Polychlorinated dibenzo-p-dioxins/dibenzofuran mass distribution in both start-up and normal condition in the whole municipal solid waste incinerator

被引:31
作者
Chen, Che-Kuan [1 ]
Lin, Chieh [1 ]
Lin, Yuan-Chung [2 ]
Wang, Lin-Chi [2 ]
Chang-Chien, Guo-Ping [2 ]
机构
[1] Natl Pingtung Univ Sci & Technol, Dept Environm Engn & Sci, Nei Pu 91207, Ping Tung, Taiwan
[2] Cheng Shiu Univ, Dept Chem & Mat Engn, Kaohsiung 833, Taiwan
关键词
PCDD/Fs; Incinerator; Ash; Congener profiles; Mass distribution;
D O I
10.1016/j.jhazmat.2008.02.077
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Although many researches focused on the polychlorinated dibenzo-p-dioxins/dibenzofuran (PCDD/F) emissions from stack, in the bottom ash and in the surrounding environment, researches focused on PCDD/F mass distributions in the whole incineration plant have seldom been addressed. This study determined PCDD/F emissions in the whole plant. A high-resolution gas chromatograph/high-resolution mass spectrometer was utilized for analyzing 17 PCDD/F species. Experimental results displayed that PCDD/Fs were formed during fly ash from super heater(SH), economizer(EC), semi-dryer absorber(SDA) and fabric filter (FF) was transferred to fly ash pit. Mass distribution ratios of PCDD/Fs in g I-TEQ (Toxicity Equivalency Quantity) per week from stack, SH. EC, SDA, FF, generation and bottom residue (BR) in start-up operations were 14.6%, 0.1%. 8.3%, 1.0%, 41.7%, 33.4% and 0.9%, respectively. Above results indicated that main PCDD/F source in the MSWl was from fly ash. However. the fly ash is easily controlled and PCDD/F emitted from stack flue gases will be difficult to be handled. Therefore, we should pay more attention on PCDD/F emission from flue gases especially from start-up procedure. Besides, fly ash should be controlled by sodium hypophosphite before being landfilled. MSWI did require further detoxification treatments for the solid residues and flue gases. (c) 2008 Published by Elsevier B.V.
引用
收藏
页码:37 / 44
页数:8
相关论文
共 24 条
[1]   Improvements in dioxin abatement strategies at a municipal waste management plant in Barcelona [J].
Abad, E ;
Caixach, J ;
Rivera, J .
CHEMOSPHERE, 2003, 50 (09) :1175-1182
[2]   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
[3]  
[Anonymous], 178 NATOCCMS
[4]  
[Anonymous], 2003, ORGANOHALOGEN COMP
[5]   The size distribution of polychlorinated dibenzo-p-dioxins and dibenzofurans in the bottom ash of municipal solid waste incinerators [J].
Chen, Che-Kuan ;
Lin, Chieh ;
Wang, Lin-Chi ;
Chang-Chien, Guo-Ping .
CHEMOSPHERE, 2006, 65 (03) :514-520
[6]   MECHANISM OF FORMATION OF POLYCHLORINATED DIBENZO-PARA-DIOXINS PRODUCED ON MUNICIPAL INCINERATOR FLY-ASH FROM REACTIONS OF CHLORINATED PHENOLS [J].
DICKSON, LC ;
KARASEK, FW .
JOURNAL OF CHROMATOGRAPHY, 1987, 389 (01) :127-137
[7]   PCDD/F mass balance in the flue gas cleaning units of a MSW incineration plant [J].
Giugliano, M ;
Cernuschi, S ;
Grosso, M ;
Miglio, R ;
Aloigi, E .
CHEMOSPHERE, 2002, 46 (9-10) :1321-1328
[8]  
HIS HC, 2007, CHEMOSPHERE, V67, P1394
[9]   Disposal strategies for municipal solid waste incineration residues [J].
Hjelmar, O .
JOURNAL OF HAZARDOUS MATERIALS, 1996, 47 (1-3) :345-368
[10]   RESULTS OF THE GERMAN DIOXIN MEASUREMENT PROGRAM AT MSW INCINERATORS [J].
JOHNKE, B ;
STELZNER, E .
WASTE MANAGEMENT & RESEARCH, 1992, 10 (04) :345-355