Pyrolysis of permethrin and formation of precursors of polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/F) under non-oxidative conditions

被引:31
作者
Altarawneh, Mohammednoor [1 ]
Carrizo, Daniel [1 ]
Ziolkowski, Artur [1 ]
Kennedy, Eric M. [1 ]
Dlugogorski, Bogdan Z. [1 ]
Mackie, John C. [1 ,2 ]
机构
[1] Univ Newcastle, Proc Safety & Environm Protect Res Grp, Sch Engn, Callaghan, NSW 2308, Australia
[2] Univ Sydney, Sch Chem, Sydney, NSW 2006, Australia
基金
澳大利亚研究理事会;
关键词
Impregnated wood; Treated wood; Wood preservatives; Pyrethroids; LOSP; TREATED WOOD; AB-INITIO; DECOMPOSITION; COMBUSTION; CONVERSION; FIRES;
D O I
10.1016/j.chemosphere.2008.12.033
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
This article reports the computational and experimental results of the thermal decomposition of permethrin, a potential source of dibenzo-p-dioxins (PCDD) and polychlorinated dibenzofurans (PCDF). We have performed a quantum chemical analysis by applying density functional theory to obtain the decomposition pathways of permethrin and the formation mechanism of dibenzofuran. We have conducted the pyrolysis experiments in a tubular reactor and identified the pyrolysis products to demonstrate the agreement between the experimental measurements and quantum chemical calculations. The initiation of the decomposition of permethrin involves principally the aromatisation of permethrin into 3-phenoxyphenylacetic acid, 2-methylphenyl ester U) and concomitant loss of 2HCl. This rearrangement is followed by the rupture of the O-CH2 linkage in J, with a rate constant derived from the quantum chemical results of 1 x 10(15) exp(-68 kcal/mol/RT) s(-1) for temperatures between 700 and 1300 K. This is confirmed by finding that the rate constant for unimolecular rearrangement of permethrin into J is 1.2 x 10(12) exp(-53 kcal/mol/RT s(-1) over the same range of temperatures and exceeds the direct fission rate constant at all temperatures up to 850 +/- 120 degrees C as well as by the experimental detection of J prior to the detection of the initial products incorporating diphenyl ether, 1-methyl-3-phenoxybenzene, 3-phenoxybenzaldehyde and 1-chloromethyl-3-phenoxybenzene. As the temperature increases, we observe a rise in secondary products formed directly or indirectly (via phenol/phenoxy) including aromatics (naphthalene), biphenyls (biphenyl, 4-methyl-1,1'-biphenyl) and dibenzofuran (DF). In particular, we discover by means of quantum chemistry a direct route from 2-phenoxyphenoxy to naphthalene. We detect no polychlorinated dibenzo-p-dioxins and dibenzofurans. Unlike the case of oxidative pyrolysis (Tame, N.W., Dlugogorski, B.Z., Kennedy, E.M., 2007b. Formation of dioxins in fires of arsenic-free treated wood: Role of organic preservatives. Environ. Sci. Technol. 41,6425-6432] where significant yields of both PCDD and PCDF were obtained, under non-oxidative conditions the thermal decomposition of permethrin does not form appreciable amounts of PCDD or PCDF and the presence of oxygen (and/or a sizable radical pool) appears necessary for the formation of dibenzo-p-dioxin itself or PCDD/F from phenol/phenoxy. (C) 2008 Elsevier Ltd. All rights reserved.
引用
收藏
页码:1435 / 1443
页数:9
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