Abstract

The availability of bound residues of polycyclic aromatic hydrocarbons (PAHs), in reference to their parent compounds, can be enhanced by microbial activity and chemical reactions, which pose severe risks for the ecosystems encompassing contaminated soils. Considerable attention has been raised on how to remove these bound residues from PAH-contaminated soils. This paper provides a novel application of Fenton oxidation in the removal of bound residues of model PAHs, such as naphthalene (NAP), acenaphthene (ACP), fluorene (FLU) and anthracene (ANT), from naturally contaminated soils. The citric acid-enhanced Fenton treatment resulted in the degradation of bound PAH residues that followed pseudo-first-order kinetics, with rate constants within 4.22 × 10−2, 1.25 × 10−1 and 2.72 × 10−1 h−1 for NAP, FLU, and ANT, respectively. The reactivity of bound PAH residues showed a correlation with their ionization potential (IP) values. Moreover, the degradation rate of bound PAH residues was significantly correlated with H2O2-Fe2+ ratio (m/m) and H2O2 concentrations. The highest removal efficiencies of bound PAH residues was up to 89.5% with the treatment of chelating agent oxalic acid, which was demonstrated to be superior to other acids, such as citric acid and hydrochloric acid. This study provides valuable insight into the feasibility of citric acid-Fenton and oxalic acid-Fenton treatments in rehabilitating bound PAH residues in contaminated soils.

Highlights

  • Polycyclic aromatic hydrocarbon (PAHs), a class of toxic organic pollutants, are composed of multiple fused aromatic rings in linear, angular or cluster arrangements

  • The results indicated that higher degradation of bound polycyclic aromatic hydrocarbons (PAHs) residues and higher H2O2 concentration alone may restrain the removal

  • The present study demonstrated that citric acid enhanced the Fenton treatment in bound PAH residues (NAP, FLU, and ANT) degradation, which followed pseudo-first-order kinetics

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Summary

Introduction

Polycyclic aromatic hydrocarbon (PAHs), a class of toxic organic pollutants, are composed of multiple fused aromatic rings in linear, angular or cluster arrangements. PAHs have generated extreme concern due to their toxicity, teratogenicity, carcinogenicity, and mutagenesis to humans and the wider environment. They are mainly released by incomplete combustion of fossil fuels or activities in the petrochemical industry, including crude oil refining, coal tar production, and asphalt production [4,5]. Owing to their high hydrophobicity and persistence, soils are the ultimate repository of PAHs with concentration up to hundreds of mg/kg in many countries [6,7]. An urgent need globally to reduce the contamination risks to human and environmental health through remediating PAH-contaminated soils

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