Mathematical modelling of slow pyrolysis of segregated solid wastes in a packed-bed pyrolyser

被引:70
作者
Yang, Yao Bin [1 ]
Phan, Anh N. [1 ]
Ryu, Changkook [1 ]
Sharifi, Vida [1 ]
Swithenbank, Jim [1 ]
机构
[1] Univ Sheffield, Dept Chem & Proc Engn, SUWIC, Sheffield S1 3JD, S Yorkshire, England
基金
英国工程与自然科学研究理事会;
关键词
segregated wastes; slow pyrolysis; mathematical modelling; FLASH PYROLYSIS; BIOMASS; FUEL; INCINERATION; COMBUSTION; COAL; MOISTURE;
D O I
10.1016/j.fuel.2006.07.012
中图分类号
TE [石油、天然气工业]; TK [能源与动力工程];
学科分类号
0807 ; 0820 ;
摘要
Waste segregation is being explored as one of the potential effective ways for waste management, where wastes are separated for either recycling or energy recovery. In this paper, three segregated wastes, contaminated waste wood, cardboard and waste textile are pyrolysed in a slow-heating packed-bed reactor for the purpose of solid, liquid and gas recovery. The effect of final temperature was investigated and product yields and compositions were measured. Mathematical modelling was employed to simulate the heat, mass transfer and kinetic processes inside the reactor. Both a parallel reaction model and a function group model were used to predict the product yields as well as their compositions. Char yield of 21-34%, tar 34-46% and gas 23-43% were obtained. It is found that packed-bed pyrolysis produces 30-100% more char compared to standard TGA tests and the local heating rate across the packed-bed reactor differs remarkably from the programmed wall-heating rate and varies greatly in both time and space. Mathematical modelling suggests that wood has higher tar cracking ability than cardboard and textile wastes during pyrolysis, and the effects of mineral contents in the fuel need to be explored. CO2, CO, tar and water are the main released species during the major stage of the pyrolysis processes which occurs between 250 and 450 degrees C, whereas noticeable quantity of hydrogen and light hydrocarbons is observed only at higher temperature levels and at the final stage. (c) 2006 Elsevier Ltd. All rights reserved.
引用
收藏
页码:169 / 180
页数:12
相关论文
共 39 条
[1]  
[Anonymous], ACS DIV FUEL CHEM PR
[2]  
BRIDGEWATER AV, 2002, FAST PYROLYSIS BIOMA, V2
[3]   An overview of fast pyrolysis of biomass [J].
Bridgwater, AV ;
Meier, D ;
Radlein, D .
ORGANIC GEOCHEMISTRY, 1999, 30 (12) :1479-1493
[4]   MODELING AND EXPERIMENTAL-VERIFICATION OF PHYSICAL AND CHEMICAL PROCESSES DURING PYROLYSIS OF A LARGE BIOMASS PARTICLE [J].
CHAN, WCR ;
KELBON, M ;
KRIEGER, BB .
FUEL, 1985, 64 (11) :1505-1513
[5]   Biomass pyrolysis/gasification for product gas production: the overall investigation of parametric effects [J].
Chen, G ;
Andries, J ;
Luo, Z ;
Spliethoff, H .
ENERGY CONVERSION AND MANAGEMENT, 2003, 44 (11) :1875-1884
[6]   Pyrolysis of Miscanthus Giganteus and wood pellets:: TG-FTIR analysis and reaction kinetics [J].
de Jong, W ;
Pirone, A ;
Wójtowicz, MA .
FUEL, 2003, 82 (09) :1139-1147
[7]   Modeling intra- and extra-particle processes of wood fast pyrolysis [J].
Di Blasi, C .
AICHE JOURNAL, 2002, 48 (10) :2386-2397
[8]   Heat, momentum and mass transport through a shrinking biomass particle exposed to thermal radiation [J].
DiBlasi, C .
CHEMICAL ENGINEERING SCIENCE, 1996, 51 (07) :1121-1132
[9]  
Domburg G., 1974, P 4 ICTA BUD, V2, P211
[10]   KINETICS OF THE PYROLYSIS OF ALMOND SHELLS AND ALMOND SHELLS IMPREGNATED WITH COCL2 IN A FLUIDIZED-BED REACTOR AND IN A PYROPROBE 100 [J].
FONT, R ;
MARCILLA, A ;
VERDU, E ;
DEVESA, J .
INDUSTRIAL & ENGINEERING CHEMISTRY RESEARCH, 1990, 29 (09) :1846-1855