Effect of carrier on the performance of copper based catalyst for selective catalytic reduction of NO with NH3 at low temperature
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摘要: 采用浸渍法制备载体负载铜氧化物催化剂。通过XRD、TG-MS、XPS、NO-TPD、NH3-TPD和H2-TPR等手段对催化剂进行表征,考察了有氧条件下载体对催化剂NH3-SCR低温脱硝性能的影响。结果表明,铜物种在载体上以CuO和Cu2O形式共存,载体影响铜物种的分散性和氧化态,影响催化剂酸性、氧化还原性和对反应物的吸脱附能力。Cu/HZSM-5催化剂,铜物种分散度高,氧化还原性能好,具有适宜的酸性和酸量,对反应物有良好的吸附-脱附性能,在NH3-SCR脱硝反应中具有较好的催化活性,反应温度低,T50和T90分别为137和165℃,活性窗口温度宽,NO转化率高于90%的温度为165-358℃。Abstract: The catalysts of supported copper oxide were prepared by impregnation method, which were characterized by XRD, TG-MS, XPS, NO-TPD, NH3-TPD and H2-TPR and the effect of carrier on the performance of catalysts for the selective catalytic reduction of NO with NH3 at low-temperature in the presence of oxygen was investigated.The results show that the copper species exist in the form of CuO and Cu2O on carriers.The dispersion and oxidation state of copper species, the acidity and redox ability of the catalysts and the performance of adsorption/desorption are affected by the carriers.The Cu/HZSM-5 catalyst with highly dispersed copper speicies has excellent redox properties, suitable acidity and acid capacity, and good adsorption/desorption performance for reactants, which shows a good catalytic activity in the NH3-SCR denitrification reaction.The reaction temperature is lower, T50 and T90 is 137 and 165℃, respectively, and the active window temperature is wide.The temperature range for the NO conversion of over 90% is 165-358℃.
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Key words:
- carrier /
- copper oxide /
- NH3-SCR /
- low-temperature denitrification
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表 1 催化剂的XPS和BET表征
Table 1 XPS and BET data of the catalysts
Sample Specific surface area
A/(m2·g-1)Percentage of oxygen species
derived from O 1s analysis /%Binding energy
E/eVCu2+/Cu+ Oα Oβ Cu+ Cu2+ HZSM-5 388 73.31 26.69 - - - ZRP-5 360 70.24 29.76 - - - γ-Al2O3 294 64.05 35.95 - - - Cu/HZSM-5 328 76.61 23.39 932.85 934.99 0.489 7 Cu/ZRP-5 290 71.93 28.07 932.50 934.25 0.825 2 Cu/γ-Al2O3 249 64.82 35.18 932.95 934.65 1.023 8 表 2 催化剂上H2还原峰面积和温度
Table 2 Peak area and peak temperature of H2 reduction with the catalysts
Peak Area/(a.u.)(Temperature t/℃) Cu/HZSM-5 Cu/ZRP Cu/γ-Al2O3 1 3.4(204) 1.7(215) 4.0(290) 2 2.1(270) 7.4(280) 9.8(338) 3 2.8(328) 3.5(348) 9.0(430) 4 5.2(474) 0.75(430) 1.3(556) Total 13.5 13.4 24.1 -
[1] 王虹, 李滨, 卢学斌, 李翠清, 丁福臣, 宋永吉. 富氧条件下Co/MOR催化剂上甲烷选择催化还原NO[J]. 燃料化学学报, 2015, 43(9):1106-1112. http://rlhxxb.sxicc.ac.cn/CN/abstract/abstract18696.shtml(WANG Hong, LI Bin, LU Xue-bin, LI Cui-qing, DING Fu-chen, SONG Yong-ji. Selective catalytic reduction of NO by methane over the Co/MOR catalysts in the presence of oxygen[J]. J Fuel Chem Technol, 2015, 43(9):1106-1112.) http://rlhxxb.sxicc.ac.cn/CN/abstract/abstract18696.shtml [2] 任翠涛, 胡颖智, 魏浩宇, 李滨, 王虹, 丁福臣, 李翠清, 宋永吉. SO2存在条件下M/REY催化剂NH3选择性还原NO性能研究[J]. 燃料化学学报, 2013, 41(10):1241-1247. http://rlhxxb.sxicc.ac.cn/CN/abstract/abstract18280.shtml(REN Cui-tao, HU Ying-zhi, WEI Hao-yu, LI Bin, WANG Hong, DING Fu-chen, LI Cui-qing, SONG Yong-ji. NH3 selective catalytic reduction of NO over M/REY catalysts in presence of SO2[J]. J Fuel Chem Technol, 2013, 41(10):1241-1247.) http://rlhxxb.sxicc.ac.cn/CN/abstract/abstract18280.shtml [3] PANAHI P N, SALARI D, NIAEI A, MOUSAVI S M. NO reductionover nanostructure M-Cu/ZSM-5 (M:Cr, Mn, Co and Fe)bimetallic catalysts and optimization of catalyst preparationby RSM[J]. J Ind Eng Chem, 2013, 19(6):1793-1799. doi: 10.1016/j.jiec.2013.02.022 [4] YU T, FAN D Q, HAO T. The effect of various templates on the NH3-SCR activities over Cu/SAPO-34 catalysts[J]. J Chem Eng, 2014, 243:159-168. doi: 10.1016/j.cej.2014.01.008 [5] LIU Q, LIU Z, SU J. Al2O3-coated cordierite honeycomb supported CuO catalyst for selective catalytic reduction of NO by NH3:Surface properties and reaction mechanism[J]. Catal Today, 2010, 158(3/4):370-376. https://www.researchgate.net/publication/289381620_Simultaneous_removal_of_SO2_and_NO_from_flue_gas_using_CuOg-Al2O3_catalyst [6] LEI Z G, LONG A B, JIA M R, LIU X Y. Experimental and kineticstudy of selective catalytic reduction of NO with NH3 over CuO/Al2O3/cordierite catalyst[J]. Chin J Chem Eng, 2010, 18(5):721-729. doi: 10.1016/S1004-9541(09)60120-8 [7] VENNESTROM P N R, JANSSENS T V W, KUSTOV A, GRILL M, PUIG-MOLINA A, LUNDEGAARD L F, TIRUVALAM R R, CONCEPCION P, CORMA A. Influence of lattice stability on hydrothermal deactivation of Cu-ZSM-5 and Cu-IM-5 zeolites for selective catalytic reduction of NOx, by NH3[J]. J Catal, 2014, 309(6):477-490. [8] PEREDA-AYO B, DE LA TORRE U, ILLAN-GOMEZ M J, BUENO-LOPEZ A, GONZALEZ-VELASCO J R. Role of the different copper species on the activity of Cu/zeolite catalysts for SCR of NOx, with NH3[J]. Appl Catal B:Environ, 2014, 147(7):420-428. [9] CHEN B H, XU R N, ZHANG R D, LIU N. Economical way to synthesize SSZ-13 with abundant ion-exchanged Cu+ for an extraordinary performance in selective catalytic reduction (SCR) of NOx, by ammonia[J]. Environ Sci Technol, 2014, 48(23):13909-13916. doi: 10.1021/es503707c [10] SI Z C, WENG D, WU X D, LI J, LI G. Structure, acidity and activity of CuOx, /WOx, -ZrO2 catalyst for selective catalytic reduction of NO by NH3[J]. J Catal, 2010, 271(1):43-51. doi: 10.1016/j.jcat.2010.01.025 [11] BONINGARI T, PAPPAS D K, ETTIREDDY P R, KOTRBA A, SMIRNIOTIS P G. Influence of SiO2 on M/TiO2 (M=Cu, Mn, and Ce) formulations for low-temperature Selective catalytic reduction of NOx, with NH3:Surface properties and key components in relation to the activity of NOx, reduction[J]. Ind Eng Chem Res, 2015, 54(8):2261-2273. doi: 10.1021/ie504709j [12] 王栋, 吴惊坤, 牛胜利, 路春美, 徐丽婷, 于贺伟, 李婧. Sn、Ti 掺杂改性γ, -Fe2O3催化剂结构及NH3-SCR 脱硝活性研究[J]. 燃料化学学报, 2015, 43(7):876-883. http://rlhxxb.sxicc.ac.cn/CN/abstract/abstract18666.shtml(WANG Dong, WU Jing-kun, NIU Sheng-li, LU Chun-mei, XU Li-ting, YU He-wei, LI Jing. Structural property of γ, -Fe2O3 catalysts doped with Sn and Ti and their activity in the selective catalytic reduction of NOx, [J]. J Fuel Chem Technol, 2015, 43(7):876-883.) http://rlhxxb.sxicc.ac.cn/CN/abstract/abstract18666.shtml [13] YANG S J, LI J H, WANG C Z, CHEN J H, MA L, CHANG H Z, CHEN L, PENG P, YAN N Q. Fe-Ti spinel for the selective catalytic reduction of NO with NH3:Mechanism and structure-activity relationship[J]. Appl Catal B:Environ, 2012, 117-118(18):73-80. https://www.researchgate.net/publication/257370778_Fe-Ti_spinel_for_the_selective_catalytic_reduction_of_NO_with_NH3_Mechanism_and_structure-activity_relationship [14] MOUSAVI S M, NIAEI A, GÓEZ M J I, SALARI D, PANAHI P N, ABALADEJO-FUENTES V. Characterization and activity of alkaline earthmetals loaded CeO2-MOx, (M=Mn, Fe) mixed oxides in catalytic reduction of NO[J]. Mater Chem Phys, 2014, 143(3):921-928. doi: 10.1016/j.matchemphys.2013.09.017 [15] LIU F, HE H, ZHANG C, SHAN W P, SHI X Y. Mechanism of the selective catalytic reduction of NOx, with NH3 over environmental-friendly iron titanate catalyst[J]. Catal Today, 2011, 175(1):18-25. doi: 10.1016/j.cattod.2011.02.049 [16] BRANDENBERGER S, KRÖCHER O, CASAPU M, TISSLER A, ALTHOFF R. Hydrothermal deactivation of Fe-ZSM-5 catalysts for the selective catalytic reduction of NO with NH3[J]. Appl Catal B:Environ, 2011, 101(3):649-659. https://www.researchgate.net/publication/251617491_Hydrothermal_deactivation_of_Fe-ZSM-5_catalysts_for_the_selective_catalytic_reduction_of_NO_with_NH_3 [17] ELLMERS I, VÉEZ R P, BENTRUP U, BRVCKNER A, GRVNERT W. Oxidation and selective reduction of NO over Fe-ZSM-5-How related are these reactions[J]. J Catal, 2014, 311:199-211. doi: 10.1016/j.jcat.2013.11.024 [18] TANG X L, HAO J M, XU W G, LI J H. Low temperature selective catalytic reduction of NOx, with NH3 over amorphous MnOx, catalysts prepared by three methods[J]. Catal Commun, 2007, 8(3):329-3341. doi: 10.1016/j.catcom.2006.06.025 [19] JIANG B Q, LIU Y, WU Z B. Low-temperature selective catalytic reduction of NO on MnOx, /TiO2 prepared by different methods[J]. J Hazard Mater, 2009, 162(2/3):1249-12541. [20] KIM M S, CHUNG S H, YOO C J, LEE M S, CHO I H, LEE D W, LEE K Y. Catalytic reduction of nitrate in water over Pd-Cu/TiO2 catalyst:Effect of the strong metal-support interaction (SMSI) on the catalytic activity[J]. Appl Catal B:Environ, 2013, 142-143(5):354-361. https://koreauniv.pure.elsevier.com/en/publications/catalytic-reduction-of-nitrate-in-water-over-pd-cutiosub2sub-cata [21] ZHANG G Q, LI Z, ZHENG H Y, FU T J, JU Y B, WANG Y C. Influence of the surface oxygenated groups of activated carbon on preparation of a nano Cu/AC catalyst and heterogeneous catalysis in the oxidative carbonylation of methanol[J]. Appl Catal B:Environ, 2015, 179:95-105. doi: 10.1016/j.apcatb.2015.05.001 [22] CHARY K V R, SAGAR G V, NARESH D, SEELA K K, SRIDHAR B. Characterization and reactivity of copper oxide catalysts supported on TiO2-ZrO2[J]. J Phys Chem B, 2005, 109(19):9437-9444. doi: 10.1021/jp0500135 [23] ZOU H B, CHEN S Z, LIN W M. Effect of pretreatment methods on the performance of Cu-Zr-Ce-O catalyst for CO selective oxidation[J]. J Nat Gas Chem, 2008, 17(2):208-211. doi: 10.1016/S1003-9953(08)60053-5 [24] LALITHA K, SADANANDAM G, KUMARI V D, SUBRAHMANYAM M, SREEDHAR B, HEBALKAR N Y. Highly stabilized and finely dispersed Cu2O/TiO2:Apromising visible sensitive photocatalyst for continuous production of hydrogen from glycerol:Water mixtures[J]. J Phys Chem C, 2010, 114(50):22181-22189. doi: 10.1021/jp107405u [25] XIN B F, WANG P, DING D D, LIU J, REN Z Y, FU H G. Effect of surface species on Cu-TiO2 photocatalytic activity[J]. Appl Surf Sci, 2008, 254(9):2569-2574. doi: 10.1016/j.apsusc.2007.09.002 [26] BAGHRICHE O, RTIMI S, PULGARIN C, SANJINES R, KIWI J. Innovative TiO2/Cu nanosurfaces inactivating bacteria in the minute range under low-intensity actinic light[J]. ACS Appl Mater Inter, 2012, 4(10):5234-5240. doi: 10.1021/am301153j [27] YAOX J, ZHANG L, LI L, LIU L C, CAOY, DONG X, GAO F, DENG Y, TANG J, CHEN Z, DONG L, CHEN Y. Investigation of the structure, acidity, and catalytic performance of CuO/Ti0.95Ce0.05O2 catalyst for the selective catalytic reduction of NO by NH3 at low temperature[J]. Appl Catal B:Environ, 2014, 150-151(11):315-329. [28] SIZ C, WENG D, WUX D, JIANG Y, WANG B. Synergistic effects between copper and tungsten on the structural and acidic properties of CuOx, /WOx, -ZrO2 catalyst[J]. Catal Sci Technol, 2011, 1(3):453-461. doi: 10.1039/c0cy00086h [29] ČAPEK L, DĚDEČEK J, WICHTERLOVÁ B, CIDER L, JOBSON E, TOKAROVÁ V. Cu-ZSM-5 zeolite highly active in reduction of NO with decane:Effect of zeolite structural parameters on the catalyst performance[J]. Appl Catal B:Environ, 2005, 60(3/4):147-153. [30] NDONGL B B, IBONDOU M P, GU X G, LU S G, QIU Z F, SUI Q, MBADINGA S M. Enhanced photocatalytic activity of TiO2nanosheetsby doping with Cu for chlorinated solvent pollutants degradation[J]. Ind Eng Chem Res, 2014, 53(4):1368-1376. doi: 10.1021/ie403405z [31] LANDI G, LISI L, PIRONE R, TORTORELLI M, RUSSO G. NO decomposition over La-doped Cu-ZSM5 monolith under adsorption-reaction conditions[J]. Appl Catal A:Gen, 2013, 464-465(16):61-67. https://www.researchgate.net/publication/257374248_NO_decomposition_over_La-doped_Cu-ZSM5_monolith_under_adsorption-reaction_conditions [32] MA L, CHENG Y S, CAVATAIO G, MCCABE R W, FU L X, LI J H. Characterization of commercial Cu-SSZ-13 and Cu-SAPO-34 catalysts with hydrothermal treatment for NH3-SCR of NOx, in diesel exhaust[J]. Chem Eng J, 2013, 225(3):323-330. [33] OCHONSKA J, MCCLYMONT D, JODŁOWSKI P J, KNAPIK A, GIL B, MAKOWSKI W, ŁASOCHA W, KOŁODZIEJ A, KOLACZKOWSKI S T, ŁOJEWSKA J. Copper exchanged ultrastable zeolite Y-A catalyst for NH3-SCR of NOx, from stationary biogas engines[J]. Catal Today, 2012, 191(1):6-11. doi: 10.1016/j.cattod.2012.06.010 [34] NEYLON M K, MARSHALL C L, KROPF A J. In situ EXAFS analysis of the temperature-programmed reduction of Cu-ZSM-5[J]. J Am Chem Soc, 2002, 124(19):5457-5465. doi: 10.1021/ja0176696