Mechanism and kinetic properties of NO_3-initiated atmospheric degradation of DDT  

Mechanism and kinetic properties of NO_3-initiated atmospheric degradation of DDT

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作  者:Cai Liu Shanqing Li Rui Gao Juan Dang Wenxing Wang Qingzhu Zhang 

机构地区:[1]Environment Research Institute, Shandong University

出  处:《Journal of Environmental Sciences》2014年第3期601-607,共7页环境科学学报(英文版)

基  金:supported by the National Natural Science Foundation of China(No.21337001,21377073);the Independent Innovation Foundation of Shandong University(IIFSDU)(No.2012JC030)

摘  要:In this article, the NO3 radical-initiated atmospheric oxidation degradation of DDT was theoretically investigated using molecular orbital theory calculations. All the calculations of intermediates, transition states and products were performed at the MPWB1K/6-311+G(3df,2p)//MPWB1K/6- 31+G(d,p) level of theory. Several energetically favorable reaction pathways were revealed. The formation mechanisms of secondary pollutants were presented and discussed. The rate constants were deduced over the temperature range of 273-333 K using canonical variational transition-state (CVT) theory with the small curvature tunneling (SCT) method. Our study shows that H abstraction from the alkyl group and NO3 addition to the Ca atom of the benzene ring are the dominant reaction pathways. The rate-temperature formula of the overall rate constants is k(T)(DDT+NO3) = (7.21 ~ 10-15)exp(-153.81/T) cm3/(mol.sec) over the possible atmospheric temperature range of 273-333 K. The atmospheric lifetime of DDT determined by NO3 radical is about 52.5 days, which indicates that it can be degraded in the gas phase within several months.In this article, the NO3 radical-initiated atmospheric oxidation degradation of DDT was theoretically investigated using molecular orbital theory calculations. All the calculations of intermediates, transition states and products were performed at the MPWB1K/6-311+G(3df,2p)//MPWB1K/6- 31+G(d,p) level of theory. Several energetically favorable reaction pathways were revealed. The formation mechanisms of secondary pollutants were presented and discussed. The rate constants were deduced over the temperature range of 273-333 K using canonical variational transition-state (CVT) theory with the small curvature tunneling (SCT) method. Our study shows that H abstraction from the alkyl group and NO3 addition to the Ca atom of the benzene ring are the dominant reaction pathways. The rate-temperature formula of the overall rate constants is k(T)(DDT+NO3) = (7.21 ~ 10-15)exp(-153.81/T) cm3/(mol.sec) over the possible atmospheric temperature range of 273-333 K. The atmospheric lifetime of DDT determined by NO3 radical is about 52.5 days, which indicates that it can be degraded in the gas phase within several months.

关 键 词:DDT NO3 radicals atmospheric oxidation reaction mechanism rate constants 

分 类 号:X592[环境科学与工程—环境工程] TQ324.9[化学工程—合成树脂塑料工业]

 

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