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首页> 外文期刊>Chemosphere >Emissions of 2,3,7,8-substituted and non-2,3,7,8-substituted polychlorinated dibenzo-p-dioxins and dibenzofurans from secondary aluminum smelters
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Emissions of 2,3,7,8-substituted and non-2,3,7,8-substituted polychlorinated dibenzo-p-dioxins and dibenzofurans from secondary aluminum smelters

机译:二级铝冶炼厂排放2,3,7,8-取代的和非2,3,7,8-取代的多氯二苯并对二恶英和二苯并呋喃

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The secondary aluminum smelting industry is an important source of polychlorinated dibenzo-p-dioxin and dibenzofurans (PCDD/Fs). However, the formations and emissions of non-2,3,7,8-PCDD/Fs have rarely been studied. Non-2,3,7,8-PCDD/Fs may also be metabolically toxic to mammalians. In this study, four typical secondary aluminum smelters were selected as demonstration smelters and the composition of the raw material they used was adjusted to investigate the influence on PCDD/F emissions and profiles. In addition to 17 congeners of 2,3,7,8-PCDD/Fs, 64 congeners of non-2,3,7,8-PCDD/Fs were firstly reported. Strong, positive correlations were found between non-2,3,7,8-PCDD/Fs and 2,3,7,8-PCDD/Fs. The concentrations of 2,3,7,8-PCDD/Fs in stack gas and fly ash samples were 120.7-870.4 pg/Nm(3) and 13.40 -292.9 ng/g, respectively. Those of non-2,3,7,8-PCDD/Fs in the stack gas and fly ash samples were 84.03 -1183.7 pg/Nm(3) and 7.20-344.7 ng/g, respectively. The raw material composition was a key factor affecting PCDD/F emissions and profiles. An analysis of Gibbs free energies (Delta G(f)) showed that non-2,3,7,8-PCDD/Fs could be transformed into 2,3,7,8-PCDD/Fs, which would increase the PCDD/F environmental risks. The emission inventories of 2,3,7,8-PCDD/Fs, non-2,3,7,8-PCDD/Fs, and International Toxic Equivalents from Chinese secondary aluminum smelters in 2013 were 8247 g, 7253 g, and 608.6 g, respectively. The results of this study could contribute to potential risk evaluations and effective reduction of non-2,3,7,8-PCDD/Fs. (C) 2018 Elsevier Ltd. All rights reserved.
机译:铝的二次冶炼工业是多氯二苯并-对-二恶英和二苯并呋喃(PCDD / Fs)的重要来源。然而,很少研究非2,3,7,8-PCDD / Fs的形成和排放。非2,3,7,8-PCDD / Fs也可能对哺乳动物具有代谢毒性。在这项研究中,选择了四个典型的二级铝冶炼厂作为示范冶炼厂,并调整了所用原料的成分,以研究其对PCDD / F排放和剖面的影响。除了2,3,7,8-PCDD / Fs的17个同源物外,首次报道了非2,3,7,8-PCDD / Fs的64个同源物。非2,3,7,8-PCDD / Fs与2,3,7,8-PCDD / Fs之间存在强正相关。烟气和粉煤灰样品中2,3,7,8-PCDD / Fs的浓度分别为120.7-870.4 pg / Nm(3)和13.40 -292.9 ng / g。烟气和粉煤灰样品中非2,3,7,8-PCDD / Fs的分别为84.03 -1183.7 pg / Nm(3)和7.20-344.7 ng / g。原料成分是影响PCDD / F排放量和分布的关键因素。对吉布斯自由能(Delta G(f))的分析表明,非2,3,7,8-PCDD / Fs可以转化为2,3,7,8-PCDD / Fs,这会增加PCDD / F环境风险。 2013年中国二级铝冶炼厂的2,3,7,8-PCDD / Fs,非2,3,7,8-PCDD / Fs和国际有毒当量的排放清单分别为8247 g,7253 g和608.6 g,分别。这项研究的结果可能有助于潜在的风险评估和有效减少非2,3,7,8-PCDD / Fs。 (C)2018 Elsevier Ltd.保留所有权利。

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