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Forty-seven fish (24 endemic Alburnus tarichi, Güldenstädt, 1814; 8 Capoeta capoeta, Guldenstaedt, 1772; 15 mirror carp Cyprinus carpio, L., 1758) and 13 mussel (Unio stevenianus, Krynicki, 1837) samples, with 10 specimens per sample, were collected from Van Lake, Turkey, and rivers flowing into it. Gamma-HCH was detected in 21 Alburnus tarichi samples (56.57 ng/g ± 22.18 ng/g) and in two Capoeta capoeta samples (27.6 ng/g and 36.45 ng/g). Beta-HCH was detected in 8 Alburnus tarichi samples (24.95 ng/g ± 4.42 ng/g) and in two mussel samples (101.25 ng/g and 129.44 ng/g). HCB was found in one Alburnus tarichi sample (14.4 ng/g) and one mussel sample (181.25 ng/g). The compound 4,4'-DDE was detected in 21 Alburnus tarichi samples (87.13 ng/g ± 32.23 ng/g), in 9 mirror carp samples (304.82 ng/g ± 100.76 ng/g) and one mussel sample (149.31 ng/g). PCB 28 was detected in one Alburnus tarichi (19.46 ng/g) sample and PCB 101 was found in one Capoeta capoeta (60.16 ng/g) sample. PCB 118 was detected in one mirror carp sample (277.5 ng/g) and in two Capoeta capoeta samples (43.77 and 54.38 ng/g). PCB 128 was detected in only one Capoeta capoeta sample (141.48 ng/g). It is concluded that (i) efforts should be made to reduce contamination of aquatic environments by these compounds and that (ii) their levels in fishery products from Van Lake and connected streams should be monitored and publicly reported on a regular basis.

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In this study, the levels of a group of organochlorine pesticides (OCPs) and polychlorinated biphenyls (PCBs) in the adipose tissue of women living in northern Turkey who gave birth by cesarean delivery were investigated. Sixty subcutaneous samples were collected in 2013 from women in urban (30) and rural (30) areas. The levels of nine OCPs, namely α-hexachlorocyclohexane (HCH), β-HCH (lindane), γ-HCH, hexachlorobenzene (HCB), aldrin, and dichlorodiphenyltrichloroethane (DDT) and its metabolites, 2,4'-dichlorodiphenyldichloroethylene (DDE), 4,4'-DDE, 2,4'-DDT, 4,4'-DDT, and 16 PCBs, PCB-28, -52, -70, -74, -81, -99, -101, -118, -138, -153, -156, -170, -180, -183, -187 and -208, were investigated with a gas chromatograph equipped with an electron capture detector (GC-ECD). β-HCH was detected in nine samples (mean 23.70 ± 4.24 ng g of fat) and γ-HCH was detected in six samples (mean 41.88 ± 12.41 ng g of fat). HCB was detected in five samples (mean 30.97 ± 14.31 ng g of fat), 2,4'-DDT in one sample (5 ng g of fat), 4,4-DDT in two samples (mean 6.70 ± 0.42 ng g of fat), 2,4'-dichlorodiphenyldichloroethylene in three samples (mean 6.27 ± 0.42 ng g of fat), PCB-28 in six samples (mean 10.03 ± 7.79 ng g of fat), PCB-81 in one sample (7.60 ng g of fat) and PCB-118 in one sample (10.20 ng g of fat). In total, organochlorine compounds were detected in 12 (40%) of rural and 12 (40%) of urban women. These results are an indication of the level of organochlorine compounds in the environment where the subjects of the study lived.

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The aim of this study was the determination of plasma concentrations of organochlorine pesticides (OCPs) and polychlorinated biphenyls (PCBs) in cats and dogs and evaluation of their prevalence and possible effects. The concentrations of nine OCPs, such as α-hexachlorocyclohexane (HCH), β-HCH, γ-HCH, hexachlorobenzene (HCB), aldrin, 2,4'-dichlorodiphenyltrichloroethane (2,4'-DDT), 4,4'-DDT, 2,4'-dichlorodiphenyldichloroethylene (2,4'-DDE) and 4,4'-DDE and 16 PCBs (PCB-28, -52, -70, -74, -81, -99, -101, -118, -138, -153, -156, -170, -180, -183, -187 and -208) were evaluated in the plasma samples of pet cats ( n = 15) and dogs ( n = 21). The concentrations of OCPs ranged from 1.12 ng g lipid weight (lw) to 7.65 ng g lw in cats and from 1.25 ng g lw to 6.79 ng g lw in dogs. In addition, mean PCB levels were 0.58-5.66 and 0.52-6.62 ng g lw in cats and dogs, respectively. β-HCH, γ-HCH and PCB-138 levels were significantly higher in dogs ( p < 0.05). As far as could be determined, OCPs and PCBs were detected in the plasma samples of domestic cats and dogs in Turkey for the first time. Their concentrations were similar to those reported in earlier studies abroad. However, in contrast to other research, the levels of some OCPs were higher in dogs than in cats. It is concluded that, because of their high prevalence and potential health effects in animals and humans, OCP and PCB levels should be monitored systematically in domestic cats and dogs.

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