Oxidation kinetics of adsorbent-decorated Fe-based oxygen carrier for chemical-looping combustion
-
摘要: 研究了吸附剂修饰合成Fe2O3/Al2O3的氧化动力学。其中,吸附剂(K2O、Na2O、CaO)用于控制化学链燃烧过程中有毒氯化物、硫化物以及重金属的排放。首先在热重分析仪(TGA)上利用合成气作为还原气氛使氧载体呈还原态(FeO/Al2O3),在空气气氛下进行了原FeO/Al2O3以及三种吸附剂修饰FeO/Al2O3的氧化实验,实验温度分别为850、875、900和925℃。通过八种等温动力学模型对900℃下原FeO/Al2O3的氧化过程进行了分析。结果表明,phase boundary-controlled(contracting cylinder)模型能够很好地描述其氧化过程(FeO向Fe2O3转化过程)。利用该模型分别计算了原FeO/Al2O3、K2O修饰FeO/Al2O3、Na2O修饰FeO/Al2O3和CaO修饰FeO/Al2O3的氧化动力学参数,其表观活化能分别为13.71、20.21、21.62和24.20 kJ/mol。通过进行比较依据动力学参数计算得到的转化率随时间的函数以及实验获得的转化率随时间的函数,进一步证实了phase boundary-controlled(contracting cylinder)模型的可靠性以及相应动力学参数的准确性。
-
关键词:
- 化学链燃烧 /
- 氧化动力学 /
- 吸附剂修饰铁基氧载体 /
- TGA
Abstract: Adsorbent-decorated Fe2O3/Al2O3 as oxygen carrier (OC) was proposed for restraining the emission of chloride, sulfide and heavy metals during the chemical-looping combustion process of gaseous or solid fuels. Three adsorbents (K2O, Na2O and CaO) were selected for decorating these OC particles. First, the raw Fe2O3/Al2O3 and three adsorbent-decorated Fe2O3/Al2O3 were reduced by synthesis gas and then the oxidation kinetics of four reduced OCs (raw FeO/Al2O3 and three adsorbent-decorated FeO/Al2O3) were investigated by using thermogravimetric analysis (TGA) technique in air atmosphere at four temperatures (850, 875, 900 and 925℃). It was found that the translation of FeO to Fe2O3 can be described by the phase boundary-controlled (contracting cylinder) model, and the apparent activation energy (E) was calculated to be 13.71, 20.21, 21.62 and 24.20 kJ/mol for raw FeO/Al2O3, K2O-decorated FeO/Al2O3, Na2O-decorated FeO/Al2O3 and CaO-decorated FeO/Al2O3, respectively. Last, the reaction mechanism was evaluated through comparing the calculated data from the obtained kinetic parameters and the experimental results, which demonstrated the reliability of the phase boundary-controlled (contracting cylinder) model.-
Key words:
- chemical looping combustion /
- oxidation kinetics /
- adsorbent-decorated Fe2O3/Al2O3 /
- TGA
-
表 1 不同反应动力学机理的动力学方程
Table 1 Kinetic equations for different reaction mechanisms
Reaction mechanism Integral form G(x)=kt 1-D diffusion x2 2-D diffusion x+(1-x)ln(1-x) 3-D diffusion-Jander [1-(1-x)1/3]2 Phase boundary-controlled
(contracting cylinder)1-(1-x)1/2 Phase boundary-controlled
(contracting sphere)1-(1-x)1/3 First order reaction -ln(1-x) 2-D growth of nuclei [-ln(1-x)]1/2 3-D growth of nuclei [-ln(1-x)]1/3 表 2 八种反应机理模型对900℃下原FeO/Al2O3氧化过程的线性拟合参数
Table 2 Linear fitting parameters of eight reaction mechanisms for the oxidation process of raw FeO/Al2O3 by air at 900℃
Reaction mechanism Fitting Line R2 1-D diffusion y=-0.17816+0.02369x 0.98406 2-D diffusion y=-0.16251+0.01842x 0.96435 3-D diffusion-Jander y=-0.07135+0.00703x 0.92741 Phase boundary-controlled
(contracting cylinder)y=-0.04508+0.01769x 0.99487 Phase boundary-controlled
(contracting sphere)y=-0.04989+0.01371x 0.98946 First order reaction y=-0.31875+0.05665x 0.97216 2-D growth of nuclei y=-0.21116+0.03167x 0.9973 3-D growth of nuclei y=-0.43192+0.02236x 0.99892 表 3 四种氧载体与空气反应的线性拟合参数
Table 3 Linear fitting parameters of the oxidation process for four OCs reacting with air
Sample Temperature t/℃ Fitting line R2 Raw FeO/Al2O3 850 y=-0.04555+0.01645x 0.99395 875 y=-0.04345+0.01719x 0.995 900 y=-0.04508+0.01769x 0.99487 925 y=-0.04721+0.01804x 0.99427 K2O-decorated FeO/Al2O3 850 y=-0.04905+0.0147x 0.99359 875 y=-0.03443+0.01564x 0.99516 900 y=-0.05703+0.01592x 0.99403 925 y=-0.0431+0.01699x 0.99627 Na2O-decorated FeO/Al2O3 850 y=-0.04227+0.01465x 0.99528 875 y=-0.04824+0.01509x 0.99521 900 y=-0.04827+0.01588x 0.99723 925 y=-0.04272+0.01693x 0.99339 CaO-decorated FeO/Al2O3 850 y=-0.03476+0.0128x 0.99805 875 y=-0.04066+0.01375x 0.99526 900 y=-0.04435+0.0144x 0.99499 925 y=-0.05129+0.01509x 0.99489 表 4 不同氧载体与空气在850-925℃条件下的氧化动力学参数
Table 4 Parameters of oxidation kinetics for four OCs reacting with air between 850-925℃
Sample E/(kJ·mol-1) A Raw FeO/Al2O3 13.71 0.07183 K2O-decorated FeO/Al2O3 20.21 0.12848 Na2O-decorated FeO/Al2O3 21.62 0.14702 CaO-decorated FeO/Al2O3 24.20 0.17198 -
[1] SAHIR A H,LIGHTY J S,SOHN H Y.Kinetics of copper oxidation in the air reactor of a chemical looping combustion system using the law of additive reaction times[J].Ind Eng Chem Res,2011,50(23):566-580. https://www.researchgate.net/publication/231377528_Kinetics_of_Copper_Oxidation_in_the_Air_Reactor_of_a_Chemical_Looping_Combustion_System_using_the_Law_of_Additive_Reaction_Times [2] NASR S,PLUCKNETT K P.Kinetics of iron ore reduction by methane for chemical looping combustion[J].Energy Fuels,2014,28(2):1387-1395. doi: 10.1021/ef402142q [3] DUESO C,ORTIZ M,ABAD A,GARCIA-LABIANO F,DE DIEGO L F,GAYAN P,ADANEZ J.Reduction and oxidation kinetics of nickel-based oxygen-carriers for chemical-looping combustion and chemical-looping reforming[J].Chem Eng J,2012,188(16):142-154. https://www.researchgate.net/publication/224953012_Reduction_and_oxidation_kinetics_of_nickel-based_oxygen-carrier_for_chemical-looping_combustion_and_chemical-looping_reforming?_sg=GRVSDhyybm9ZoKZOyZqbly8PPmFov8GeB5ZLkqjMRAlAdEE2y-qLVA0ZyJ6FYXaEupXoSRVkxnhuCmeGXnOnVA [4] XIAO R,CHEN L Y,SAHA C,ZHANG S.Pressurized chemical-looping combustion of coal using an iron ore as oxygen carrier in a pilot-scale unit[J].Inter J Greenh Gas Con,2012,10(5):363-373. https://www.researchgate.net/publication/257692020_Pressurized_chemical-looping_combustion_of_coal_using_an_iron_ore_as_oxygen_carrier_in_a_pilot-scale_unit [5] BERGUERAND N,LYNGFELT A.Design and operation of a 10kWth chemical-looping combustor for solid fuels-Testing with South African coal[J].Fuel,2008,87(12):2713-2726. doi: 10.1016/j.fuel.2008.03.008 [6] YU Z L,LI C Y,FANG Y T,HUANG J J,WANG Z Q.Reduction rate enhancements for coal direct chemical looping combustion with an iron oxide oxygen carrier[J].Energy Fuels,2012,26(4):128-134. https://www.researchgate.net/publication/263947229_Reduction_Rate_Enhancements_for_Coal_Direct_Chemical_Looping_Combustion_with_an_Iron_Oxide_Oxygen_Carrier [7] GU H M,SHEN L H,XIAO J,ZHANG S W,SONG T,CHEN D Q.Iron ore as oxygen carrier improved with potassium for chemical looping combustion of anthracite coal[J].Combust Flame,2012,159(7):2480-2490. doi: 10.1016/j.combustflame.2012.03.013 [8] XIAN R,SONG Q L,SONG M,LU Z J,ZHANG S A,SHEN L H.Pressurized chemical-looping combustion of coal with an iron ore-based oxygen carrier[J].Combust Flame,2010,157(6):1140-1153. doi: 10.1016/j.combustflame.2010.01.007 [9] SONG T,SHEN T X,SHEN L H,XIAN J,GU H M,ZHANG S W.Evaluation of hematite oxygen carrier in chemical-looping combustion of coal[J].Fuel,2013,104(2):244-252. https://www.researchgate.net/publication/256712201_Evaluation_of_hematite_oxygen_carrier_in_chemical-looping_combustion_of_coal [10] PECHO J,SCHILDHAUER T J,STURZENEGGER A,BIOLLAZ S,WOKAUN A.Reactive bed materials for improved biomass gasification in a circulating fluidised bed reactor[J].Chem Eng Sci,2008,63(9):2465-2476. doi: 10.1016/j.ces.2008.02.001 [11] ZHU H M,JIANG X G,YAN J H,CHI Y,CEN K F.TG-FTIR analysis of PVC thermal degradation and HCl removal[J].J Anal Appl Pyrolysis,2008,82(1):1-9. doi: 10.1016/j.jaap.2007.11.011 [12] SOLUNKE R D,VESER G.Integrating desulfurization with CO2-capture in chemical-looping combustion[J].Fuel,2011,90(2):608-617. doi: 10.1016/j.fuel.2010.09.039 [13] TAFUR-MARINOS J A,GINEPRO M,PASTERRO L,TORAZZO A,PASCHETTA E,FABBRI D,ZELANO V.Comparison of inorganic constituents in bottom and fly residues from pelletised wood pyro-gasification[J].Fuel,2014,119(1):157-162. https://www.researchgate.net/publication/259284027_Comparison_of_inorganic_constituents_in_bottom_and_fly_residues_from_pelletised_wood_pyro-gasification [14] WANG J X,ZHAO H B.Chemical looping dechlorination through adsorbent-decorated Fe2O3/Al2O3 oxygen carriers[J].Combust Flame,2015,162(10):3503-3515. doi: 10.1016/j.combustflame.2015.06.008 [15] GU H M,SHEN L H,XIAO J,ZHANG S W,SONG T,CHEN D Q.Evaluation of the effect of sulfur on iron-ore oxygen carrier in chemical-looping combustion[J].Ind Eng Chem Res,2013,52(5):1795-1805. doi: 10.1021/ie303023w [16] HAN Y,HWANG G,KIM D,PARK S,KIM H.Porous Ca-based bead sorbents for simultaneous removal of SO2,fine particulate matters,and heavy metals from pilot plant sewage sludge incineration[J].J Hazard Mater,2015,283:44-52. doi: 10.1016/j.jhazmat.2014.09.009 [17] NOWAK B,PESSL A,ASCHENBRENNER P,SZENTANNAI P,MATTENBERGER H,RECHBERGER H,HERMANN L,WINTER F.Heavy metal removal from municipal solid waste fly ash by chlorination and thermal treatment[J].J Hazard Mater,2010,179(1/3):323-331. https://www.researchgate.net/publication/42806150_Heavy_metal_removal_from_municipal_solid_waste_fly_ash_by_chlorination_and_thermal_treatment [18] LIU Z S,PENG T H,LIN C L.Effects of bed material size distribution,operating conditions and agglomeration phenomenon on heavy metal emission in fluidized bed combustion process[J].Waste Manage,2012,32(3):417-425. doi: 10.1016/j.wasman.2011.10.033 [19] ZHANG Y X,DOROODCHI E,MOGHTADERI B.Reduction Kinetics of Fe2O3/Al2O3 by ultralow concentration methane under conditions pertinent to chemical looping combustion[J].Energy Fuels,2015,29(1):337-345. doi: 10.1021/ef5024252 [20] MONAZAM E R,BREAULT R W,SIRIWARDANE R,MILLER D D.Thermogravimetric analysis of modified hematite by methane (CH4) for chemical-looping combustion:A global kinetics mechanism[J].Ind Eng Chem Res,2013,52(42):14808-14816. doi: 10.1021/ie4024116 [21] MONAZAM E R,BREAULT R W,SIRIWARDANE R.Kinetics of magnetite (Fe3O4) oxidation to hematite (Fe2O3) in air for chemical looping combustion[J].Ind Eng Chem Res,2014,53(34):13320-13328. [22] MONAZAM E R,BREAULT R W,SIRIWARDANE R.Kinetics of hematite to wustite by hydrogen for chemical looping combustion[J].Energy Fuels,2014,28(8):5406-5414. doi: 10.1021/ef501100b [23] WANG C B,WANG J X,LEI M,GAO H N.Investigations on combustion and NO emission characteristics of coal and biomass blends[J].Energy Fuels,2013,27(10):6185-6190. doi: 10.1021/ef401589k [24] CHIU P C,KU Y,WU H C,KUO Y L,TSENG Y H.Chemical looping combustion of polyurethane and polypropylene in an annular dual-tube moving bed reactor with iron-based oxygen carrier[J].Fuel,2014,135(11):146-152. [25] MONAZAM E R,BREAULT R W,SIRIWARDANE R,RICHARDS G,CARPENTER S.Kinetics of the reduction of hematite (Fe2O3) by methane (CH4) during chemical looping combustion:A global mechanism[J].Chem Eng J,2013,232:478-487. doi: 10.1016/j.cej.2013.07.091 [26] 熊绍武,张守玉,吴巧美,郭熙,董爱霞,陈川,郑红俊,邓文祥,刘大海,唐文蛟.生物质炭燃烧特性与动力学分析[J].燃料化学学报,2013,41(8):958-965. http://rlhxxb.sxicc.ac.cn/CN/abstract/abstract18236.shtmlXIONG Shao-wu,ZHANG Shou-yu,WU Qiao-mei,GUO Xi,DONG Ai-xia,CHEN Chuan,ZHENG Hong-jun,DENG Wen-xiang,LIU Da-hai,TANG Wen-jiao.Investigation on combustion characteristics and kinetics of bio-char[J].J Fuel Chem Technol,2013,41(8):958-965. http://rlhxxb.sxicc.ac.cn/CN/abstract/abstract18236.shtml [27] 武宏香,李海滨,赵增立.煤与生物质热重分析及动力学研究[J].燃料化学学报,2009,37(5):538-545. http://rlhxxb.sxicc.ac.cn/CN/abstract/abstract17488.shtmlWU Hong-xiang,LI Hai-bin,ZHAO Zeng-li.Thermogravimetric analysis and pyrolytic kinetic study on coal/biomass blends[J].J Fuel Chem Technol,2009,37(5):538-545. http://rlhxxb.sxicc.ac.cn/CN/abstract/abstract17488.shtml