4.7 Article

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

Journal

JOURNAL OF HAZARDOUS MATERIALS
Volume 160, Issue 1, Pages 37-44

Publisher

ELSEVIER SCIENCE BV
DOI: 10.1016/j.jhazmat.2008.02.077

Keywords

PCDD/Fs; Incinerator; Ash; Congener profiles; Mass distribution

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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.

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