Mechanism and kinetic properties for the OH-initiated atmospheric oxidation degradation of 9,10-Dichlorophenanthrene

被引:24
|
作者
Dang, Juan [1 ]
Shi, Xiangli [1 ]
Zhang, Qingzhu [1 ]
Hu, Jingtian [1 ]
Wang, Wenxing [1 ]
机构
[1] Shandong Univ, Environm Res Inst, Jinan 250100, Peoples R China
基金
中国国家自然科学基金;
关键词
9,10-Dichlorophenanthrene; OH radicals; Oxidation mechanism; Degradation products; Rate constants; POLYCYCLIC AROMATIC-HYDROCARBONS; URBAN AIR; GAS-PHASE; PARENT COMPOUNDS; TIDAL FLATS; WATER; NAPHTHALENE; PHOTOOXIDATION; ANTHRACENE; RADICALS;
D O I
10.1016/j.scitotenv.2014.10.081
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Chlorinated polycyclic aromatic hydrocarbons (CIPAHs) have become a serious environmental concern due to their widespread occurrence and dioxin-like toxicities. In this work, the mechanism of the OH-initiated atmospheric oxidation degradation of 9,10-dichlorophenanthrene (9,10-Cl(2)Phe) was investigated by using high-accuracy quantum chemistry calculations. The rate constants of the crucial elementary reactions were determined by the Rice-Ramsperger-Kassel-Marcus (RRKM) theory. The theoretical results were compared with the available experimental data. The main oxidation products are a group of ring-retaining and ring-opening compounds including chlorophenanthrols, 9,10-dichlorophenanthrene-3,4-dione, dialdehydes, chlorophenanthrenequinones, nitro-9,10-Cl(2)Phe and epoxides et al. The overall rate constant of the OH addition reaction is 2.35 x 10(-12) cm(3) molecule(-1) s(-1) at 298 K and 1 atm. The atmospheric lifetime of 9,10-Cl(2)Phe determined by OH radicals is about 5.05 days. This study provides a comprehensive investigation of the OH-initiated oxidation degradation of 9,10-Cl(2)Phe and should contribute to clarifying its atmospheric fate. (C) 2014 Elsevier B.V. All rights reserved.
引用
收藏
页码:787 / 794
页数:8
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