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Multiyear levels of PCDD/Fs, dl-PCBs and PAHs in background air in central Europe and implications for deposition. | LitMetric

AI Article Synopsis

  • This study analyzed four years of environmental monitoring data for various toxic compounds, focusing on polychlorinated dibenzo-p-dioxins and dibenzofurans (PCDD/Fs), dioxin-like polychlorinated biphenyls (dl-PCBs), and polycyclic aromatic hydrocarbons (PAHs) in central Europe from 2011 to 2014.
  • The findings showed that while the toxic equivalents (TEQs) of PCDD/Fs were higher than those of dl-PCBs, the mass concentrations were the opposite, with ΣPAHs exhibiting a significant range in concentrations.
  • Over the study period, concentrations of PCDD/Fs remained stable, whereas levels of dl-PCBs and PA

Article Abstract

This study presents four years ambient monitoring data of seventeen 2,3,7,8-chlorine substituted polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans (PCDD/Fs), twelve dioxin-like polychlorinated biphenyls (dl-PCBs) and sixteen polycyclic aromatic hydrocarbons (PAHs) designed by the US EPA at a background site in central Europe during 2011-2014. The concentrations expressed as toxic equivalents (TEQs) using the WHO-scheme for PCDD/Fs (0.2 fg m-61.1 fg m) were higher than for dl-PCBs (0.01 fg m-2.9 fg m), while the opposite was found in terms of mass concentrations. ΣPAHs ranged from 0.20 ng m to 134 ng m. The mass concentration profile of PCDD/Fs, dl-PCBs and PAHs was similar throughout the four years. PCDD/Fs and PAHs concentrations were dominated by primary sources peaking in winter, while those of dl-PCBs were controlled by secondary sources characterized by a spring-summer peak. During 2011-2014, no significant decrease in the atmospheric levels of ΣPCDD/Fs was observed. On the other hand, the concentrations of Σdl-PCBs and ΣPAHs were decreasing, with halving times of 5.7 and 2.7 years, respectively. We estimated that 422 pg m year-567 pg m year TEQ PCDD/Fs and 3.48 pg m year-15.8 pg m year TEQ dl-PCBs were transferred from the air to the ground surfaces via dry particulate deposition during 2011-2014.

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Source
http://dx.doi.org/10.1016/j.chemosphere.2019.124852DOI Listing

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