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首页> 外文期刊>Environmental Science and Pollution Research >Distribution of PCDD/Fs in the fly ash and atmospheric air of two typical hazardous waste incinerators in eastern China
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Distribution of PCDD/Fs in the fly ash and atmospheric air of two typical hazardous waste incinerators in eastern China

机译:中国东部两个典型危险废物焚烧炉的粉煤灰和大气中PCDD / Fs的分布

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Distribution of polychlorinated dibenzo-p-dioxins and furans (PCDD/Fs) in the fly ash and atmospheric air of one medical waste incinerator (MWI) and one industrial hazardous waste incinerator (IHWI) plants were characterized. The PCDD/F concentrations of the stack gas (fly ash) produced from MWI and IHWI were 17.7 and 0.7 ng international toxic equivalent (I-TEQ)/Nm(3) (4.1 and 2.5 ng I-TEQ/g), respectively. For workplace air, the total concentrations of PCDD/Fs were 11.32 and 0.28 pg I-TEQ/Nm(3) (819.5 and 15.3 pg/Nm(3)). We assumed that the large differences of PCDD/F concentrations in workplace air were due to the differences in chlorine content of the waste, combustion conditions, and other contamination sources. With respect to the homologue profiles, the concentrations of PCDFs decreased with the increase of the substituted chlorine number for each site. Among all of the PCDD/F congeners, 2,3,4,7,8-PeCDF was the most important contributor to the I-TEQ value accounting for ca. 43 % of two sites. The gas/particle partition of PCDD/Fs in the atmosphere of the workplace in the MWI was also investigated, indicating that PCDD/Fs were more associated in the particle phase, especially for the higher chlorinated ones. Moreover, the ratio of the I-TEQ values in particle and gas phase of workplace air was 11.0. At last, the relationship between the distribution of PCDD/Fs in the workplace air and that from stack gas and fly ash was also analyzed and discussed. The high correlation coefficient might be a sign for diffuse gas emissions at transient periods of fumes escaping from the incinerator.
机译:对一台医疗废物焚化炉(MWI)和一台工业危险废物焚化炉(IHWI)的粉煤灰和大气中的多氯二苯并对二恶英和呋喃(PCDD / Fs)进行了表征。 MWI和IHWI产生的烟道气(粉煤灰)的PCDD / F浓度分别为17.7和0.7 ng国际毒性当量(I-TEQ)/ Nm(3)(4.1​​和2.5 ng I-TEQ / g)。对于工作场所空气,PCDD / Fs的总浓度为11.32和0.28 pg I-TEQ / Nm(3)(819.5和15.3 pg / Nm(3))。我们假设工作场所空气中PCDD / F浓度的较大差异是由于废物中氯含量,燃烧条件和其他污染源的差异所致。关于同系物谱,PCDFs的浓度随每个位点的取代氯数的增加而降低。在所有PCDD / F同系物中,2,3,4,7,8-PeCDF是I-TEQ值的最重要贡献者,约占两个网站的43%。还对MWI中工作场所大气中PCDD / Fs的气体/颗粒分配进行了研究,表明PCDD / Fs在颗粒相中的相关性更高,尤其是对于氯化程度更高的颗粒。此外,工作场所空气中的颗粒物和气相中的I-TEQ值之比为11.0。最后,分析和讨论了工作场所空气中PCDD / Fs的分布与烟道气和粉煤灰中PCDD / Fs的分布之间的关系。高相关系数可能是在焚化炉逸出的烟气瞬态扩散气体排放的信号。

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