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基于污泥掺烧的某生活垃圾焚烧厂烟道气、飞灰及炉渣中的二(口恶)英特征
引用本文:付建平,青宪,冯桂贤,尹文华,杨艳艳,黄锦琼,韩静磊,张素坤,谢丹平,任明忠.基于污泥掺烧的某生活垃圾焚烧厂烟道气、飞灰及炉渣中的二(口恶)英特征[J].环境科学学报,2017,37(12):4677-4684.
作者姓名:付建平  青宪  冯桂贤  尹文华  杨艳艳  黄锦琼  韩静磊  张素坤  谢丹平  任明忠
作者单位:环境保护部华南环境科学研究所, 广州 510655,环境保护部华南环境科学研究所, 广州 510655,环境保护部华南环境科学研究所, 广州 510655,环境保护部华南环境科学研究所, 广州 510655,环境保护部华南环境科学研究所, 广州 510655,环境保护部华南环境科学研究所, 广州 510655,环境保护部华南环境科学研究所, 广州 510655,环境保护部华南环境科学研究所, 广州 510655,环境保护部华南环境科学研究所, 广州 510655,环境保护部华南环境科学研究所, 广州 510655
基金项目:环保公益性行业科研专项(No.201109001);中央级公益性科研院所基本科研业务费专项(No.PM-zx703-201607-225)
摘    要:以我国南方某生活垃圾焚烧厂掺烧10%市政污泥的生活垃圾为研究对象,对前/后口废气、飞灰、炉渣及用于掺烧的污泥中17种二(口恶)英的含量进行了测定,并分析了其指纹分布特征.结合焚烧工况及处理设施,从生成机理角度探讨了二(口恶)英的排放特征、毒性当量浓度主成分特征及主要单体的排放因子线性关系.结果表明:掺烧10%的市政污泥后,废气中二(口恶)英的去除率为99.4%,低于国家排放标准;固体废物中二(口恶)英含量为飞灰 > 炉渣 > 污泥.这说明采用高温焚烧和"活性炭喷射+布袋除尘"装置不会影响掺烧10%污泥的达标排放.指纹分布特征表明,前口废气以1,2,3,4,6,7,8-HpCDF和OCDD为主,后口废气以OCDD和OCDF为主;飞灰、炉渣及污泥中的主要单体为OCDD、1,2,3,4,6,7,8-HpCDD、OCDF、1,2,3,4,6,7,8-HpCDF.主成分分析显示,前口废气和飞灰中的二(口恶)英毒性分布特征相似;炉渣和污泥的毒性分布特征相似;后口废气有自身的特征.这说明在相同工况条件下,经同一设施处理的废物中二(口恶)英排放特征相似.排放因子分析表明,2,3,4,7,8-PeCDF和1,2,3,6,7,8-HxCDF、1,2,3,6,7,8-HxCDD和1,2,3,7,8,9-HxCDD与总毒性排放因子具有较强的线性关系,且呋喃类(PCDFs)强于二(口恶)英类(PCDDs).

关 键 词:二(口恶)英  生活垃圾焚烧  主成分分析  排放因子
收稿时间:2017/5/10 0:00:00
修稿时间:2017/8/3 0:00:00

Characteristics of polychlorinated dibenzo-p-dioxins and dibenzofurans(PCDD/Fs) in flue gas, fly ash and bottom slag from a municipal solid waste incineration (MSWI) plant based on co-firing of sewage sludge
FU Jianping,QING Xian,FENG Guixian,YIN Wenhu,YANG Yanyan,HUANG Jinqiong,HAN Jinglei,ZHANG Sukun,XIE Danping and REN Mingzhong.Characteristics of polychlorinated dibenzo-p-dioxins and dibenzofurans(PCDD/Fs) in flue gas, fly ash and bottom slag from a municipal solid waste incineration (MSWI) plant based on co-firing of sewage sludge[J].Acta Scientiae Circumstantiae,2017,37(12):4677-4684.
Authors:FU Jianping  QING Xian  FENG Guixian  YIN Wenhu  YANG Yanyan  HUANG Jinqiong  HAN Jinglei  ZHANG Sukun  XIE Danping and REN Mingzhong
Institution:South China Insititute of Environmental Sciences, Ministry of Environmental Protection, Guangzhou 510655,South China Insititute of Environmental Sciences, Ministry of Environmental Protection, Guangzhou 510655,South China Insititute of Environmental Sciences, Ministry of Environmental Protection, Guangzhou 510655,South China Insititute of Environmental Sciences, Ministry of Environmental Protection, Guangzhou 510655,South China Insititute of Environmental Sciences, Ministry of Environmental Protection, Guangzhou 510655,South China Insititute of Environmental Sciences, Ministry of Environmental Protection, Guangzhou 510655,South China Insititute of Environmental Sciences, Ministry of Environmental Protection, Guangzhou 510655,South China Insititute of Environmental Sciences, Ministry of Environmental Protection, Guangzhou 510655,South China Insititute of Environmental Sciences, Ministry of Environmental Protection, Guangzhou 510655 and South China Insititute of Environmental Sciences, Ministry of Environmental Protection, Guangzhou 510655
Abstract:Determination and fingerprint analysis of PCDD/Fs of the front/back flue gas, fly ash, bottom slag and sewage sludge sampled from a MSWI plant with co-combustion of sewage sludge at 10% in Southern China were performed. Based on incineration operating conditions and treatment facilities, we explored the emission characteristics, principal component (PC) characteristics of international toxicity equivalent (I-TEQ) and linear relationship of emission factor of main congeners from a perspective of formation mechanisms of PCDD/Fs. The results revealed that the removal rate of PCDD/Fs in flue gas was 99.4%, which was lower than the national emission standard. The concentrations of PCDD/Fs in solid wastes were in the order as follows:fly ash > bottom slag > sewage sludge. These indicated that the application of high temperature combustion and activated carbon injection+bag filter had no effect on the standardized emission of co-firing sewage sludge at 10%. The fingerprint analysis showed that the main congeners in the front flue gas were 1,2,3,4,6,7,8-HpCDF, OCDD, and those in the back flue gas were OCDD and OCDF. The major congeners in fly ash, bottom slag and sludge were OCDD, 1,2,3,4,6,7,8-HpCDD, OCDF and 1,2,3,4,6,7,8-HpCDF. Results of principal component analysis (PCA) revealed that the similarity of I-TEQ distribution characteristics of PCDD/Fs in the front flue gas and fly ash; the I-TEQ distribution characteristics of PCDD/Fs in ash and sludge were also similar, whileas these were specific in the back flue gas. This indicated that the emission characteristics of PCDD/Fs were similar after treated with the same facility and the same operating condition. Analysis of emission factor showed that 2,3,4,7,8-PeCDF, 1,2,3,6,7,8-HxCDF, 1,2,3,6,7,8-HxCDD and 1,2,3,7,8,9-HxCDD significantly correlated with total toxic emission factor. And PCDFs showed more significant linear correlations with the total toxic emission factor in comparison with PCDDs.
Keywords:PCDD/Fs  MSWI  principal component analysis  emission factor
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