Abstract To date, the leachates from municipal solid waste (MSW) landfills of south China (Guangxi province), which could be considerated as a source of polybrominated diphenyl ethers (PBDEs) to the environments, have received little investigation. To address this gap, 8 kinds of PBDEs were measured in the leachates taken from 15 MSW landfills in Guangxi province. The detection rates of PBDE-13, -47, -99, and -153 were 100%, while the value of PBDE-209 is only 60%, most likely due to the degradation of PBDE-209. The total concentrations of PBDEs (∑8PBDE) ranged from 0.78 to 12.43 ng·L−1. The dominant compounds of PBDE-13, -47, -99, and -209 amounted to 46.64–91.59% of the concentrations of ∑8PBDE. Redundancy analysis (RDA) results demonstrated that leachate pH had positive correlations with ∑7PBDE (except for PBDE-209) and ∑8PBDE with correlation coefficients of 0.73 (P 0.01) and 0.68 (P 0.05), respectively. Non-statistically significant but moderate impacts are obtained between the landfill age (Years and BOD5/COD) and total PBDE contents (r = 0.32–0.55, P 0.05). Similar results were also obtained in Linear Alkylbenzene Sulfonates (LAS). The total concentrations of PBDEs were primarily influenced by pH and LAS, with the interpretations of 44.0% (P = 0.032 0.05) and 38.8% (P = 0.046 0.05), respectively, but the effects of Total Dissolved Solids (TDS), Total Hardness (TH), Biochemical Oxygen Demand/Chemical Oxygen Demand (BOD5/COD), and Years were small and insignificant (P 0.05). These findings provide insights into the levels, compositions, and influencing factors of PBDEs in leachates from MSW landfills in south China.
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Liang et al. (Thu,) studied this question.
www.synapsesocial.com/papers/69c772d98bbfbc51511e34ef — DOI: https://doi.org/10.1093/etojnl/vgag079
Synapse has enriched 5 closely related papers on similar clinical questions. Consider them for comparative context:
Liuling Liang
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Environmental Toxicology and Chemistry
Guangxi University
Guangxi Academy of Sciences
Guangxi Science and Technology Department
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