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热解吸氯苯污染土壤过程中多氯二苯并二恶英/呋喃的形成。

PCDD/F formation during thermal desorption of chlorobenzene contaminated soil.

机构信息

State Key Laboratory of Clean Energy Utilization, Institute for Thermal Power Engineering, Zhejiang University, Hangzhou, 310027, China.

出版信息

Environ Sci Pollut Res Int. 2017 Oct;24(29):23321-23330. doi: 10.1007/s11356-017-9963-8. Epub 2017 Aug 24.

Abstract

Unintentional formation of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/F) is observed and investigated during the thermal desorption in an airflow of a sandy soil, doped artificially with either 1,2-dichlorobenzene (1,2-DiCBz) or hexachlorobenzene (HCBz) using a lab-scale experimental set-up. At all temperatures investigated (200, 250, 300, 350 and 400 °C), this thermal treatment creates significant amounts of PCDD, PCDF and polychlorinated biphenyls (PCB), starting from 1,2-DiCBz. The highest yield of PCDD/F formed from 1,2-DiCBz occurs at 250 °C, with a total (gas + residual soil) output of 117 and 166 pg/g PCDD and PCDF, respectively. Most output reports to the gas phase and the PCDD/F signature is significantly different for residue and gas phase. Also PCB are formed, at a scale of 224 ng/g (300 °C). Compared with 1,2-DiCBz, HCBz converts into PCDD/F even more actively at 350 and 400 °C: the total PCDD/F output created attains 967 pg/g PCDD and 465 pg/g PCDF at 350 °C. As a precursor, 1,2-DiCBz favours formation of PCDF, while PCDD predominates, when the HCBz contaminated soil is treated.

摘要

在气流中对人工掺杂有 1,2-二氯苯(1,2-DiCBz)或六氯苯(HCBz)的沙土进行热解吸实验时,观察到并研究了非故意形成的多氯二苯并对二恶英和多氯二苯并呋喃(PCDD/F)。在研究的所有温度(200、250、300、350 和 400°C)下,这种热处理从 1,2-DiCBz 开始生成大量的 PCDD、PCDF 和多氯联苯(PCB)。从 1,2-DiCBz 生成的 PCDD/F 的最高产率出现在 250°C,总(气体+残留土壤)输出分别为 117 和 166 pg/g PCDD 和 PCDF。大部分产物报告为气相,残留相和气相的 PCDD/F 特征明显不同。也形成了 PCB,规模为 224ng/g(300°C)。与 1,2-DiCBz 相比,HCBz 在 350 和 400°C 时更活跃地转化为 PCDD/F:在 350°C 时,生成的总 PCDD/F 输出达到 967 pg/g PCDD 和 465 pg/g PCDF。作为前体,1,2-DiCBz 有利于 PCDF 的形成,而当处理 HCBz 污染的土壤时,PCDD 占主导地位。

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