Abstract

Toxicity and transformation process of polycyclic aromatic hydrocarbons (PAHs) is strongly depended on the interaction between PAHs and dissolved organic matters (DOM). In this study, a 125W high-pressure mercury lamp was used to simulate the sunlight experiment to explore the inhibition mechanism of four dissolved organic matters (SRFA, LHA, ESHA, UMRN) on the degradation of anthracene and pyrene in water environment. Results indicated that the photodegradation was the main degradation approach of PAHs, which accorded with the first-order reaction kinetics equation. The extent of degradation of anthracene and pyrene was 36% and 24%, respectively. DOM influence mechanism on PAHs varies depending upon its source. SRFA, LHA and ESHA inhibit the photolysis of anthracene, however, except for SRFA, the other three DOM inhibit the photolysis of pyrene. Fluorescence quenching mechanism is the main inhibiting mechanism, and the binding ability of DOM and PAHs is dominantly correlated with its inhibiting effect. FTIR spectroscopies and UV–Visible were used to analyze the main structural changes of DOM binding PAHs. Generally, the stretching vibration of N–H and C–O of polysaccharide carboxylic acid was the key to affect its binding with anthracene and C–O–C in aliphatic ring participated in the complexation of DOM and pyrene.

Highlights

  • Toxicity and transformation process of polycyclic aromatic hydrocarbons (PAHs) is strongly depended on the interaction between Polycyclic aromatic hydrocarbons (PAHs) and dissolved organic matters (DOM)

  • − ln CCot = kt t1 = 0.693 k where t is the photolysis time, Ct is the concentration of PAHs in the photolysis solution at time t, C0 is the concentration of PAHs in the initial photolysis solution, K is the apparent photolysis rate constant of PAHs

  • The extent of degradation of anthracene and pyrene can reach 36% and 24%, which shows that anthracene is easier to photolysis in water environment

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Summary

Introduction

Toxicity and transformation process of polycyclic aromatic hydrocarbons (PAHs) is strongly depended on the interaction between PAHs and dissolved organic matters (DOM). The inhibition mechanism is mainly embodied in the abundant conjugated chromophore structure in DOM, which may be related to the photoshielding effect of organic pollutants competing to absorb light and the quenching effect of DOM on the excited state of pollutants[15]. This process is related to the bonding action between pollutant molecules[16]. Anthracene and pyrene are selected as model materials for PAHs study to explore the mechanism of photodegradation of polycyclic aromatic hydrocarbons (PAHs) caused by four DOMs from land sources (LHA and ESHA) and water sources (SRFA and UMRN)

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