بررسی هم‌زمان فاکتورهای فرآیندی موثر در تخریب رنگ‌زای راکتیو آبی 19 از آب‌های آلوده با کمک نانو اکسیدهای فلزی (TiO2/Fe2O3) بر پایه کلینوپتیلولایت
محورهای موضوعی : آلودگی محیط زیست (آب و فاضلاب)آرسو اریمی 1 , مهرداد فرهادیان 2 , علیرضا سلیمانی‌نظر 3 , نیلا داوری 4
1 - کارشناسی ارشد مهندسی شیمی، دانشکده فنی و مهندسی، دانشگاه اصفهان، اصفهان، ایران
2 - دانشیار گروه مهندسی شیمی، دانشکده فنی و مهندسی، دانشگاه اصفهان، اصفهان، ایران و پژوهشکده محیط زیست، گروه پژوهشی تصفیه آب و بازیافت پساب، دانشگاه اصفهان، اصفهان، ایران *(مسوول مکاتبات)
3 - دانشیار گروه مهندسی شیمی، دانشکده فنی و مهندسی، دانشگاه اصفهان، اصفهان، ایران
4 - کارشناسی ارشد مهندسی شیمی، دانشکده فنی و مهندسی، دانشگاه اصفهان، اصفهان، ایران
کلید واژه: رنگ راکتیو آبی 19, نانوفتوکاتالیست, نانواکسیدهای فلزی تیتانیم و آهن, زئولیت کلینوپتیلولایت,
چکیده مقاله :
زمینه و هدف: در این پژوهش با استفاده از زئولیت طبیعی و تثبیت هم زمان نانو ذرات اکسید آهن (III) و تیتانیم (IV) بر روی آن، نانوفتوکاتالیستی با قدرت تخریبی بیش تر، سنتز شد. عوامل مؤثر و نیز تداخلی در فرآیندی، تعیین شرایط بهینه عملیاتی بر بازده فرآیند تخریب رنگ زای راکتیو آبی 19 مورد بررسی قرار گرفت. روش بررسی: مشخصه یابی نانوفتوکاتالیست سنتز شده با آنالیزهای XRD، XRF، FT-IR، FE-SEM و EDX انجام گرفت. توانایی نانوفتوکاتالیست در تخریب رنگ زای راکتیو آبی 19 با کمک اشعه فرابنفش در طول‌موج 254 نانومتر و به روش طراحی آزمایش‌های تاگوچی مورد بررسی قرار گرفت و عوامل pH اولیه (7-2)، غلظت محلول رنگ زا (200-50 میلی‌گرم بر لیتر)، زمان پرتودهی (120-30 دقیقه) و غلظت نانوفتوکاتالیست (5/1-5/0 گرم بر لیتر) انتخاب شد. یافته‌ها: عوامل pH، غلظت محلول رنگ زا و زمان پرتودهی به ترتیب، بیش ترین اثر را بر بازده واکنش‌ها داشته‌اند.مقادیر بهینه عوامل در تخریب کامل آلاینده برابر با غلظت رنگ زا 50 میلی‌گرم بر لیتر، زمان پرتودهی 120 دقیقه، 2=pH و غلظت نانوفتوکاتالیست 5/1 گرم بر لیتر به دست آمد. بحث و نتیجه گیری: این پژوهش نشان داد که نانوفتوکاتالیست سنتزی بازده قابل قبولی در تخریب آلاینده زیست تخریب ناپذیر دارد.
Background and Objective: In this study, a nanophotocatalyst with more effective efficiency was synthesized by doping of TiO2 and Fe2O3 nanoparticles supported on natural zeolite. Main and interacting factors in the process and determining optimum operating conditions degradation efficiency Reactive Blue 19 dye degradation efficiency were investigated. Method: Synthesized nanophotocatalyst was characterized by XRD, XRF, FT-IR, FE-SEM and EDX analyses. Efficiency of the nanophotocatalyst for the degradation of Reactive Blue 19 dye with UV lamp at 254 nm wavelength was studied via Taguchi method and the parameters were chosen as following: pH (2-7), dye concentration (50-200 mg/l), irradiation time (30-120 min), and nanophotocatalyst concentration (0.5-1.5 g/l). Findings: pH, dye concentration, and irradiation time were the most effective factors in these experiments respectively. The complete degradation of contaminant was achieved at optimal conditions as follows: dye concentration=50 mg/l, irradiation time=120 min, pH=2 and nanophotocatalyst concentration=1.5 g/l. Discussion and Conclusions: This study showed that the synthesized Nano photo catalyst has acceptable efficiency for the degradation of a non-biodegradable pollutant.
1. Arimi A, Farhadian M, Solaimany Nazar AR, Homayoonfal M. Assessment of operating parameters for photocatalytic degradation of a textile dye by Fe2O3/TiO2/clinoptilolite nanocatalyst using Taguchi experimental design. Research on Chemical Intermediates. 2015:1-20.
2. Abou-Gamra ZM, Ahmed MA. Synthesis of mesoporous TiO2–curcumin nanoparticles for photocatalytic degradation of methylene blue dye. Journal of Photochemistry and Photobiology B: Biology. 2016;160:134-41.
3. Eskandari P, Farhadian M, Solaimany Nazar AR. Performance enhancement and optimization of photocatalytic cyanide degradation in aqueous solution using Zn (II) and Fe (III) oxides as nanostructure supported on activated carbon. Journal of Chemical Technology & Biotechnology. 2017;92(9):2360-8.
4. Jaafar NF, Abdul Jalil A, Triwahyono S, Muhd Muhid MN, Sapawe N, Satar MAH, et al. Photodecolorization of methyl orange over α-Fe2O3-supported HY catalysts: The effects of catalyst preparation and dealumination. Chemical Engineering Journal. 2012;191:112-22.
5. Nguyen AT, Juang R-S. Photocatalytic degradation of p-chlorophenol by hybrid H2O2 and TiO2 in aqueous suspensions under UV irradiation. Journal of Environmental Management. 2015;147:271-7.
6. Nikazar M, Gholivand K, Mahanpoor K. Photocatalytic degradation of azo dye Acid Red 114 in water with TiO2 supported on clinoptilolite as a catalyst. Desalination. 2008;219(1):293-300.
7. Davari N, Farhadian M, Solaimany Nazar AR, Homayoonfal M. Degradation of diphenhydramine by the photocatalysts of ZnO/Fe2O3 and TiO2/Fe2O3 based on clinoptilolite: Structural and operational comparison. Journal of Environmental Chemical Engineering. 2017;5(6):5707-20.
8. Wang C, Shi H, Li Y. Synthesis and characterization of natural zeolite supported Cr-doped TiO2 photocatalysts. Applied Surface Science. 2012;258(10):4328-33.
9. Eskandari P, Farhadian M, Solaimany Nazar AR, Jeon B-H. Adsorption and Photodegradation Efficiency of TiO2/Fe2O3/PAC and TiO2/Fe2O3/Zeolite Nanophotocatalysts for the Removal of Cyanide. Industrial & Engineering Chemistry Research. 2019;58(5):2099-112.
10. Yalçın Y, Kılıç M, Çınar Z. Fe+3-doped TiO2: A combined experimental and computational approach to the evaluation of visible light activity. Applied Catalysis B: Environmental. 2010;99(3–4):469-77.
11. Wang C, Shi H, Li Y. Synthesis and characteristics of natural zeolite supported Fe3+-TiO2 photocatalysts. Applied Surface Science. 2011;257(15):6873-7.
12. Rice EW, Bridgewater L, American Public Health A, American Water Works A, Water Environment F. Standard methods for the examination of water and wastewater. Washington, D.C.: American Public Health Association; 2012.
13. Korkuna O, Leboda R, Skubiszewska-Zie¸ba J, Vrublevs’ka T, Gun’ko VM, Ryczkowski J. Structural and physicochemical properties of natural zeolites: clinoptilolite and mordenite. Microporous and Mesoporous Materials. 2006;87(3):243-54.
14. Battisha IK, Afify HH, Ibrahim M. Synthesis of Fe2O3 concentrations and sintering temperature on FTIR and magnetic susceptibility measured from 4 to 300 K of monolith silica gel prepared by sol–gel technique. Journal of Magnetism and Magnetic Materials. 2006;306(2):211-7.
15. Kannaiyan D, Kochuveedu ST, Jang YH, Jang YJ, Lee JY, Lee J, et al. Enhanced Photophysical Properties of Nanopatterned Titania Nanodots/Nanowires upon Hybridization with Silica via Block Copolymer Templated Sol-Gel Process. Polymers. 2010;2(4):490.
16. Rauf MA, Meetani MA, Hisaindee S. An overview on the photocatalytic degradation of azo dyes in the presence of TiO2 doped with selective transition metals. Desalination. 2011;276(1–3):13-27.
17. Goharshadi EK, Hadadian M, Karimi M, Azizi-Toupkanloo H. Photocatalytic degradation of reactive black 5 azo dye by zinc sulfide quantum dots prepared by a sonochemical method. Materials Science in Semiconductor Processing. 2013;16(4):1109-16.
18. Huang M, Xu C, Wu Z, Huang Y, Lin J, Wu J. Photocatalytic discolorization of methyl orange solution by Pt modified TiO2 loaded on natural zeolite. Dyes and Pigments. 2008;77(2):327-34.
19. Yola ML, Eren T, Atar N, Wang S. Adsorptive and photocatalytic removal of reactive dyes by silver nanoparticle-colemanite ore waste. Chemical Engineering Journal. 2014;242:333-40.
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1. Arimi A, Farhadian M, Solaimany Nazar AR, Homayoonfal M. Assessment of operating parameters for photocatalytic degradation of a textile dye by Fe2O3/TiO2/clinoptilolite nanocatalyst using Taguchi experimental design. Research on Chemical Intermediates. 2015:1-20.
2. Abou-Gamra ZM, Ahmed MA. Synthesis of mesoporous TiO2–curcumin nanoparticles for photocatalytic degradation of methylene blue dye. Journal of Photochemistry and Photobiology B: Biology. 2016;160:134-41.
3. Eskandari P, Farhadian M, Solaimany Nazar AR. Performance enhancement and optimization of photocatalytic cyanide degradation in aqueous solution using Zn (II) and Fe (III) oxides as nanostructure supported on activated carbon. Journal of Chemical Technology & Biotechnology. 2017;92(9):2360-8.
4. Jaafar NF, Abdul Jalil A, Triwahyono S, Muhd Muhid MN, Sapawe N, Satar MAH, et al. Photodecolorization of methyl orange over α-Fe2O3-supported HY catalysts: The effects of catalyst preparation and dealumination. Chemical Engineering Journal. 2012;191:112-22.
5. Nguyen AT, Juang R-S. Photocatalytic degradation of p-chlorophenol by hybrid H2O2 and TiO2 in aqueous suspensions under UV irradiation. Journal of Environmental Management. 2015;147:271-7.
6. Nikazar M, Gholivand K, Mahanpoor K. Photocatalytic degradation of azo dye Acid Red 114 in water with TiO2 supported on clinoptilolite as a catalyst. Desalination. 2008;219(1):293-300.
7. Davari N, Farhadian M, Solaimany Nazar AR, Homayoonfal M. Degradation of diphenhydramine by the photocatalysts of ZnO/Fe2O3 and TiO2/Fe2O3 based on clinoptilolite: Structural and operational comparison. Journal of Environmental Chemical Engineering. 2017;5(6):5707-20.
8. Wang C, Shi H, Li Y. Synthesis and characterization of natural zeolite supported Cr-doped TiO2 photocatalysts. Applied Surface Science. 2012;258(10):4328-33.
9. Eskandari P, Farhadian M, Solaimany Nazar AR, Jeon B-H. Adsorption and Photodegradation Efficiency of TiO2/Fe2O3/PAC and TiO2/Fe2O3/Zeolite Nanophotocatalysts for the Removal of Cyanide. Industrial & Engineering Chemistry Research. 2019;58(5):2099-112.
10. Yalçın Y, Kılıç M, Çınar Z. Fe+3-doped TiO2: A combined experimental and computational approach to the evaluation of visible light activity. Applied Catalysis B: Environmental. 2010;99(3–4):469-77.
11. Wang C, Shi H, Li Y. Synthesis and characteristics of natural zeolite supported Fe3+-TiO2 photocatalysts. Applied Surface Science. 2011;257(15):6873-7.
12. Rice EW, Bridgewater L, American Public Health A, American Water Works A, Water Environment F. Standard methods for the examination of water and wastewater. Washington, D.C.: American Public Health Association; 2012.
13. Korkuna O, Leboda R, Skubiszewska-Zie¸ba J, Vrublevs’ka T, Gun’ko VM, Ryczkowski J. Structural and physicochemical properties of natural zeolites: clinoptilolite and mordenite. Microporous and Mesoporous Materials. 2006;87(3):243-54.
14. Battisha IK, Afify HH, Ibrahim M. Synthesis of Fe2O3 concentrations and sintering temperature on FTIR and magnetic susceptibility measured from 4 to 300 K of monolith silica gel prepared by sol–gel technique. Journal of Magnetism and Magnetic Materials. 2006;306(2):211-7.
15. Kannaiyan D, Kochuveedu ST, Jang YH, Jang YJ, Lee JY, Lee J, et al. Enhanced Photophysical Properties of Nanopatterned Titania Nanodots/Nanowires upon Hybridization with Silica via Block Copolymer Templated Sol-Gel Process. Polymers. 2010;2(4):490.
16. Rauf MA, Meetani MA, Hisaindee S. An overview on the photocatalytic degradation of azo dyes in the presence of TiO2 doped with selective transition metals. Desalination. 2011;276(1–3):13-27.
17. Goharshadi EK, Hadadian M, Karimi M, Azizi-Toupkanloo H. Photocatalytic degradation of reactive black 5 azo dye by zinc sulfide quantum dots prepared by a sonochemical method. Materials Science in Semiconductor Processing. 2013;16(4):1109-16.
18. Huang M, Xu C, Wu Z, Huang Y, Lin J, Wu J. Photocatalytic discolorization of methyl orange solution by Pt modified TiO2 loaded on natural zeolite. Dyes and Pigments. 2008;77(2):327-34.
19. Yola ML, Eren T, Atar N, Wang S. Adsorptive and photocatalytic removal of reactive dyes by silver nanoparticle-colemanite ore waste. Chemical Engineering Journal. 2014;242:333-40.
