首页> 外文期刊>Environmental Science and Pollution Research >Emission and distribution of PCDD/Fs, chlorobenzenes, chlorophenols, and PAHs from stack gas of a fluidized bed and a stoker waste incinerator in China
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Emission and distribution of PCDD/Fs, chlorobenzenes, chlorophenols, and PAHs from stack gas of a fluidized bed and a stoker waste incinerator in China

机译:PCDD / FS,氯苯,氯酚的排放和分布,来自流化床的堆气和中国的堆气垃圾焚烧炉

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The concentrations, homologue, and congener profiles, as well as the gas/particle distribution of polychlorinated dibenzo-p-dioxins and furans (PCDD/Fs), chlorobenzenes (CBzs), chlorophenols (CPhs), and polyaromatic hydrocarbons (PAHs) from stack gas of two different municipal solid waste incinerators in China, were characterized. The incinerators were a stoker furnace incinerator equipped with the advanced air pollution control device (APCD) and a common circulating fluidized bed (CFB) furnace. The concentration of PCDD/Fs in the stack gas of the stoker incinerator ranged 0.011-0.109 ng international toxic equivalent factor (ITEQ)/Nm(3) and was below the current limit for PCDD/F emissions from the municipal solid waste incinerators (MSWIs) in China (0.1 ng I-TEQ/Nm(3)) in most of the cases. Moreover, the concentration of PCDD/Fs in the stack gas of the stoker incinerator was significantly lower than that of the CFB incinerator (0.734 to 24.6 ng I-TEQ/Nm(3)). In both incinerators, the majority of the total PCDD/F emissions (above 90%) ended up in the gas phase. 2,3,4,7,8-PeCDF, which occupied 24.3-43.6 and 32.5-75.6% of I-TEQ contribution in MSWIs A and B, respectively, was the most abundant congener. However, different types of incinerators and APCDs induced different congener and homologue distributions. The total concentration of CBzs from the stoker incinerator (0.05-3.2 similar to g/Nm(3)) was also much lower than that formed from the CFB incinerator (10.9-75.2 similar to g/Nm(3)). The phase distribution of CBzs followed the same pattern as with the PCDD/Fs. Moreover, the emission level of CBz was 100-1000 times higher than that of the PCDD/Fs, which determines the applicability of CBzs as indicators of PCDD/F emissions. High correlations between the emission concentrations of PCDD/Fs, TeCBz, and PCBz in specific ranges were revealed. Furthermore, high concentrations of CPhs (0.6-141.0 similar to g/Nm(3)) and PAHs (148.6-4986.5 similar to g/Nm(3)) were detected in the stack gases of MSWI B. In some cases, the concentrations were as high as the concentrations in the fumes exiting the boiler of one foreign stoker without flue gas purification indicating the abundance of CPh and PAH emissions in the stack gas of waste incinerators.
机译:的浓度,同系物,和同类型材,以及从栈多氯二苯并 - 对 - 二恶英和呋喃(PCDD / FS),氯苯(CBzs),氯酚(CPHS),和聚芳烃(PAHs的)的气体/颗粒分布在中国两个不同的城市固体废物焚烧炉气进行了表征。所述焚化炉配备了先进的空气污染控制装置(APCD)和公共循环流化床(CFB)炉加料机炉焚烧炉。 PCDD的浓度/ Fs的给煤机焚化炉的烟道气中介于0.011-0.109纳克国际毒性当量因子(联茂)/牛顿米(3)并且是低于电流限制用于从城市固体废物焚烧炉PCDD / F排放(MSWIs )在中国(0.1纳克I-TEQ / Nm的(3))在大多数情况下。此外,PCDD / F与司炉焚化炉的烟道气中的浓度显著低于所述CFB焚化炉(0.734至24.6纳克I-TEQ / Nm的(3))。在这两种焚化炉,大部分总PCDD的/ F排放(90%以上)在气相中结束了。 2,3,4,7,8-PeCDF,占24.3-43.6以及在MSWIs A和B I-TEQ贡献32.5-75.6%,分别是最丰富的同源。然而,不同类型的焚烧炉和APCDs的不同引起的同类和同系物分布。 CBzs从炉排焚烧炉的总浓度(类似于克0.05-3.2 /牛顿米(3))也要比从CFB焚化炉形成降低(10.9-75.2类似于克/米(3))。 CBzs的相位分布遵循相同的图案与PCDD / Fs的。此外,CBz基的排放水平高于所述PCDD / Fs的,它决定CBzs的适用性PCDD / F排放指标的高100-1000倍。 PCDD / Fs的,TeCBz,和PCBZ的在特定范围内的排放浓度之间的相关性高,揭示。此外,高浓度的CPHS(0.6-141.0类似于克/ Nm的(3))和多环芳烃(148.6-4986.5类似于克/ Nm的(3))在垃圾焚烧B的烟道气在一些情况下,该浓度检测竟达在离开一个外国司炉的锅炉无烟气净化指示器CPh和PAH的排放废物焚烧炉的烟道气中的丰度的烟气浓度。

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