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. 2019 Apr;26(11):11300-11313.
doi: 10.1007/s11356-019-04586-4. Epub 2019 Feb 22.

PCB residues in the tissues of sea ducks wintering on the south coast of the Baltic Sea, Poland

Agnieszka Tomza-Marciniak  1 , Bogumiła Pilarczyk  2 , Agata Witczak  3 , Izabella Rząd  4 , Renata Pilarczyk  5
Affiliations

PCB residues in the tissues of sea ducks wintering on the south coast of the Baltic Sea, Poland

Agnieszka Tomza-Marciniak et al. Environ Sci Pollut Res Int. 2019 Apr.

Abstract

The Baltic Sea is known to be severely polluted by a range of chemicals, one group of which being PCBs. Although the use and production of PCBs were limited or banned in many countries in the 1970s, their presence is still observed in the environment. The aim of this study was to evaluate PCBs concentration in four species of diving sea ducks, interspecies and tissues differences, and in the case of game species, comparison of the obtained results with maximal residue levels (MRLs) and tolerable weekly intake (TWI). The level of Σi-PCBs was noted in most examined samples (liver, muscle, fat tissue) at levels ranging between < LoD and 2315.45 ng/g lw. The dominant congener was PCB 153, followed by PCB 180 and 138. The mean dl-PCB-TEQ value in the muscles of the tested tufted ducks and common pochards was 0.31 and 0.71 pg-TEQ/g lw, respectively, which is 8-25 and 18-57% of the TEQ maximum limit (ML) value for farm animal muscles. The average decrease in i-ΣPCB concentration in the fat tissue of ducks wintering in the Baltic Sea southern coast was found to be 2.9-3.3%/year. The analysis of PCB residues indicates that the common pochard and tufted duck are not suitable for consumption due to high Σi-PCB concentrations. However, the regular consumption of muscle and liver of game birds does not result in an unacceptable intake of dl-PCBs, i.e., above the TWI value.

Keywords: Baltic Sea; Biomonitoring; PCBs; Sea ducks; TEQ.

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Figures

Fig. 1
Fig. 1
Location of sample collection
Fig. 2
Fig. 2
The concentrations (mg/kg lw) of homologs in the examined seabird tissues
Fig. 3
Fig. 3
Temporal differences in PCB residues
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