首页> 外文期刊>Aerosol and Air Quality Research >Emissions of Polychlorinated Dibenzo-p-dioxins and Dibenzofurans from an Electric Arc Furnace, Secondary Aluminum Smelter, Crematory and Joss Paper Incinerators
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Emissions of Polychlorinated Dibenzo-p-dioxins and Dibenzofurans from an Electric Arc Furnace, Secondary Aluminum Smelter, Crematory and Joss Paper Incinerators

机译:电弧炉,二次铝冶炼厂,火化炉和香纸焚烧炉排放的多氯二苯并对二恶英和二苯并呋喃

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Emissions of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs) from the stack flue gases, fly ashes and bottom ashes of various stationary sources were investigated. The mean total PCDD/F I-TEQ concentration of flue gas ranged from 0.00681 to 0.703 ng I-TEQ/Nm3. However, the emission factor of PCDD/F from various incinerators was 0.00827 to 3.50 μg I-TEQ/ton, whereas it was 5.36 μg I-TEQ/body for a crematory (CM). In addition, the mean total PCDD/F I-TEQ content in fly ash from an electric arc furnace (EAF) and a secondary aluminium smelter (secondary ALS) were 74.0, and 49.9 ng I-TEQ/kg, respectively, whereas they are 21.3 and 0.494 ng I-TEQ/kg for bottom ash. Meanwhile, the removal efficiency of PCDD/F by bag filters from EAF was –44.4% which is attributed to the “memory effect”. The indicatory PCDD/Fs of EAF, and secondary ALS have the same congeners (1,2,3,7,8,9-HxCDF, 2,3,7,8-TeCDF, and 1,2,3,7,8-PeCDF). In addition, CM, joss paper-A (JP-A) and joss paper-B (JP-B) incinerators have similar indicatory PCDD/F (2,3,4,6,7,8-HxCDF, OCDF, 1,2,3,4,6,7,8-HpCDD, and OCDD). The high contribution of total PCDD/F is from fly ash (61.1-95.3%) for metallurgical facilities (EAF, secondary ALS), whereas 99.9% contribution of stack flue gas is from JP-A and JP-B. In conclusion, continually monitoring various PCDD/F emission sources is necessary to understand current PCDD/F emission (flue gas, fly/bottom ash) and the related removal efficiency of existing air pollution control devices. Information about both emission factors of PCDD/Fs and indicatory PCDD/F congeners are useful for the establishment of control strategies and for use as fingerprints with regard to the dominant congeners from different emission sources.
机译:研究了各种固定来源烟囱烟气,粉煤灰和底灰的多氯二苯并对二恶英和二苯并呋喃(PCDD / Fs)排放。烟气的平均PCDD / F I-TEQ总浓度范围为0.00681至0.703 ng I-TEQ / Nm3。然而,各种焚化炉的PCDD / F排放因子为0.00827至3.50μgI-TEQ /吨,而对于火葬场(CM),则为5.36μgI-TEQ /体。此外,电弧炉(EAF)和二次铝冶炼厂(二次ALS)的粉煤灰中平均PCDD / F I-TEQ含量分别为74.0和49.9 ng I-TEQ / kg,而分别为底灰为21.3和0.494 ng I-TEQ / kg。同时,EAF袋式除尘器去除PCDD / F的效率为–44.4%,这归因于“记忆效应”。 EAF的指示性PCDD / F和次级ALS具有相同的同源物(1,2,3,7,8,9-HxCDF,2,3,7,8-TeCDF和1,2,3,7,8 -PeCDF)。此外,CM,jo纸A(JP-A)和jo纸B(JP-B)焚烧炉具有相似的指示性PCDD / F(2,3,4,6,7,8-HxCDF,OCDF,1, 2,3,4,6,7,8-HpCDD和OCDD)。冶金设施(EAF,二次ALS)的粉煤灰占PCDD / F总量的很大比例(61.1-95.3%),而JP-A和JP-B则占烟道气的99.9%。总之,有必要持续监视各种PCDD / F排放源,以了解当前的PCDD / F排放(烟气,粉煤灰/底灰)以及相关的现有空气污染控制设备的清除效率。有关PCDD / Fs和指示性PCDD / F同系物的排放因子的信息对于建立控制策略以及用作来自不同排放源的主要同系物的指纹非常有用。

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