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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 Envir Sci Eng    2012, Vol. 6 Issue (2) : 171-176    https://doi.org/10.1007/s11783-011-0319-1
RESEARCH ARTICLE
Kinetics of oxidation of dimethyl trisulfide by potassium permanganate in drinking water
Xiaoyan MA1(), Shifei HU1, Hongyu WANG1, Jun LI1, Jing HUANG1, Yun ZHANG2, Weigang LU1, Qingsong LI3
1. Municipal Department of Architecture Engineering College, Zhejiang University of Technology, Hangzhou 310014, China; 2. National Water Quality Monitoring Net of City Water Supply Hangzhou Station, Hangzhou 310014, China; 3. Water Resources and Environmental Institute, Xiamen University of Technology, Xiamen 361005, China
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Abstract

Metabolites of algae such as geosmin, 2-methylisoborneol etc. are reported to induce pungent odors into drinking water and attract additional scientific attention. Recently, in China, taste and odor outbreaks in drinking water supply have become increasingly common. In source water affected by eutrophication, dimethyl trisulfide, speculated to be produced by decayed algae, was found to be the source of taste and odor issues and can be removed effectively by usual oxidation agents. In this experimental study, batch scale tests were carried out focusing on the removal of dimethyl trisulfide. Reaction kinetics of dimethyl trisulfide oxidized by potassium permanganate in water had been studied; influence factors such as pH, organic substrate, other existed taste, and odor contaminant in equivalent concentration were also discussed. Results showed that dimethyl trisulfide can be removed by potassium permanganate efficiently; the ratio can reach more than 70% with oxidant dosage of 4 mg·L-1 and contact time prolonged to 120 min. The dimethyl trisulfide decomposition followed a second-order kinetics pattern with a rate constant k = 0.00213 L·(min·mg)-1. Typically, the degradation rate of dimethyl trisulfide was increased with the increasing KMnO4 dosage, but dramatically dropped with the increasing levels of humic acid (1.8–4.5 mg·L-1) and other odor-causing compounds (e.g. β-cyclocitral, 0–1886.0 μg·L-1). Solution pH (5.2–9.0) and initial dimethyl trisulfide concentration did not significantly affected the degradation. This study demonstrates that KMnO4 oxidation is an effective option to remove dimethyl trisulfide from water.

Keywords odor and taste      oxidation reaction      reaction kinetics      water treatment     
Corresponding Author(s): MA Xiaoyan,Email:mayaner620@163.com   
Issue Date: 01 April 2012
 Cite this article:   
Jun LI,Jing HUANG,Yun ZHANG, et al. Kinetics of oxidation of dimethyl trisulfide by potassium permanganate in drinking water[J]. Front Envir Sci Eng, 2012, 6(2): 171-176.
 URL:  
https://academic.hep.com.cn/fese/EN/10.1007/s11783-011-0319-1
https://academic.hep.com.cn/fese/EN/Y2012/V6/I2/171
Fig.1  Degradation of dimethyl trisulfide under different dosages of potassium permanganate
Fig.2  Oxidation fit curves of dimethyl trisulfide under different dosages of potassium permanganate
dosage of permanganate /(mg·L-1)fitting equationkobs/min-1R2t1/2/min
1ln c = -0.0021t + 6.18540.00210.920330
2ln c = -0.005t + 6.10360.0050.921138.6
3ln c = -0.0081t + 6.06310.00810.90985.6
4ln c = -0.0107t + 5.98530.01070.91564.8
Tab.1  Kinetics parameters of dimethyl trisulfide under different dosage of potassium permanganate
Fig.3  Oxidation fit curves of dimethyl trisulfide under different initial concentrations
inatial concentration of dimethyl trisulfide /(μg·L-1)fitting equationk/min-1R2t1/2/min
272.8ln c = -0.0088 t + 5.4310.00880.92478.8
381.3ln c = -0.0083 t + 5.79990.00830.94283.5
490.2ln c = -0.0087 t + 5.99650.00870.89979.6
651.3ln c = -0.0082 t + 6.33260.00820.92984.5
Tab.2  Oxidation kinetics parameters of dimethyl trisulfide under different initial concentrations
initial concentration of dimethyl trisulfide/(μg·L-1)potassium permanganate dosage/(mg·L-1)rate constant kobs/min-1initial rate of reaction r/(μg·L-1·min-1)
500.210.00211.02
493.320.0052.24
519.230.00813.48
490.240.01074.25
272.830.00882.00
381.330.00832.74
651.330.00824.61
Tab.3  Initial response parameters of dimethyl trisulfide oxidized by potassium permanganate
Fig.4  Relationship of lg and initial concentrations at initial dimethyl trisulfide = 500 μg·L
Fig.5  Relationship of initial rates and initial concentration of CHS at condition of constant dosage 3 mg·L of
Fig.6  Degradation speed of dimethyl trisulfide by KMnO at different initial pH
Fig.7  Degradation speed of dimethyl trisulfide by KMnO at different dosage of humic acid
Fig.8  Degradation speed of dimethyl trisulfide by KMnO at different concentrations of coexisting -cyclocitral
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