Evaluation of the emission characteristics of PCDD/Fs from electric are furnaces

被引:44
作者
Chang, MB [1 ]
Huang, HC
Tsai, SS
Chi, KH
Chang-Chien, GP
机构
[1] Natl Cent Univ, Grad Inst Environm Engn, Chungli 320, Taiwan
[2] Cheng Shiu Inst Technol, Dept Chem Engn, Kaohsiung 833, Taiwan
关键词
electric arc furnace; PCDD/Fs; oxidation; reduction;
D O I
10.1016/j.chemosphere.2005.07.054
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Distribution of PCDD/F (polychlorinated dibenzo-p-dioxin and polychlorinated dibenzofuran) congeners at two electric arc furnaces (EAFs) in Taiwan is evaluated via intensive stack sampling and analysis. Two kinds of exhaust system in EAFs including stack system and shutter system are selected for measuring dioxin emissions. In addition, dioxin emissions during oxidation and reduction stages at EAF-A were characterized. Results indicate that the PCDD/F concentration of stack gas in EAF-A was 4.39 ng/N m(3) while total Toxic Equivalent Quantity (TEQ) concentration was 0.35 ng I-TEQ/N m(3). The PCDD/F concentration of stack gas in EAF-B was 2.20 ng/N m(3) and the TEQ concentration was 0.14 ng I-TEQ/N m(3). 1,2,3,4,6,7,8-HpCDF, OCDD and OCDF are the major contributors of the dioxin concentrations for two EAFs investigated and the percentage of PCDD/F in particulate phase increases as the chlorination level of the PCDD/F congener increases. The results obtained on gas/particulate partitioning of PCDD/Fs in flue gases prior to the APCD in EAFs indicate that more than 90% exists in particulate phase. In EAF-A, the PCDD/F concentration during oxidation stage is slightly higher than that measured during reduction stage, including the sampling points of CO converter outlet, prior to bag filter and stack. Majority of PCDD/Fs emitted from steel-making-processes exists in particulate-phase (about 60-70%) at both EAFs investigated. (c) 2005 Elsevier Ltd. All rights reserved.
引用
收藏
页码:1761 / 1773
页数:13
相关论文
共 21 条
[1]   Improvements to the UK PCDD/F and PCB atmospheric emission inventory following an emissions measurement programme [J].
Alcock, RE ;
Gemmill, R ;
Jones, KC .
CHEMOSPHERE, 1999, 38 (04) :759-770
[2]   Sources of dioxins in the United Kingdom: the steel industry and other sources [J].
Anderson, DR ;
Fisher, R .
CHEMOSPHERE, 2002, 46 (03) :371-381
[3]  
[Anonymous], ORGANOHALOGEN COMPD
[4]  
ARION A, 2002, ORGANOHALOGEN COMPD, V56, P127
[5]   Dioxins from thermal and metallurgical processes: recent studies for the iron and steel industry [J].
Buekens, A ;
Stieglitz, L ;
Hell, K ;
Huang, H ;
Segers, P .
CHEMOSPHERE, 2001, 42 (5-7) :729-735
[6]   PCDD/Fs emissions inventory in the Lombardy Region: results and uncertainties [J].
Caserini, S ;
Monguzzi, AM .
CHEMOSPHERE, 2002, 48 (08) :779-786
[7]   An updated inventory of potential PCDD and PCDF emission sources in the UK [J].
Eduljee, GH ;
Dyke, P .
SCIENCE OF THE TOTAL ENVIRONMENT, 1996, 177 :303-321
[8]  
*EUR UN ON LIN, 2001, EUR DIOX INV RES
[9]  
FISHER R, 2004, ORGANOHALOGEN COMPOU, V66, P1132
[10]   A WIRE RECLAMATION INCINERATOR AS A SOURCE OF ENVIRONMENTAL CONTAMINATION WITH TETRACHLORODIBENZO-P-DIOXINS AND TETRACHLORODIBENZOFURANS [J].
HRYHORCZUK, DO ;
WITHROW, WA ;
HESSE, CS ;
BEASLEY, VR .
ARCHIVES OF ENVIRONMENTAL HEALTH, 1981, 36 (05) :228-234