021, 47, 7321-7343.

[10]

Chen C, Fei L, Wang B, Xu J, Li B, Shen L, et al. MOF-based photocatalytic membrane for water purification: A review. Small 2024, 20, 2305066. doi:10.1002/smll.202305066.

[11]

Liu S, Wang M, He Y, Cheng Q, Qian T, Yan C. Covalent organic frameworks towards photocatalytic applications: Design principles, achievements, and opportunities. Coord. Chem. Rev. 2023, 475, 214882. doi:10.1016/j.ccr.2022.214882.

[12]

Wang J, Sun S, Zhou R, Li Y, He Z, Ding H, et al. A review: Synthesis, modification and photocatalytic applications of ZnIn2S4. J. Mater. Sci. Technol. 2021, 78, 1-19. doi:10.1016/j.jmst.2020.09.045.

[13]

Du S, Lian J, Zhang F. Visible Light-Responsive N-Doped TiO2 Photocatalysis: Synthesis, Characterizations, and Applications. Trans. Tianjin Univ. 2022, 28, 33-52. doi:10.1007/s12209-021-00303-w.

[14]

Natarajan TS, Mozhiarasi V, Tayade RJ. Nitrogen Doped Titanium Dioxide (N-TiO2): Synopsis of Synthesis Methodologies 2022, Doping Mechanisms, Property Evaluation and Visible Light Photocatalytic Applications. Photochem 2021, 1, 371-410. doi:10.3390/photochem1030024.

[15]

Rengifo-Herrera JA, Osorio-Vargas P, Pulgarin C. A critical review on N-modified TiO2 limits to treat chemical and biological contaminants in water. Evidence that enhanced visible light absorption does not lead to higher degradation rates under whole solar light. J. Hazard. Mater. 2022, 425, 127979. doi:10.1016/j.jhazmat.2021.127979.

[16]

Irie H, Watanabe Y, Hashimoto K. Nitrogen-concentration dependence on photocatalytic activity of TiO2-x Nx powders. J. Phys. Chem. B 2003, 107, 5483-5486.

[17]

Hoque MA, Guzman MI. Photocatalytic activity: Experimental features to report in heterogeneous photocatalysis. Materials 2018, 11, 1990.

[18]

Braslavsky SE, Braun AM, Cassano AE, Emeline AV, Litter MI, Palmisano L, et al. Glossary of terms used in photocatalysis and radiation catalysis (IUPAC Recommendations 2011). Pure Appl. Chem. 2011, 83, 931-1014.

[19]

Alfano OM, Cassano AE, Brandi RJ, Satuf ML. A methodology for modeling slurry photocatalytic reactors for degradation of an organic pollutant in water. In Photocatalysis and Water Purification: From Fundamentals to Recent Applications; Wiley-VCH: Weinheim, Germany, 2013; pp. 335-359. doi:10.1002/9783527645404.ch13.

[20]

Manassero A, Satuf ML, Alfano OM. Evaluation of UV and visible light activity of TiO2 catalysts for water remediation. Chem. Eng. J. 2013, 225, 378-386. doi:10.1016/j.cej.2013.03.097.

[21]

Manassero A, Satuf ML, Alfano OM. Kinetic modeling of the photocatalytic degradation of clofibric acid in a slurry reactor. Environ. Sci. Pollut. Res. 2015, 22, 926-937. doi:10.1007/s11356-014-2682-5.

[22]

el Mehdi Zekri M, Colbeau-Justin C. A mathematical model to describe the photocatalytic reality: What is the probability that a photon does its job? Chem. Eng. J. 2013, 225, 547-557. doi:10.1016/j.cej.2013.03.129.

[23]

Bracco E, Butler M, Carnelli P, Candal R. TiO2 and N-TiO2-photocatalytic degradation of salicylic acid in water: Characterization of transformation products by mass spectrometry. Environ. Sci. Pollut. Res. 2020, 27, 28469-28479.

[24]

Satuf ML, Brandi RJ, Cassano AE, Alfano OM. Experimental method to evaluate the optical properties of aqueous titanium dioxide suspensions. Ind. Eng. Chem. Res. 2005, 44, 6643-6649.

[25]

Murov SL, Carmichael I, Hug GL. Handbook of Photochemistry; CRC Press: Boca Raton, FL, USA, 1993.

[26]

Howell JR, Pinar Mengüc M, Daun K, Siegel R. Thermal Radiation Heat Transfer; CRC Press: Boca Raton, FL, USA, 1993.

[27]

Tolosana-Moranchel Á, Manassero A, Satuf ML, Alfano OM, Casas JA, Bahamonde A. Influence of TiO2-rGO optical properties on the photocatalytic activity and efficiency to photodegrade an emerging pollutant. Appl. Catal. B Environ. 2019, 246, 1-11.

[28]

Yurdakal S, Loddo V, Bayarri Ferrer B, Palmisano G, Augugliaro V, Giménez Farreras J, et al. Optical properties of TiO2 suspensions: Influence of pH and powder concentration on mean particle size. Ind. Eng. Chem. Res. 2007, 46, 7620-7626.

[29]

Regazzoni AE, Mandelbaum P, Matsuyoshi M, Schiller S, Bilmes SA, Blesa MA. Adsorption and photooxidation of salicylic acid on titanium dioxide: A surface complexation description. Langmuir 1998, 14, 868-874. doi:10.1021/la970665n.

[30]

Wang N, Zhu L, Huang Y, She Y, Yu Y, Tang H. Drastically enhanced visible-light photocatalytic degradation of colorless aromatic pollutants over TiO2 via a charge-transfer-complex path: A correlation between chemical structure and degradation rate of the pollutants. J. Catal. 2009, 266, 199-206. doi:10.1016/j.jcat.2009.06.006.

[31]

Park J, Moon GH, Shin KO, Kim J. Oxalate-TiO2 complex-mediated oxidation of pharmaceutical pollutants through ligand-to metal charge transfer under visible light. Chem. Eng. J. 2018, 343, 689-698. doi:10.1016/j.cej.2018.01.078.

[32]

Hoque MA, Barrios Cossio J, Guzman MI. Photocatalysis of Adsorbed Catechol on Degussa P 25 TiO2 at the Air-Solid Interface. J. Phys. Chem. C 2024, 128, 17470-17482.

[33]

Bideau M, Claudel B, Otterbein M. Photocatalysis of formic acid oxidation by oxygen in an aqueous medium. J. Photochem. 1980, 14, 291-302.

[34]

Dijkstra MFJ, Michorius A, Buwalda H, Panneman HJ, Winkelman JGM, Beenackers AACM. Comparison of the efficiency of immobilized and suspended systems in photocatalytic degradation. Catal. Today 2001, 66, 487-494.

[35]

Wang CY, Rabani J, Bahnemann DW, Dohrmann JK. Photonic efficiency and quantum yield of formaldehyde formation from methanol in the presence of various TiO2 photocatalysts. J. Photochem. Photobiol. A Chem. 2002, 148, 169-176.

[36]

Davydov L, Smirniotis PG. Quantification of the primary processes in aqueous heterogeneous photocatalysis using single-stage oxidation reactions. J. Catal. 2000, 191, 105-115.

[37]

Kumar SG, Devi LG. Review on modified TiO2 photocatalysis under UV/visible light: Selected results and related mechanisms on interfacial charge carrier transfer dynamics. J. Phys. Chem. A 2011, 115, 13211-13241.

[38]

Hurum DC, Agrios AG, Gray KA, Rajh T, Thurnauer MC. Explaining the enhanced photocatalytic activity of Degussa P 25 mixed-phase TiO2 using EPR. J. Phys. Chem. B 2003, 107, 4545-4549.

[39]

Wood PM. The potential diagram for oxygen at pH 7. Biochem. J. 1988, 253, 287.

[40]

Shehzad N, Tahir M, Johari K, Murugesan T, Hussain M. A critical review on TiO2 based photocatalytic CO2 reduction system: Strategies to improve efficiency. J. CO2 Util. 2018, 26, 98-122.

[41]

Colucci J, Montalvo V, Hernandez R, Poullet C. Electrochemical oxidation potential of photocatalyst reducing agents. Electrochim. Acta 1999, 44, 2507-2514.

PDF (1539KB)

0

Accesses

0

Citation

Detail

Sections
Recommended

/