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Coking wastewater treatment plant as a sources of polycyclic aromatic hydrocarbons (PAHs) in sediments and ecological risk assessment.


ABSTRACT: The spatial and temporal distribution of polycyclic aromatic hydrocarbons (PAHs) was investigated in sediments of Maba River, a major tributary of Beijiang River (South China). A total of 13 samples from Maba River and its tributary, Meihua River, were analyzed for 16 PAHs. The total concentration of 16 PAHs (?PAH) in high and low water period ranged between 47.61 to 25480.98?ng?g-1, with a mean concentration of 4382.98?ng?g-1, and 60.30 to 15956.62?ng?g-1 with a mean concentration of 3664.32?ng?g-1, respectively. Three-ring and four-ring PAHs were the dominant species. It was concluded that a pattern of pyrolytic input as a major source of PAHs in sediments through the molecular ratio method for the source identification, such as HMW/LMW PAHs, Flu/(Flu+Pyr), IcdP/(IcdP+BghiP) and BaA/(BaA+Chr). It is suggested that the pollution emission from the iron and steel plant might be the most important sources of PAHs into Maba River water system. The threat of PAHs contamination to biota of the river was assessed using effect range low (ERL) and effect range median (ERM) values, which suggested that PAHs in Maba River and its tributary had already caused ecological risks.

SUBMITTER: Chen J 

PROVIDER: S-EPMC7217903 | biostudies-literature | 2020 May

REPOSITORIES: biostudies-literature

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Coking wastewater treatment plant as a sources of polycyclic aromatic hydrocarbons (PAHs) in sediments and ecological risk assessment.

Chen Jundong J   Liao Jianbo J   Wei Chaohai C  

Scientific reports 20200512 1


The spatial and temporal distribution of polycyclic aromatic hydrocarbons (PAHs) was investigated in sediments of Maba River, a major tributary of Beijiang River (South China). A total of 13 samples from Maba River and its tributary, Meihua River, were analyzed for 16 PAHs. The total concentration of 16 PAHs (ΣPAH) in high and low water period ranged between 47.61 to 25480.98 ng g<sup>-1</sup>, with a mean concentration of 4382.98 ng g<sup>-1</sup>, and 60.30 to 15956.62 ng g<sup>-1</sup> with a  ...[more]

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