State Key Laboratory of Environmental Chemistry and Ecotoxicology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences , P.O. Box 2871, Beijing 100085, China.
Environ Sci Technol. 2014 Nov 18;48(22):13165-72. doi: 10.1021/es503161v. Epub 2014 Oct 29.
Iron foundries have been identified as dioxin sources in previous field investigations. Similar formation mechanisms between dioxins and unintentional polychlorinated naphthalenes (PCNs) have led us to speculate that iron foundries are also potential PCN sources. In this study, PCNs in stack gas and fly ash samples representing atmospheric and residue emissions from 13 typical iron foundry plants were analyzed. The average emission factor of ∑(2-8)PCNs to residue was calculated to be 61 μg t(-1), with a range of 10-107 μg t(-1). The emission factors of ∑(2-8)PCNs to air in two case plants were 267 and 1472 μg t(-1). The derived emission factors might be useful for estimating annual emissions and understanding the contribution of PCNs from iron foundries. The possible formation mechanisms of PCNs, based on the PCN profiles, are discussed. Successive reductions in the abundance of homologues were observed to occur with the increase in chlorine substituted numbers. Abundances of congeners containing more β-position chlorines in the naphthalene skeleton were much higher than those of congeners containing more α-position chlorines for penta-, hexa-, and hepta- homologues, which suggests that the β-positions are favored for chlorination. Potential chlorination pathways from tetra- to octa- homologues are proposed.
在之前的实地调查中,已经确定铸造厂是二恶英的来源。二恶英和非故意多氯萘(PCN)之间类似的形成机制使我们推测铸造厂也是潜在的 PCN 来源。在这项研究中,分析了来自 13 家典型铸造厂的代表大气和残留排放的烟道气和飞灰样品中的 PCN。计算了残渣中∑(2-8)PCN 的平均排放因子为 61μg t(-1),范围为 10-107μg t(-1)。在两个案例工厂中,∑(2-8)PCN 向空气中的排放因子分别为 267 和 1472μg t(-1)。得出的排放因子可能有助于估算年排放量并了解铸造厂 PCN 的贡献。根据 PCN 分布情况,讨论了 PCN 的可能形成机制。随着氯取代数量的增加,观察到同系物的丰度连续降低。萘骨架中含有更多β位氯的同系物的丰度远高于含有更多α位氯的同系物,这表明β位更有利于氯化。提出了从四氯到八氯同系物的潜在氯化途径。