Abstract

The qualitative and quantitative analysis of 16 polycyclic aromatic hydrocarbons (PAHs) in sludge samples from drinking water treatment plants (DWTP) and wastewater treatment plants (WWTP) were established using gas chromatography–mass spectrometry (GC-MS). The method was suitable to quantify PAHs in the sludge of DWTP and WWTP and it was confirmed by the relevant quality assurance/quality control (QA/QC) procedures. The recovery of individual PAHs in the spiked samples ranged from 74.3% to 108.7%. Detection limits of the analytical procedure were 0.0010–0.0046 mg/kg dw for individual PAHs. This method was used to determine the concentration of PAHs in the selected two DWTP and four WWTP sludge samples. The results showed that the total PAHs (∑PAHs) were in low levels which ranged from 0.0668 to 0.1357 mg/kg dw, and 0.5342–1.0666 mg/kg dw for DWTP and WWTP respectively. The 3- & 4-ring PAHs were predominant in DWTP sludge, ranging from 77.4% to 82.7%; the 4-ring PAHs were predominant in WWTP sludge, ranging from 40.7% to 47.6%. The PAHs of DWTP sludge are mainly composed of 3-ring phenanthrene and anthracene and 4-ring pyrene, and chrysene. The PAHs of WWTP sludge are dominated by 4-ring fluoranthene, pyrene, and chrysene. The detected PAHs concentration should be undoubtedly considered for agriculture in sludge applications based on the limits of the EU regulations. The results of this study can be used for regular monitoring to establish a reference for sludge management and application to agriculture.

Highlights

  • With the growth of urbanization, changes in industrial structure and raising awareness of environmental protection, drinking water treatment plants (DWTP) and wastewater treatment plants (WWTP) have been extensively built

  • Sixteen polycyclic aromatic hydrocarbons (PAHs) were quantified using the response factors related to the respective internal standards based on a five-point calibration curve for individual compounds

  • The results showed that 16 PAHs could be effectively separated (Figure 1A)

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Summary

Introduction

With the growth of urbanization, changes in industrial structure and raising awareness of environmental protection, drinking water treatment plants (DWTP) and wastewater treatment plants (WWTP) have been extensively built. The quality of drinking water and rates of sewage treatment has increased. DWTP and WWTP ensure the safety of drinking water and reduce environmental water pollution problems, the sludge they produce is a potential threat to the environment. The sludge may contain hundreds of organic toxic compounds (e.g., polycyclic aromatic hydrocarbons (PAHs), phthalate esters (PAEs), alkylphenol polyethoxylates, synthetic musks, antibiotics, ultraviolet stabilizers, bisphenol analogs, organochlorine pesticides, polybrominated diphenyl ethers (PBDE), pharmaceuticals, hormones, perfluorinated compounds, and polychlorinated. Res. Public Health 2019, 16, 2604; doi:10.3390/ijerph16142604 www.mdpi.com/journal/ijerph

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