حسگر انتخابی بر پایه چارچوبهای آلی کووالانسی پلیآمید برای جذب و شناسایی گازهای سرطانزا در فاز آبی با کمک شبیهسازی مولکولی
محورهای موضوعی : کاربرد نانوساختارها
افسانه قهاری
1
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حیدر رئیسی
2
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احمد حاجی زاده
3
1 - گروه شیمی، دانشکده علوم پایه، پردیس علوم، دانشگاه بیرجند، بیرجند، ایران.
2 - گروه شیمی، دانشکده علوم پایه، پردیس علوم، دانشگاه بیرجند، بیرجند، ایران.
3 - گروه شیمی، دانشکده علوم پایه، پردیس علوم، دانشگاه بیرجند، بیرجند، ایران.
کلید واژه: آلایندههای گازی سمی, نیتروژن دیاکسید(NO₂), نیتروژن تریفلورید(NF₃), هیدرازین(N₂H₄), شبیهسازی دینامیک مولکولی(MD).,
چکیده مقاله :
انتشار آلایندههای گازی سمی مانند نیتروژن دیاکسید(NO₂)، نیتروژن تری فلورید(NF₃) و هیدرازین(N₂H₄) به محیط زیست، بهویژه منابع آبی، از چالشهای زیستمحیطی جدی و رو به گسترش بهشمار میرود. در این مطالعه، از چارچوبهای آلی کووالانسی(COFs) بهعنوان جاذبهای هوشمند با قابلیت تنظیم ساختاری و خواص لومینسانس ذاتی، برای شناسایی، جذب و حذف این سه آلاینده گازی از فاز آبی استفاده شده است. با طراحی هدفمند پیوندهای ایمنی و بهرهگیری از شبیهسازی دینامیک مولکولی(MD)، نحوهی برهمکنش گازهای مورد نظر با دیوارههای منافذ COFs مورد بررسی و تحلیل قرار گرفت. نتایج شبیهسازیها نشان داد که انرژیهای برهمکنش میان COFs و آلایندهها بهترتیب برای NF₃، N₂H₄ و NO₂ برابر با 479/51-، 57/10- و 10/79 کیلوژول بر مول است، که نشاندهندهی تعامل قویتر COFs با مولکول NF₃ میباشد. این یافتهها نقش کلیدی طراحی ساختار COFsها را در بهینهسازی عملکرد آنها برای جذب انتخابی و حسگری گازهای سمی تأیید میکند. در نهایت، این چارچوبها میتوانند بهعنوان گزینهای نویدبخش در توسعهی فناوریهای پاکسازی و پایش محیط زیست مطرح شوند.
The emission of toxic gaseous pollutants such as nitrogen dioxide(NO₂), nitrogen trifluoride(NF₃), and hydrazine(N₂H₄) into the environment, particularly into water resources represents a serious and growing environmental challenge. In this study, covalent organic frameworks(COFs) were employed as intelligent adsorbents with tunable structures and inherent luminescent properties for the detection, adsorption, and removal of these three gaseous pollutants from the aqueous phase. By purposefully designing imine linkages and utilizing molecular dynamics(MD) simulations, the interactions of the target gases with the pore walls of the COFs were investigated and analyzed. The simulation results revealed that the interaction energies between the COFs and the pollutants for NF₃, N₂H₄, and NO₂ were −479.51, −57.10, and −10.79 kJ/mol, respectively, indicating a stronger interaction of COFs with NF₃ molecules. These findings confirm the crucial role of COF structural design in optimizing their performance for selective adsorption and sensing of toxic gases. Ultimately, these frameworks could serve as promising candidates for the development of environmental purification and monitoring technologies.
References:
[1] F. B. Elehinafe, E. A. Aondoakaa, A. F. Akinyemi, O. Agboola, and O. B. Okedere, “Separation processes for the treatment of industrial flue gases--effective methods for global industrial air pollution control,” Heliyon, vol. 10, no. 11, 2024.
[2] G. O. Ofremu et al., “Exploring the relationship between climate change, air pollutants and human health: impacts, adaptation, and mitigation strategies,” Green Energy Resour., p. 100074, 2024.
[3] R. Mesburis et al., “Mitigation of indoor air pollution from air cleaners using a catalyst,” ACS ES\&T Air, 2025.
[4] Z. Han, K.-H. Yu, K.-Y. Wang, and H.-C. Zhou, “Binding Sites of Automobile Exhaust Gases on Metal--Organic Frameworks: Advances and Perspectives,” Energy \& Fuels, vol. 39, no. 13, pp. 6151–6163, 2025.
[5] Y. Wang et al., “Disparities in ambient nitrogen dioxide pollution in the United States,” Proc. Natl. Acad. Sci., vol. 120, no. 16, p. e2208450120, 2023.
[6] X. Li et al., “Trace Detection of Nitrogen Dioxide via Porous Tin Dioxide Nanopods with High Specific Surface Area and Enhanced Charge Transfer,” ACS sensors, 2025.
[7] J. Liu et al., “Ammonia transfers through interprovincial agricultural trade and their health burden implications in China,” Environ. Res. Lett., 2025.
[8] K. Hanif et al., “DFT-based evaluation of C3N2 nanosheet as sensor against industrial gaseous effluents: NH3, NCl3, NF3, COCl2, and SOCl2,” Struct. Chem., pp. 1–18, 2025.
[9] Y. Pan, L. Tang, L. Li, X. Wu, and L. Yan, “A versatile fluorescent probe for the ratiometric detection of hydrazine (N2H4) in water, soil, plant, and food samples,” Environ. Pollut., vol. 359, p. 124766, 2024.
[10] D. Yang et al., “Semi-Crystalline Ruthenium Catalyst for Zero-Drag Hydrogen Production from Hybrid Alkaline Seawater Electrolysis,” Adv. Sci., p. e07848, 2025.
[11] B. Yang, D. T. H. To, E. Resendiz Mendoza, and N. V Myung, “Achieving one part per billion hydrogen sulfide (H2S) level detection through optimizing composition and crystallinity of gold-decorated tungsten trioxide (Au-WO3) nanofibers,” ACS sensors, vol. 9, no. 1, pp. 292–304, 2024.
[12] S. Gong et al., “A Near-Infrared Fluorescent Probe with a Large Stokes Shift for Detecting Hydrogen Sulfide in Environmental Waters, Wine Samples, and Living Systems,” J. Agric. Food Chem., vol. 73, no. 8, pp. 4594–4604, 2025.
[13] M. C. Padole and A. Raj, “NO2 Reduction by HCN, HNC, and CN during Cofiring of Spent Pot Lining in Cement Plant: A DFT and Reaction Kinetics Study,” Ind. \& Eng. Chem. Res., vol. 64, no. 16, pp. 8089–8108, 2025.
[14] C. Yildiz, M. Richter, J. Ströhle, and B. Epple, “Pollutant Formation under Nitrogen and Carbon Dioxide Atmosphere of Torrefied Poplar in an Entrained Flow Reactor,” Energy \& Fuels, vol. 38, no. 9, pp. 8157–8167, 2024.
[15] F. Xu et al., “Enhanced marine VOC emissions driven by terrestrial nutrient inputs and their impact on urban air quality in coastal regions,” Environ. Sci. \& Technol., vol. 59, no. 16, pp. 8140–8154, 2025.
[16] J. Fan, Z. Mo, J. Hang, J. Liang, and X. Wang, “Street Canyon Air Pollution and Pedestrian Health Risk Affected by Household Volatile Chemical Products (VCPs) Emission,” ACS ES\&T Air, 2025.
[17] S. Gooneh-Farahani and M. Anbia, “Strategies to Reduce NOx Emissions from Flue Gas: Trends and Prospects,” Water, Air, \& Soil Pollut., vol. 236, no. 11, pp. 1–48, 2025.
[18] S. Song, Y. J. Kim, S. H. Yoon, J. Hwang, and D. G. Park, “Experimental Investigation of Fundamental Flame Characteristics, N₂O and Nf₃ Decomposition, and Noₓ Formation in Hydrogen/Methane Diffusion Flames,” N₂O Nf₃ Decomposition, Noₓ Form. Hydrog. Diffus. Flames.
[19] T. Sari and D. Akgul, “Hydrazine (Bio) synthesis and separation: Advances, state-of-the-art methods, and patent review,” Biomass Convers. Biorefinery, pp. 1–22, 2025.
[20] K. M. Saidi et al., “Electrochemical and computational study of novel 5-fluoro-2-(methylamino) benzenesulfonamide as an organic catalyst for hydrazine electrooxidation,” Ionics (Kiel)., pp. 1–17, 2025.
[21] M. G. Kallitsakis, K. D. Nikopoulos, and I. N. Lykakis, “Hydrazine as a Reducing Agent in Catalytic Transfer Hydrogenation Processes: Up-to-Date Overview Approaches,” ChemCatChem, vol. 17, no. 8, p. e202401927, 2025.
[22] M. H. Alenazi et al., “Covalent organic frameworks (COFs) for CO2 utilizations,” Carbon Capture Sci. \& Technol., p. 100365, 2025.
[23] J. S. De Vos et al., “High-throughput screening of covalent organic frameworks for carbon capture using machine learning,” Chem. Mater., vol. 36, no. 9, pp. 4315–4330, 2024.
[24] X. Yang et al., “Synergistic linker and linkage of covalent organic frameworks for enhancing gold capture,” Small, vol. 20, no. 44, p. 2404192, 2024.
[25] H. Mabuchi, T. Irie, J. Sakai, S. Das, and Y. Negishi, “Covalent Organic Frameworks: Cutting-Edge Materials for Carbon Dioxide Capture and Water Harvesting from Air,” Chem. Eur. J., vol. 30, no. 6, p. e202303474, 2024.
[26] K. Xu et al., “Polyphosphonate covalent organic frameworks,” Nat. Commun., vol. 15, no. 1, p. 7862, 2024.
[27] X. Liu et al., “Recent advances in covalent organic frameworks (COFs) as a smart sensing material,” Chem. Soc. Rev., vol. 48, no. 20, pp. 5266–5302, 2019.
[28] T. Skorjanc, D. Shetty, and M. Valant, “Covalent organic polymers and frameworks for fluorescence-based sensors,” ACS sensors, vol. 6, no. 4, pp. 1461–1481, 2021.
[29] Y. Wang, T. Wang, Q. Gu, and J. Shang, “Adsorption Removal of NO2 Under Low-Temperature and Low-Concentration Conditions: A Review of Adsorbents and Adsorption Mechanisms,” Adv. Mater., vol. 37, no. 5, p. 2401623, 2025.
[30] S.-M. Wang, H.-L. Lan, G.-W. Guan, and Q.-Y. Yang, “Amino-Functionalized Microporous MOFs for Capturing Greenhouse Gases CF4 and NF3 with Record Selectivity,” ACS Appl. Mater. Interfaces, vol. 14, no. 35, pp. 40072–40081, Sep. 2022, doi: 10.1021/acsami.2c12164.
[31] R. Van Der Jagt et al., “Synthesis and Structure − Property Relationships of Polyimide Covalent Organic Frameworks for Carbon Dioxide Capture and ( Aqueous ) Sodium-Ion Batteries,” 2021, doi: 10.1021/acs.chemmater.0c03218.
[32] T. Makarewicz and R. Kazmierkiewicz, “Molecular dynamics simulation by GROMACS using GUI plugin for PyMOL.” ACS Publications, 2013.
[33] J. Huang and A. D. MacKerell Jr, “CHARMM36 all-atom additive protein force field: Validation based on comparison to NMR data,” J. Comput. Chem., vol. 34, no. 25, pp. 2135–2145, 2013.
[34] A. S. Lemak and N. K. Balabaev, “On the Berendsen thermostat,” Mol. Simul., vol. 13, no. 3, pp. 177–187, 1994.
[35] H. Saito, H. Nagao, K. Nishikawa, and K. Kinugawa, “Molecular collective dynamics in solid para-hydrogen and ortho-deuterium: The Parrinello--Rahman-type path integral centroid molecular dynamics approach,” J. Chem. Phys., vol. 119, no. 2, pp. 953–963, 2003.
[36] Y. Ding et al., “Effect of different retarding agents on the hydration-crystallization process of $β$-hemihydrate gypsum,” Mater. Today Commun., p. 113106, 2025.
[37] A. Ghahari and H. Raissi, “Enhanced Antibiotic Pollutant Capture: Coupling Carbon Nanotubes with Covalent Organic Frameworks,” 2024, doi: 10.1021/acs.jpcc.4c04602.
[38] S. Akhzari, H. Raissi, and A. Ghahari, “Architectural design of 2D covalent organic frameworks (COFs) for pharmaceutical pollutant removal,” npj Clean Water, vol. 7, no. 1, p. 31, 2024, doi: 10.1038/s41545-024-00315-8.
[39] M. Ghasemi et al., “Removal of Pharmaceutical Pollutants from Wastewater Using 2D Covalent Organic Frameworks (COFs): An In Silico Engineering Study,” Ind. \& Eng. Chem. Res., vol. 61, no. 25, pp. 8809–8820, 2022.
[40] D. W. Mc Bride and V. G. J. Rodgers, “Obtaining protein solvent accessible surface area when structural data is unavailable using osmotic pressure,” AIChE J., vol. 58, no. 4, pp. 1012–1017, 2012.