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城市固体废弃物焚烧炉在启动和正常运行条件下多氯代二苯并对二噁英/多氯代二苯并呋喃的质量分布情况。

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

作者信息

Chen Che-Kuan, Lin Chieh, Lin Yuan-Chung, Wang Lin-Chi, Chang-Chien Guo-Ping

机构信息

Department of Environmental Engineering and Science, National Pingtung University of Science and Technology, Ping Tung, Taiwan.

出版信息

J Hazard Mater. 2008 Dec 15;160(1):37-44. doi: 10.1016/j.jhazmat.2008.02.077. Epub 2008 Feb 29.

DOI:10.1016/j.jhazmat.2008.02.077
PMID:18440134
Abstract

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 MSWI 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.

摘要

尽管许多研究聚焦于焚烧炉烟囱、底灰及周边环境中多氯二苯并对二噁英/二苯并呋喃(PCDD/F)的排放,但针对整个焚烧厂内PCDD/F质量分布的研究却鲜有涉及。本研究测定了整个工厂内PCDD/F的排放情况。采用高分辨率气相色谱仪/高分辨率质谱仪分析17种PCDD/F物质。实验结果表明,过热器(SH)、省煤器(EC)、半干式吸收器(SDA)和布袋除尘器(FF)中的飞灰转移至飞灰坑的过程中会形成PCDD/F。在启动运行时,烟囱、SH、EC、SDA、FF、发电设备及底渣(BR)每周每克毒性当量(TEQ)中PCDD/F的质量分布比例分别为14.6%、0.1%、8.3%、1.0%、41.7%、33.4%和0.9%。上述结果表明,城市生活垃圾焚烧(MSWI)中PCDD/F的主要来源是飞灰。然而,飞灰易于控制,而烟囱排放的烟气中的PCDD/F则难以处理。因此,我们应更加关注烟气尤其是启动过程中的PCDD/F排放。此外,飞灰在填埋前应用次磷酸钠进行处理。MSWI确实需要对固体残渣和烟气进行进一步的解毒处理。

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