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Ultimate analysis(Dry basis)
TAR FROM BIOMASS DURING DEVOLATIZATION AND CHAR GASIFICATION PROCESS JH Moon1, BR Bang1, IH Choi2, UD Lee1* 1KITECH, South Korea, 2KAIST, South Korea The 33rd International Symposium on Combustion, Beijing, China, August 1-6, 2010. Introduction Results As main contaminants in the product gas of biomass gasification, tar should be reduced or reformed from the bio-syngas, and detailed understanding of tar generation characteristics is very important. In this research, differences of tar properties in devolatization and char gasification process are investigated. Tar - All organic contaminants with a molecular weight larger than benzene A complex mixture of condensable hydrocarbons, which includes single ring to 5-ring aromatic compounds Tar structure and its formation mechanism have not yet been well understood. Problem The large amount of tar formation during the gasification blocks the pipes and valves, and contaminates the processing equipments. -Tar has hindered the commercialization of biomass gasification. Classification of tar components Tar generation characteristics at different state (# = Undetermined class, P = Pyrolysis, 1~3 = steam to woodchip ratio, F = 1st Gasification, S = 2nd Gasification, A = All state, D = F&S) Benzene: Generation at every 1st gasification process Phenols: Generation almost all process, methylphenols generation at high temperature 3 class components: Almost all generation at 1st gasification process 4 class components: Heavier components were generated at only 900℃ Most lighter components were generated at 700℃ 5 class components: “Fluoranthene” was only generated at 900℃ 1st gasification Class Components State # Formamide (CAS)methanamide(CH3NO) 800℃:PF,1D,2F,3D Benzene(C6H6) 700·900℃:PD,1F,2F,3F 800℃:PD,1D,2F,3F 2-Furancarboxaldehyde(CAS) Furfural (C5H4O2) 700℃:2F,3F Acetic acid (C5H10O2) 700℃:AF, 800℃:PF,2F TRANS-METHOXY-6METHYLENE-3-OXABYCYCLO[3.3.0] 700℃:3F 2 Phenol Izal (C6H6O) 700℃:PF,1D,2D,3D, 800℃:AD 900℃:PD,1D,2F,3F 2-methyl-Phenol (C7H8O) 700℃:AF, 800℃:PF,2D,3F 3-Methylphenol (C7H8O) 700℃:AD, 900℃:1F 3 Methylbenzene (Toluene, C7H8) 700℃:PD,1F,2F,3F 800·900℃:AF ISOPROPYL BUTYRATE (C7H14O2) Styrene (C8H8) Benzene, 1,3-dimethyl-(CAS)m-xylene (C8H10) 700℃:AF Benzene, 1,2-dimethyl-(CAS) o-Xylene (C8H10) 800℃:2F,3F 2,3-benzofuran (C8H6O) 800℃·900℃:AF BICYCLO[2.2.1]-HEPT-5-EN-2-ALDEHYDE (C8H10O) Bicyclo[3.2.0]hept-2ene,2-methyl (C8H12) 4 1-H-indene (C9H8) 700℃:PD,1F,2D,3D 800·900℃:AD 3-Phenylpropenal (Cinnamaldehyde, C9H8O) 1,3,5-Trimethyl benzene (C9H12) 700℃:PF Methyl 5-NORBORNEN-2YL KETONE (C9H12O) TRANS-METHOXY-6METHYLENE-3-OXABYCYCLO[3.3.0] OCTAN-2-ONE(C9H12O3) Naphthalene White tar (C10H8) 700℃:PS,1D,2D,3D 1-METHYL-INDENE (C10H10) 700℃:AF, 900℃:PF,1F,2D,3D (1-methyl-2cyclopropen-1-yl)-CYCLOPROPENE (C10H10) 800℃:PF,2F,3F 1-Methylnaphthalene (C11H10) 700℃·900℃:AD 800℃:PF,1D,2D,3D Phenyl benzene (Biphenyl, C12H10) 900℃:PF,1D,2D,3D Acenaphylene (C12H10) 700℃:1D,2D,3D 800℃:PF,2D,3D Dibenzofuran (C12H8O) 900℃:AD Fluorene (C13H10) Phenanthrene (C14H10) 5 Fluoranthene(CAS)1,2-BENZACENAPTHENE (C16H10) 900℃:1F,2F,3F Light tar Heavy tar Materials and methods Materials: Korean pine woodchip (Average size: 5mm) Methods Tar was generated in an electric tube furnace and tars from devolatization and char gasification process were collected separately. Tar collector followed by European tar protocol Biomass pyrolysis and gasification principal 1st Gasification: Gas formation rate significantly increase because of devolatization. 2nd Gasification: High concentration H2 generates because of char steam gasification. Proximate analysis Ultimate analysis(Dry basis) LHV Moist. V.M. Ash F.C. C H N O S Wt% mg/kg kcal/kg 6.4 75.9 0.3 17.4 50.8 5.4 0.0 43.6 61.8 4,518 Batch type Sic electric heater GC/MS Sample amount: 20g Steam/Biomass ratio(S/B) : Pyrolysis, 1/1, 2/1, 3/1 Purging gas: N2 1L/min Temperature(℃): 700,800,900 Conclusion Various tar components were generated by changing temperature and steam to biomass ratio. Compare to 2nd gasification process, 1st gasification process produces more various kinds of tar components. The heavier components were generated at high temperature. The existence of steam affects to the tar properties but change of the steam to biomass ratio has little effect on tar properties. Reference [1] Yu-Hong Qin, Jie Feng, Wen-Ying Li: Formation of tar and its characterization during air-steam gasification of sawdust in a fluidized bed reactor. Energy, Fuel(2009) [2] J.P.A. Neeft et al.: GUIDELINE FOR SAMPLING AND ANALYSIS OF "TARS" AND PARTICLES IN BIOMASS PRODUCER GASES, ECN-RX , pp.29-40 [3] Young Kyo Choi, et al., "Kinetics of Non-Catalytic Steam Gasification of Various Coal Chars under Isothermal Condition", Hwahak Konghak, Vol.30, No. 3, June, 1992, pp [4] J.P.A. Neeft: Rationale for setup of impinger train - as used in the Technical Specification of Sampling and Analysis of Tar and Particles in the Product Gases of Biomass Gasification. SenterNovem, CEN BT/TF 143(2005) [5] J. Good et al.: Sampling and analysis of tar and particles in biomass producer gases - Technical Report, CEN BT/TF 143(2005) [6] Maniatis K: Tar Protocols. IEA Bioenergy Gasification Task. Biomass Bioenergy, vol.18, No.1,pp.1-4(2000) [7] Chunshan Li, Kenzi Suzuki: Tar property, analysis, reforming mechanism and model for biomass gasification - An overview, Renewable and Sustainable Energy Reviews. Sci., Vol.13, pp (2009)
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