Sandimirov S. Screening studies of POP levels in fish from selected lakes in the Paz watercourse / In State of the environment in the Norwegian, Finnish and Russian border area. The Finnish Environment. Finland, Jyvaskyla: Kopijyva Oy. 2007, №6.

Appendix: Screening studies of POPs in fish from the Paz watercourse Table 3.10. Polycyclic aromatic hydrocarbons (PAH, ng/g wet weight) in pooled tissue samples o f whitefish andpike from Stuorajavri Lake in 2005 and TCDD-equivalents fo r dioxin-like PAHs (TEQPAH) (pgTEQ/g wet weight) calculated using toxic equivalencyfactors (TEFs) proposed by Klimm et al. (1997). N is number o f sub-samples, Wt is weight range. ________________________________________________________________________________________________ PAHs Whitefish, female Whitefish, male Pike, M&F N=13 N=6 N=9 N=10 N=6 N=5 Wt=100-200g Wt=300-400g Wt=400-500g Wt=100-200g Wt=200-300g Muscle Liver Muscle Liver Muscle Liver Muscle Liver Muscle Liver Muscle Liver Lipid, % 0.71 3.05 0.50 3.60 0.76 8.40 0.44 3.06 0.55 3.17 0.32 6.86 Naphthalene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. 1-Methylnaphtalene n.d. 8.91 n.d. n.d. n.d. n.d. n.d. 14.8 n.d. 22.2 n.d. 11.4 2-Methylnaphtalene n.d. n.d. n.d. n.d. n.d. n.d. n.d. 6.28 n.d. 6.64 n.d. n.d. C2-Naphtalenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C3-Naphtalenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C4-Naphtalenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Acenaphthylene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Acenaphthene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Fluorene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C1-Fluorenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C2-Fluorenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C3-Fluorenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Phenanthrene n.d. n.d. n.d. n.d. n.d. n.d. n.d. 4.02 n.d. 2.89 n.d. 1.90 Anthracene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C1-Phens/Anths 1.44 n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C2-Phens/Anths 1.84 4.21 n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. 2.11 5.54 C3-Phens/Anths 5.23 10.3 n.d. n.d. n.d. n.d. n.d. 7.82 n.d. n.d. 7.87 2.88 C4-Phens/Anths n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Dibenzothiophene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C1-Dibenzothiophenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C2-Dibenzothiophenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C3 -Dibenzothiophenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Fluoranthene 0.36 1.14 n.d. n.d. n.d. n.d. 0.25 2.01 n.d. n.d. 0.70 1.17 Pyrene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. 1.65 0.85 C1-Flanths/Pyrs n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C2-Flanths/Pyrs n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C3-Flanths/Pyrs n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Benzo(a)anthracene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. 1.62 1.31 1.21 Chrysene 0.31 0.78 n.d. n.d. n.d. n.d. n.d. n.d. n.d. 2.75 0.73 0.80 C1-Chrysenes 0.53 2.17 n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C2-Chrysenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C3-Chrysenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Benzo(b+j )fluoranthene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Benzo(k)fluoranthene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Benzo(e)pyrene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Benzo(a)pyrene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Perylene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Indeno( 1,2,3-c,d)pyrene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Dibenzo(a,h)anthracene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Benzo(g,h,i)perylene 4.92 23.4 n.d. n.d. n.d. n.d. n.d. 11.3 n.d. 33.8 7.63 24.5 SPAH 14.6 50.9 n.d. n.d. n.d. n.d. 0.25 46.2 n.d. 69.9 22 50.3 TEQ pah n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. 0.044 0.035 0.033 n.d.=not detected. Akvaplan-niva report APN 514-3365.02 64