Abstract

Degradation of 2,4,6-trichlorophenol (2,4,6-TCP) by zero-valent iron (ZVI) activating three common peroxides (peroxymonosulfate (PMS), hydrogen peroxide (H2O2), and peroxydisulfate (PS)) was investigated. The effects of ZVI dosage, peroxides concentration, initial pH, and Cl- concentration were examined. The 2,4,6-TCP degradation efficiencies by Fe0/peroxides (PMS, H2O2, PS) were compared. Results showed that the order for degradation efficiency was H2O2≥PMS>PS. The degradation efficiency of 2,4,6-TCP in ZVI/peroxides systems were optimal at c(Ox) = 1 mmol•L-1; c(Fe0) = 0.1 g/L; initial pH = 3.2. Additionally, pH had a vital effect on 2,4,6-TCP degradation. At pH<3.2, ferrous play a vital role in all reaction, and accelerate the reaction rate rapidly. The existence of NaCl showed different results in the four systems. Chloride had little effect on 2,4,6-TCP degradation when chloride concentration at 5 mM, whereas the presence of 300 mM chloride significantly accelerated the degradation of 2,4,6-TCP from 72.7% to 95.2% in ZVI-PMS system. Notably, the other three systems showed opposite results. In contrast, the AOX (Absorbable Organic Halogen) values were highest in ZVI-PMS-Cl- system, due to the formation of lots of refractory chlorinated phenols as identified by GC-MS. These findings are good for choosing the most suitable technology for chlorophenol wastewater treatment.

Highlights

  • Chlorophenols are widely used in different kinds of areas, such as wood preservers, pesticides, herbicides, biocides, and dyes [1, 2]. due to the numerous sources, chlorophenols have been found in groundwater and wastewater [3]

  • Chlorophenols are persistent, hardly biodegradable and accumulate in the environment. These substances have been reported to have adverse effects on the nervous system and have been connected to many health disorders. 2,4,6-TCP has been designated as a priority pollutant, and listed in the Drinking Water Contaminant Candidate List (CCL) [4, 5]

  • These researches have showed the oxidation caused by free radicals which were generated by zero-valent iron (ZVI) activating hydrogen peroxide (H2O2, E0(H2O2/H2O) = 1.77 V vs NHE (Normal Hydrogen Electrode)), peroxydisulfate (PS, S2O82, E0(S2O82-/SO42-) = 2.01 V vs NHE), and peroxymonosulfate (PMS, HSO5, E0(HSO5-/HSO4-) = 1.85 V vs NHE)

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Summary

Introduction

Chlorophenols are widely used in different kinds of areas, such as wood preservers, pesticides, herbicides, biocides, and dyes [1, 2]. due to the numerous sources, chlorophenols have been found in groundwater and wastewater [3]. Oh et al [16] reported spent caustic degradation using Fenton and persulfate oxidation with ZVI, spent caustic was mineralized when iron powder added into hydrogen peroxide or persulfate solution These researches have showed the oxidation caused by free radicals which were generated by ZVI activating hydrogen peroxide (H2O2, E0(H2O2/H2O) = 1.77 V vs NHE (Normal Hydrogen Electrode)), peroxydisulfate (PS, S2O82-, E0(S2O82-/SO42-) = 2.01 V vs NHE), and peroxymonosulfate (PMS, HSO5-, E0(HSO5-/HSO4-) = 1.85 V vs NHE). ZVI as a reducing agent can lead to the dechlorination of 2,4,6-TCP; the existence of peroxygens can further decompose 2,4,6-TCP to other chlorinated compounds In such complex systems, we cannot yet determine the degradation mechanism of 2,4,6-TCP. The best technology for contaminant elimination with ZVI-based peroxygen systems can be chosen from an environmentally friendly point of view

Materials
Experimental procedures
Analysis
Results and discussion
GC-MS analysis
AOX formation
Conclusions
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