研究报告

  • 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

  • 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
  • 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
  • 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)
  • 作者
  • 单位
  • 付建平
  • 环境保护部华南环境科学研究所, 广州 510655
  • 青宪
  • 环境保护部华南环境科学研究所, 广州 510655
  • 冯桂贤
  • 环境保护部华南环境科学研究所, 广州 510655
  • 尹文华
  • 环境保护部华南环境科学研究所, 广州 510655
  • 杨艳艳
  • 环境保护部华南环境科学研究所, 广州 510655
  • 黄锦琼
  • 环境保护部华南环境科学研究所, 广州 510655
  • 韩静磊
  • 环境保护部华南环境科学研究所, 广州 510655
  • 张素坤
  • 环境保护部华南环境科学研究所, 广州 510655
  • 谢丹平
  • 环境保护部华南环境科学研究所, 广州 510655
  • 任明忠
  • 环境保护部华南环境科学研究所, 广州 510655
  • 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).
  • 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.

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