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Frontiers of Environmental Science & Engineering

ISSN 2095-2201

ISSN 2095-221X(Online)

CN 10-1013/X

Postal Subscription Code 80-973

2018 Impact Factor: 3.883

Front. Environ. Sci. Eng.    2015, Vol. 9 Issue (4) : 583-590    https://doi.org/10.1007/s11783-014-0691-8
RESEARCH ARTICLE
Kinetics and mechanisms of reactions for hydrated electron with chlorinated benzenes in aqueous solution
Haixia YUAN1,2,Huxiang PAN2,Jin SHI1,Hongjing LI1,*(),Wenbo DONG1,*()
1. Shanghai Key Laboratory of Atmospheric Particle Pollution and Prevention, Department of Environmental Science & Engineering, Fudan University, Shanghai 200433, China
2. Institutes of Naval Medicine, Shanghai 200433, China
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Abstract

The reactions between chlorinated benzenes (CBzs) and hydrated electron (eaq-) were investigated by the electron beam (EB) and laser flash photolysis (LFP) experiments. Under the EB irradiation, the effects of irradiation dose, initial concentration and the number of Cl atoms on the removal efficiencies were further examined. At 10 kGy, the removal efficiencies of mono-CB, 1,3-diCB, 1,2-diCB and 1,4-diCB were 41.2%, 87.2%, 84.0%, and 84.1%, respectively. While irradiation dose was 50 kGy, the removal efficiencies increased to 47.4%, 95.8%, 95.0%, and 95.2%, respectively. Irradiation of CBzs solutions has shown that the higher the initial concentration, the lower the percentage of CBzs removal. In addition to this, the dechlorination efficiencies of 1,2-dichlorobenzene (1,2-diCB), 1,3-dichlorobenzene (1,3-diCB) and 1,4-dichlorobenzene (1,4-diCB) were much higher than that of chlorobenzene (mono-CB). The kinetics of the reactions was achieved with nanosecond LFP. The rate constants of second-order reaction between eaq- with mono-CB, 1,2-diCB, 1,3-diCB and 1,4-diCB were (5.3±0.4) × 108, (4.76±0.1) × 109, (1.01±0.1) × 1010 and (3.29±0.2) × 109 L·mol-1·s-1, respectively. Density functional theory (DFT) calculations were performed to determine the optical properties of unstable CBzs anion radicals, and the main absorption peaks lied in the range of 300–550 nm. The primary reaction pathway of CBzs with eaq- was gradual dechlorination, and the major products were Cl- and benzene (CBzs(-Cl-)). Furthermore, biphenyl (or chlorobiphenyl) was observed during the LFP, which was probably formed by recombination of benzene radicals.

Keywords chlorinated benzenes      hydrated electron      electron beam      laser flash photolysis     
Corresponding Author(s): Hongjing LI,Wenbo DONG   
Online First Date: 10 April 2014    Issue Date: 25 June 2015
 Cite this article:   
Haixia YUAN,Huxiang PAN,Jin SHI, et al. Kinetics and mechanisms of reactions for hydrated electron with chlorinated benzenes in aqueous solution[J]. Front. Environ. Sci. Eng., 2015, 9(4): 583-590.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-014-0691-8
https://academic.hep.com.cn/fese/EN/Y2015/V9/I4/583
CBzs initial concentration/(mg·L-1) removal efficiency /%
10 kGy 20 kGy 30 kGy 40 kGy 50 kGy
mono-CB 43.5153.9 41.237.7 44.037.9 47.041.6 47.645.1 55.247.4
1,2-diCB 53.3144.5 94.587.2 97.192.0 97.092.2 98.394.2 99.195.8
1,3-diCB 77.8144.4 86.984.0 93.891.6 95.892.4 96.694.4 99.895.0
1,4-diCB 92.3152.3 92.184.1 94.491.4 96.993.0 97.194.5 98.295.2
Tab.1  Removal efficiency of CBzs under different initial concentrations
Fig.1  HPLC chromatogram at 30 kGy of mono-CB and 1,2-diCB
Fig.2  Concentrations of irradiation products of mono-CB (a), 1, 2-diCB (b), 1, 3-diCB (c) and 1, 4-diCB (d) in N2 saturated ethanol aqueous solution
CBzs G values
CBzs Cl- mono-CB benzene
mono-CB 0.54 0.21 0.18
1,2-diCB 0.82 0.35 0.025 0.005
1,3-diCB 0.82 0.35 0.027 0.004
1,4-diCB 0.82 0.35 0.025 0.004
Tab.2  G values at 10 kGy of 150 mg·L-1 CBzs solution in the presence of ethanol (mole·100 ev-1)
Fig.3  Decay kinetics of e a q - at 690 nm in the presence of mono-CB measured by LFP. Insert: linear dependence of the pseudo-first-order decay rate of e a q - with mono-CB concentration
CBzs k /(L·mol-1·s-1) (this work) k/(L·mol-1·s-1) [21]
chlorobenzene (5.44±0.4) × 108 5.0 × 108
m-dichlorobenzene (1.01±0.1) × 1010 5.2 × 109
o-dichlorobenzene (4.76±0.1) × 109 4.7 × 109
p-dichlorobenzene (3.29±0.2) × 109 5.0 × 109
Tab.3  Rate constants for reactions of e a q - with CBzs
CBzs anions radicals calculation absorbance peaks oscillator strengths
mono-CB anions radical 350.0 nm f = 0.3144
1,2-diCB anions radical 469.7 nm332.5 nm f = 0.1206f = 0.0166
1,3-diCB anions radical 340.0 nm346.2 nm f = 0.1471f = 0.1394
1,4-diCB anions radical 550.0 nm450.0 nm f = 0.0589f = 0.0367
Tab.4  Optical properties of CBzs anions radical
Fig.4  Major reaction pathway of CBzs with e a q -
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