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富氮生物质原料热解过程中NOx前驱物释放特性研究

张晓鸿 詹昊 阴秀丽 吴创之

张晓鸿, 詹昊, 阴秀丽, 吴创之. 富氮生物质原料热解过程中NOx前驱物释放特性研究[J]. 燃料化学学报(中英文), 2016, 44(12): 1464-1472.
引用本文: 张晓鸿, 詹昊, 阴秀丽, 吴创之. 富氮生物质原料热解过程中NOx前驱物释放特性研究[J]. 燃料化学学报(中英文), 2016, 44(12): 1464-1472.
ZHANG Xiao-hong, ZHAN Hao, YIN Xiu-li, WU Chuang-zhi. Release characteristic of NOx precursors during the pyrolysis of nitrogen-rich biomass[J]. Journal of Fuel Chemistry and Technology, 2016, 44(12): 1464-1472.
Citation: ZHANG Xiao-hong, ZHAN Hao, YIN Xiu-li, WU Chuang-zhi. Release characteristic of NOx precursors during the pyrolysis of nitrogen-rich biomass[J]. Journal of Fuel Chemistry and Technology, 2016, 44(12): 1464-1472.

富氮生物质原料热解过程中NOx前驱物释放特性研究

基金项目: 

国家自然科学基金 51676195

详细信息
  • 中图分类号: TK6

Release characteristic of NOx precursors during the pyrolysis of nitrogen-rich biomass

More Information
  • 摘要: 利用热重分析-傅里叶红外光谱联用(TG-FTIR)和水平管式炉-X射线光电子能谱(XPS)研究了两种富氮生物质原料(大豆秸秆(SBS)和纤维板(FB))热解过程中NOx前驱物(NH3、HCN和HNCO)的释放特性,考察温度、升温速率及燃料含N物质结构对其NOx前驱物释放行为的影响。结果表明,燃料中的N来源不同(天然固有与人工添加)造成其转化差异:SBS释放的NOx前驱物主要为NH3而FB为NH3、HCN(快速)和HNCO(慢速);FB气相N主要随挥发分析出,而SBS则相反,在二次反应阶段析出;两种燃料中N的转化随温度变化,低温下富集于半焦N,600℃以上时更多向非半焦N转移,NOx前驱物以NH3为主,高温及高升温速率利于HCN生成,若以减排NOx为目的,热解温度控制在600℃为佳;两种燃料中N的结构均为胺类N(N-A),热解时部分N-A向半焦中杂环N转化,同时伴随杂环N分解;高温下吡啶N和吡咯N分解分别主要产生HCN和NH3
  • 图  1  SBS和FB结构示意图

    Figure  1  Structure diagrams of SBS and FB

    图  2  快速热解实验装置示意图

    Figure  2  Schematic diagram of the reactor for rapid pyrolysis

    图  3  SBS与FB热解失重曲线(升温速率: 40K/min)

    Figure  3  Curves of weight and its derivative during the slow pyrolysis of SBS and FB with a heating rate of 40K/min

    (a): weight change; (b): deriv.weight change

    图  4  SBS与FB慢速热解气相产物红外三维谱图 (升温速率: 40K/min)

    Figure  4  3D FT-IR spectra of gaseous products during the slow pyrolysis of SBS and FB with a heating rate of 40K/min

    图  5  SBS与FB热解气相产物的红外光谱谱图

    Figure  5  FT-IR spectra of gaseous products for the pyrolysis of SBS (a) and FB (b) at 360℃

    图  6  NH3和HNCO吸光度随热解温度的变化

    Figure  6  Absorbance profile of NH3 and HNCO during the pyrolysis

    (a): SBS-NH3; (b): FB-NH3; (c): FB-HNCO

    图  7  SBS与FB热解气相产物的红外光谱谱图

    Figure  7  FT-IR spectra of gaseous pyrolysis products for SBS at 660℃ (a) and FB at 280℃(b)

    图  8  SBS与FB快速热解NH3、 HCN产率随热解终温的变化

    Figure  8  Yields of gaseous nitrogen-containing products during the rapid pyrolysis of SBS (a) and FB (b)

    图  9  FB与SBS快速热解N产物分布随热解温度变化

    Figure  9  Nitrogen distribution in various products during the rapid pyrolysis of SBS (a) and FB (b)

    Figure 9 : NOx precurrsor; : other-N; : char-N

    图  10  原料及特征温度下半焦的N 1s谱图

    Figure  10  N 1s XPS spectra of the biomass and derived char by pyrolysis

    (a): raw-SBS; (b): SBS-char-500; (c): SBS-char-700; (d): raw-FB; (e): FB-char-500; (f): FB-char-700

    图  11  FB与SB热解过程各含N结构相对含量随温度的变化

    Figure  11  Forms of nitrogen in the raw biomass and derived char during the rapid pyrolysis of (a) SBS and (b) FB

    图  12  氨基酸热解N转化路径示意图

    Figure  12  Evolution of amino acid nitrogen duirng pyrolysis

    图  13  生物质热解半焦N转化路径示意图

    Figure  13  Evolution of Char-N during the biomass pyrolysis

    表  1  豆秸与纤维板的元素分析与工业分析

    Table  1  Ultimate and proximate analysis of soybean straw (SBS) and fiberboard (FB)

    Sample Ultimate analysis w/%(dry-ash free basis) Proximate analysis w/%(dry basis)
    C H N S O* V FC A
    SBS 46.74 6.59 1.40 0.06 45.21 77.77 16.91 5.32
    FB 44.79 6.16 7.49 0.01 41.55 83.56 16.13 0.30
    *: calculated by difference
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  • [1] BALAT M.Mechanisms of thermochemical biomass conversion processes.Part 1:Reactions of pyrolysis[J].Energy Source Part A,2008,30(7):620-635. doi: 10.1080/15567030600817258
    [2] HANSSON K M,SAMUELSSON J,TULLIN C,AMAND L E.Formation of HNCO,HCN and NH3 from the pyrolysis of bark and nitrogen-containing model compounds[J].Combust Flame,2004,137(3):265-277. doi: 10.1016/j.combustflame.2004.01.005
    [3] CAO J J,SHEN Z X,CHOW J C,WATSON J G,LEE S C,TIE X X,HO K F,WANG G H,HAN Y M.Winter and summer PM2.5 chemical compositions in fourteen Chinese cities[J].J Air Waste Manage,2012,62(10):1214-1226. doi: 10.1080/10962247.2012.701193
    [4] TIAN F J,LI B Q,CHEN Y,LI C Z.Formation of NOx precursors during the pyrolysis of coal and biomass.Part V.Pyrolysis of a sewage sludge[J].Fuel,2002,81(17):2203-2208. doi: 10.1016/S0016-2361(02)00139-4
    [5] BECIDAN M,SKREIBERG O,HUSTAD J E.NOx and N2O precursors (NH3 and HCN) in pyrolysis of biomass residues[J].Energy Fuels,2007,21(2):1173-1180. doi: 10.1021/ef060426k
    [6] YUAN S,ZHOU Z J,LI J,CHEN X L,WANG F C.HCN and NH3 released from biomass and soybean cake under rapid pyrolysis[J].Energy Fuels,2010,24:6166-6171. doi: 10.1021/ef100959g
    [7] REN Q Q.NOx and N2O precursors from co-pyrolysis of biomass and sludge[J].J Therm Anal Calorim,2013,112(2):997-1002. doi: 10.1007/s10973-012-2645-3
    [8] HANSSON K M,SAMUELSSON J,AMAND L E,TULLIN C.The temperature's influence on the selectivity between HNCO and HCN from pyrolysis of 2,5-diketopiperazine and 2-pyridone[J].Fuel,2003,82(18):2163-2172. doi: 10.1016/S0016-2361(03)00206-0
    [9] REN Q Q,ZHAO C S,CHEN X P,DUAN L B,LI Y J,MA C Y.NOx and N2O precursors (NH3 and HCN) from biomass pyrolysis:Co-pyrolysis of amino acids and cellulose,hemicellulose and lignin[J].Proc Combust Inst,2011,33:1715-1722. doi: 10.1016/j.proci.2010.06.033
    [10] REN Q Q,ZHAO C S.NOx and N2O precursors (NH3 and HCN) from biomass pyrolysis:Interaction between amino acid and mineral matter[J].Appl Energy,2013,112:170-174. doi: 10.1016/j.apenergy.2013.05.061
    [11] 谢光辉,王晓玉,韩东倩,薛帅.中国非禾谷类大田作物收获指数和秸秆系数[J].中国农业大学学报,2011,(1):9-17. http://www.cnki.com.cn/Article/CJFDTOTAL-NYDX201101003.htm

    XIE Guang-hui,WANG Xiao-yu,HAN Dong-qian,XUE Shuai.Harvest index and residue factor of non-cereal crops in China[J].J China Agric Univers,2011,(1):9-17. http://www.cnki.com.cn/Article/CJFDTOTAL-NYDX201101003.htm
    [12] 张发安,张建辉.中密度纤维板企业环保措施[J].林产工业,2012,(2):35-37+40. http://www.cnki.com.cn/Article/CJFDTOTAL-LCGY201202012.htm

    ZHANG Fa-an,ZHANG Jian-hui.Environmental protection measures to be used in MDF enterprise[J].China Forest Products Indust,2012,(2):35-37+40. http://www.cnki.com.cn/Article/CJFDTOTAL-LCGY201202012.htm
    [13] HIRATA T,KAWAMOTO S,OKURO A.Pyrolysis of melamine formaldehyde and urea formaldehyde resins[J].J Appl Polym Sci,1991,42(12):3147-3163. doi: 10.1002/app.1991.070421208
    [14] VALENTIM B,GUEDES A,BOAVIDA D.Nitrogen functionality in "oil window" rank range vitrinite rich coals and chars[J].Org Geochem,2011,42(5):502-509. doi: 10.1016/j.orggeochem.2011.03.008
    [15] WEI L H,WEN L,YANG T H,ZHANG N.Nitrogen transformation during sewage sludge pyrolysis[J].Energy Fuels,2015,29(8):5088-5094. doi: 10.1021/acs.energyfuels.5b00792
    [16] ZHOU H,JENSEN A D,GLARBORG P,KAVALIAUSKAS A.Formation and reduction of nitric oxide in fixed-bed combustion of straw[J].Fuel,2006,85(5/6):705-716.
    [17] VERMEULEN I,BLOCK C,VANDECASTEELE C.Estimation of fuel-nitrogen oxide emissions from the element composition of the solid or waste fuel[J].Fuel,2012,94(1):75-80. https://www.researchgate.net/publication/256711753_Estimation_of_fuel-nitrogen_oxide_emissions_from_the_element_composition_of_the_solid_or_waste_fuel
    [18] EIGENMANN F,MACIEJEWSKI M,BAIKER A.Quantitative calibration of spectroscopic signals in combined TG-FTIR system[J].Thermochim Acta,2006,440(1):81-92. doi: 10.1016/j.tca.2005.10.018
    [19] 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
    [20] 袁帅,李军,周志杰,王辅臣.吡啶型氮快速热解中HCN和NH3生成机理研究[J].燃料化学学报,2011,39(6):413-418. http://rlhxxb.sxicc.ac.cn/CN/abstract/abstract17751.shtml

    YUAN Shuai,LI Jun,ZHOU Zhi-jie,WANG Fu-cheng.Mechanisms of HCN and NH3 formation during rapid pyrolysis of pyridinic nitrogen containing substances[J].J Fuel Chem Technol,2011,39(6):413-418. http://rlhxxb.sxicc.ac.cn/CN/abstract/abstract17751.shtml
    [21] ZHU X D,YANG S J,WANG L,LIU Y C,QIAN F,YAO W Q,ZHANG S C,CHEN J M.Tracking the conversion of nitrogen during pyrolysis of antibiotic mycelial fermentation residues using XPS and TG-FTIR-MS technology[J].Environ Pollut,2016,211:20-27. doi: 10.1016/j.envpol.2015.12.032
    [22] HANSSON K M,AMAND L E,HABERMANN A,WINTER F.Pyrolysis of poly-L-leucine under combustion-like conditions[J].Fuel,2003,82(6):653-660. doi: 10.1016/S0016-2361(02)00357-5
    [23] LEICHTNAM J N,SCHWARTZ D,GADIOU R.J.The behaviour of fuel-nitrogen during fast pyrolysis of polyamide at high temperature[J].J Anal Appl Pyrolysis,2000,55(2):255-268. doi: 10.1016/S0165-2370(00)00075-9
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出版历程
  • 收稿日期:  2016-06-23
  • 修回日期:  2016-09-15
  • 网络出版日期:  2021-01-23
  • 刊出日期:  2016-12-10

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