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吸附剂修饰铁基氧载体的氧化动力学研究

王金星 赵海波

王金星, 赵海波. 吸附剂修饰铁基氧载体的氧化动力学研究[J]. 燃料化学学报(中英文), 2016, 44(12): 1457-1463.
引用本文: 王金星, 赵海波. 吸附剂修饰铁基氧载体的氧化动力学研究[J]. 燃料化学学报(中英文), 2016, 44(12): 1457-1463.
WANG Jin-xing, ZHAO Hai-bo. Oxidation kinetics of adsorbent-decorated Fe-based oxygen carrier for chemical-looping combustion[J]. Journal of Fuel Chemistry and Technology, 2016, 44(12): 1457-1463.
Citation: WANG Jin-xing, ZHAO Hai-bo. Oxidation kinetics of adsorbent-decorated Fe-based oxygen carrier for chemical-looping combustion[J]. Journal of Fuel Chemistry and Technology, 2016, 44(12): 1457-1463.

吸附剂修饰铁基氧载体的氧化动力学研究

基金项目: 

国家自然科学基金 51522603,51561125001

详细信息
  • 中图分类号: TQ534

Oxidation kinetics of adsorbent-decorated Fe-based oxygen carrier for chemical-looping combustion

More Information
  • 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。
  • 图  1  化学链燃烧原理示意图

    Figure  1  Schematic representation of the CLC concept

    图  2  TGA实验系统示意图

    Figure  2  Schematic of TGA experiments

    图  3  900℃下Fe2O3/Al2O3为氧载体时 TG 随时间的变化

    Figure  3  TG as a function of time for reduction (a) and oxidation (b) of raw OC at 900℃

    图  4  空气条件下不同氧载体颗粒的转化特性

    Figure  4  Conversion characteristics obtained from oxidation of different OC particles in air atmosphere

    图  5  八种反应机理模型拟合900℃下原FeO/Al2O3颗粒在空气气氛下的氧化过程

    Figure  5  Integral form expressions of eight reaction mechanisms for raw FeO/Al2O3 reacting with air at 900℃

    图  6  四种氧载体被空气氧化过程中lnk与1000/T的线性拟合

    Figure  6  Plots of lnk vs 1000/T for the oxidation of four OCs with air

    图  7  900℃下四种氧载体的实验线

    Figure  7  Experimental values of four OC s oxidation at 900℃ vs the calculated model

    (a): raw FeO/Al2O3; (b): K2O decorated FeO/Al2O3; (c): Na2O decorated FeO/Al2O3; (d): CaO decorated FeO/Al2O3 : computed result; : experimental result

    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
    下载: 导出CSV

    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
    下载: 导出CSV

    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
    900y=-0.04508+0.01769x0.99487
    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
    900y=-0.05703+0.01592x0.99403
    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
    900y=-0.04827+0.01588x0.99723
    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
    900y=-0.04435+0.0144x0.99499
    925 y=-0.05129+0.01509x 0.99489
    下载: 导出CSV

    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
    下载: 导出CSV
  • [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.shtml

    XIONG 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.shtml

    WU 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
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出版历程
  • 收稿日期:  2016-07-04
  • 修回日期:  2016-09-23
  • 网络出版日期:  2021-01-23
  • 刊出日期:  2016-12-10

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