Solid-gaseous phase transformation of elemental contaminants during the gasification of biomass

被引:40
作者
Jiang, Ying [1 ]
Ameh, Abiba [1 ]
Lei, Mei [2 ]
Duan, Lunbo [3 ]
Longhurst, Philip [1 ]
机构
[1] Cranfield Univ, Sch Energy Environm & Agrifood, Ctr Bioenergy & Resource Management, Cranfield MK43 0AL, Beds, England
[2] Chinese Acad Sci, Inst Geog Sci & Nat Resources Res, Ctr Environm Remediat, Beijing 100101, Peoples R China
[3] Southeast Univ, Sch Energy & Environm, Key Lab Energy Thermal Convers & Control, Minist Educ, Nanjing 210096, Jiangsu, Peoples R China
基金
英国工程与自然科学研究理事会;
关键词
Land contamination; Heavy metal; Biomass waste; Gasification; MTDATA; HEAVY-METALS; COAL; PHYTOEXTRACTION; PHYTOREMEDIATION; COMBUSTION; EMISSIONS; BIOENERGY; PRESSURE; BEHAVIOR; FATE;
D O I
10.1016/j.scitotenv.2015.11.017
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Disposal of plant biomass removed from heavy metal contaminated land via gasification achieves significant volume reduction and can recover energy. However, these biomass often contain high concentrations of heavy metals leading to hot-corrosion of gasification facilities and toxic gaseous emissions. Therefore, it is of significant interest to gain a further understanding of the solid-gas phase transition of metal(loid)s during gasification. Detailed elemental analyses (C, H, O, N and key metal/metalloid elements) were performed on five plant species collected from a contaminated site. Using multi-phase equilibria modelling software (MTDATA), the analytical data allows modelling of the solid/gas transformation of metal(loid)s during gasification. Thermodynamic modelling based on chemical equilibrium calculations was carried out in this study to pi-edict the fate of metal(loid) elements during typical gasification conditions and to show how these are influenced by metal(loid) composition in the biomass and operational conditions. As, Cd, Zn and Pb tend to transform to their gaseous forms at relatively low temperatures (<1000 degrees C). Ni, Cu, Mn and Co converts to gaseous forms within he typical gasification temperature range of 1000-1200 degrees C. Whereas Cr, Al, Fe and Mg remain in solid phase at higher temperatures (>1200 degrees C). Simulation of pressurised gasification conditions shows that higher pressures increase the temperature ay which solid-to-gaseous phase transformations takes place. (C) 2015 The Authors. Published by Elsevier B.V.
引用
收藏
页码:724 / 730
页数:7
相关论文
共 34 条
[1]   Can we use biomass produced from phytoremediation? [J].
Abhilash, P. C. ;
Yunus, Mohammad .
BIOMASS & BIOENERGY, 2011, 35 (03) :1371-1372
[2]  
[Anonymous], 2014, 2014 KEY WORLD EN ST
[3]   The global potential of bioenergy on abandoned agriculture lands [J].
Campbell, J. Elliott ;
Lobell, David B. ;
Genova, Robert C. ;
Field, Christopher B. .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2008, 42 (15) :5791-5794
[4]   Minor and trace element emissions from post-combustion CO2 capture from coal: Experimental and equilibrium calculations [J].
Cotton, A. ;
Patchigolla, K. ;
Oakey, J. E. .
FUEL, 2014, 117 :391-407
[5]  
Defra, 2014, SP1011 DEFR
[6]   Estimation of calorific values of fuels from lignocellulosics [J].
Demirbas, A ;
Gullu, D ;
Caglar, A ;
Akdeniz, F .
ENERGY SOURCES, 1997, 19 (08) :765-770
[7]   Combustion characteristics of different biomass fuels [J].
Demirbas, A .
PROGRESS IN ENERGY AND COMBUSTION SCIENCE, 2004, 30 (02) :219-230
[8]   A review of the primary measures for tar elimination in biomass gasification processes [J].
Devi, L ;
Ptasinski, KJ ;
Janssen, FJJG .
BIOMASS & BIOENERGY, 2003, 24 (02) :125-140
[9]   Spanish biofuels heating value estimation. Part II: Proximate analysis data [J].
Garcia, Roberto ;
Pizarro, Consuelo ;
Lavin, Antonio G. ;
Bueno, Julio L. .
FUEL, 2014, 117 :1139-1147
[10]   Integrating phytoremediation with biomass valorisation and critical element recovery: A UK contaminated land perspective [J].
Jiang, Ying ;
Lei, Mei ;
Duan, Lunbo ;
Longhurst, Philip .
BIOMASS & BIOENERGY, 2015, 83 :328-339