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 Table3.10. Polycyclic aromatic hydrocarbons (PAH, ng/g wet weight) in pooled tissue samples o f whitefish (Coregonus lavaretus) and pike (Esox lucius) from lakes located in Pasvik River area 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. _____________________________________________________________________ PAHs White fish Pike Tj^rebukta Skrukkebukta Ruskebukta Kuetsjarvi Kuetsj arvi 4-5 years, Wt 100-500 g 3-5 years, Wt 100-300 g 4-6 years, Wt 300-500 g 3-5 years, Wt 50-140 g Muscle Liver Muscle Liver Mus cle Liver Muscle Liver Muscle Liver N=10 N=10 N=5 N=5 N= 5 N=5 N=10 N=15 N=10 N=10 Lipids, % 0.66 14.1 0.88 5.25 0.54 7.94 1.86 6.99 0.41 25.9 Naphthalene n.d. n.d. n.d. 28.3 n.d. 19.7 n.d. 102.0 n.d. 39.5 1-Methylnaphtalene n.d. 13.3 7.20 33.3 6.26 23.1 n.d. 90.5 n.d 13.8 2-Methylnaphtalene n.d. 7.97 n.d. 15.5 n.d. 11.4 n.d. 83.6 n.d. 31.4 C2-Naphtalenes n.d. 10.6 n.d. 22.4 n.d. 17.7 n.d. 44.9 n.d. 23.9 C3-Naphtalenes n.d. n.d. n.d. 6.75 n.d. n.d. n.d. n.d. n.d. 20.6 C4-Naphtalenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. 8.55 Acenaphthylene 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. Fluorene n.d. n.d. n.d. n.d. n.d. n.d. 0.5 n.d. n.d. 2.98 C1-Fluorenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. 2.62 C2-Fluorenes 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. Phenanthrene n.d. 1.45 n.d. 1.23 n.d. 1.22 1.24 6.82 n.d. 7.32 Anthracene n.d. 0.24 n.d. n.d. n.d. n.d. n.d. n.d. n.d. 0.38 C1-Phens/Anths n.d. n.d. 0.66 n.d. n.d. n.d. n.d. n.d. n.d. n.d. C2-Phens/Anths n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C3-Phens/Anths n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C4-Phens/Anths 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. C1-Dibenzothiophenes 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. C3-Dibenzothiophenes n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Fluoranthene n.d. 0.56 n.d. 0.63 n.d. 0.46 0.62 2.88 n.d. 3.24 Pyrene n.d. n.d. n.d. n.d. n.d. n.d. 0.62 0.34 n.d. 1.22 C1-Flanths/Pyrs 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. C3-Flanths/Pyrs 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. n.d. Chrysene n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. C1-Chrysenes 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. C3-Chrysenes 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. Benzo(k)fluoranthene 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. Benzo(a)pyrene 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. 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. Dibenzo(a,h)anthracene 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 n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. XPAH n.d. 34.12 7.86 101.86 6.26 73.58 2.48 286.14 n.d. 155.5 TEQ PAH n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. n.d. Akvaplan-niva report APN 514-3365.02 62