Abstract:Two remote maritime populations were evaluated for their biological exposure to orgnochlorines in [1989][1990] Because of their high intake ofseafood, these two populations have high biological levels. One hundred nine breast milk samples from Inuit women from Arctic Quebec were analyzed to determine levels of polychlorodibenzo-p-dioxins (PCDDs), polychlorinated dibenzofrans (PCDFs), and coplanar polychlorinated bipheuWls (PCBs) including non-ortho, mono-oriho, and di-outho congeners. Total 2,3,7,-tetrachlorod… Show more
“…In Canadian Inuit, the serum ratio of non-DL-PCBs (e.g., PCB-153) to the DL-PCB levels was higher than for Canadian Caucasians from the Arctic area (18,40). In the present study, among the 14 PCB congeners the plasma levels of 11 non-DL-PCBs and 3 mono-ortho-DL-PCBs (#105, #118, #156) were determined.…”
Section: Discussionmentioning
confidence: 62%
“…The latter group is made up of weak AhR ligands with very low or no TEF values, whereas di-ortho PCBs are non-DL-PCBs (15). The 3 most highly bioaccumulated di-ortho PCBs (138, Plasma dioxin-like activity in Greenlandic Inuit and Danish women 153, 180) make up to 55% of the total PCBs in human matrices (16,17) and they are found in Inuit breast milk and the blood of north shore fishermen in Arctic Quebec at concentrations between 10 and 30 times higher compared with Caucasian controls, respectively (18).The higher chlorinated PCBs have the potential to inhibit the AhR function (19,20). These results emphasize that assessment of the toxicological potential of a chemical mixture is much more complex than can be deduced by a given TEQ value.…”
Objectives.(1) To determine whether plasma dioxin-like (DL) bioactivity differs between Inuit living in different Greenlandic districts, (2) to compare the DL activity of the Inuit having high burdens of POPs with a low-burden study group (Danish volunteers), and (3) to evaluate DL activity associations to POP exposure biomarkers and/or lifestyle factors. Study design. The study was a cross-sectional survey, including randomized inhabitants (70) from 6 different Greenlandic districts and young Danish volunteers (22). Methods. POPs and fatty acids profiles were analysed. Aryl hydrocarbon receptor (AhR) mediated DL-activity was determined by exposure of Hepa1.12cR AhR-CALUX reporter cell line to hexane: ethanol plasma extracts. Results. The sum PCBs/POPs level of Inuit was more than10 times higher than the levels found in Danish volunteers, and for both study groups the level was positively associated with age. The TCDD equivalent of the determined DL-activity, AhR-TEQ, differed between the Greenlandic districts. The AhR-TEQ data of the combined Inuit was significantly higher compared with the Danish women. AhR-TEQ of Inuit were positively associated with plasma POPs after adjustment for age and/or the ratio of n-3 to n-6 fatty acids, whereas no correlations were found for the Danish samples. Conclusions. AhR-TEQ differs between Inuit and Danish plasma samples. Plasma POP levels alone cannot be used as a biomarker for DL-activity. We suggest that the profile and level of plasma POPs, geographical location and diet have the greatest impact on plasma dioxin activity. Further studies are needed to elucidate the differences in geographical determinants of blood DL-activity.
“…In Canadian Inuit, the serum ratio of non-DL-PCBs (e.g., PCB-153) to the DL-PCB levels was higher than for Canadian Caucasians from the Arctic area (18,40). In the present study, among the 14 PCB congeners the plasma levels of 11 non-DL-PCBs and 3 mono-ortho-DL-PCBs (#105, #118, #156) were determined.…”
Section: Discussionmentioning
confidence: 62%
“…The latter group is made up of weak AhR ligands with very low or no TEF values, whereas di-ortho PCBs are non-DL-PCBs (15). The 3 most highly bioaccumulated di-ortho PCBs (138, Plasma dioxin-like activity in Greenlandic Inuit and Danish women 153, 180) make up to 55% of the total PCBs in human matrices (16,17) and they are found in Inuit breast milk and the blood of north shore fishermen in Arctic Quebec at concentrations between 10 and 30 times higher compared with Caucasian controls, respectively (18).The higher chlorinated PCBs have the potential to inhibit the AhR function (19,20). These results emphasize that assessment of the toxicological potential of a chemical mixture is much more complex than can be deduced by a given TEQ value.…”
Objectives.(1) To determine whether plasma dioxin-like (DL) bioactivity differs between Inuit living in different Greenlandic districts, (2) to compare the DL activity of the Inuit having high burdens of POPs with a low-burden study group (Danish volunteers), and (3) to evaluate DL activity associations to POP exposure biomarkers and/or lifestyle factors. Study design. The study was a cross-sectional survey, including randomized inhabitants (70) from 6 different Greenlandic districts and young Danish volunteers (22). Methods. POPs and fatty acids profiles were analysed. Aryl hydrocarbon receptor (AhR) mediated DL-activity was determined by exposure of Hepa1.12cR AhR-CALUX reporter cell line to hexane: ethanol plasma extracts. Results. The sum PCBs/POPs level of Inuit was more than10 times higher than the levels found in Danish volunteers, and for both study groups the level was positively associated with age. The TCDD equivalent of the determined DL-activity, AhR-TEQ, differed between the Greenlandic districts. The AhR-TEQ data of the combined Inuit was significantly higher compared with the Danish women. AhR-TEQ of Inuit were positively associated with plasma POPs after adjustment for age and/or the ratio of n-3 to n-6 fatty acids, whereas no correlations were found for the Danish samples. Conclusions. AhR-TEQ differs between Inuit and Danish plasma samples. Plasma POP levels alone cannot be used as a biomarker for DL-activity. We suggest that the profile and level of plasma POPs, geographical location and diet have the greatest impact on plasma dioxin activity. Further studies are needed to elucidate the differences in geographical determinants of blood DL-activity.
“…In addition, as OCPs are lipophylic and capable of being biomagnified, they could pose a serious threat to upper trophic levels of aquatic communities and potentially to humans. Many studies have reported that people consuming large amounts of contaminated seafood may have elevated concentrations of pollutants in their tissues compared with the general population (e.g., Asplund et al, 1994;Dewailly et al, 1994). From the human health viewpoint, the presence of OCPs in seafood should be of great concern due to their potential risks as they can cause a range of adverse human health effects, such as cancer, reproductive effects, and acute and chronic injury to the nervous system (Hayes et al, 1971).…”
“…The consumption of these contaminated fish will exceed the risk-based concentration of ''zero'' recommended by the US EPA (1996). People consuming large amounts of contaminated seafood may have elevated concentration of heavy metals in their tissues compared to the general population (Asplund et al 1994;Dewailly et al 1994). A correlation between blood mercury levels and methylmercury exposure via fish consumption has been shown in several different studies (Grandjean et al 1992;Svensson et al 1992;Oskarsson et al 1996).…”
Abstract. The purpose of this paper is to describe the impact of metal pollution on the main seafood and assess the potential health risk from consuming the contaminated seafood in Taiwan. The results of geometric mean (GM) metal concentrations in various seafood showed that the copper, zinc, and arsenic concentrations in oysters were significantly (p Ͻ 0.001) higher than those in the other seafood by about 1,057, 74.3, and 56.2 times, respectively. The green color found in the oysters was due to high GM copper and zinc concentrations of 909 (ranging from 113-2,805) and 1,293 (ranging from 303-3,593) µg/g dry wt, respectively. In addition, using a maximum consumption rate of 139 g/day of oysters for individuals, calculations yield target hazard quotients (daily intake/ reference dose) of below 1 for cadmium and mercury and high values of 1.61, 9.33, and 1.77 for inorganic arsenic, copper, and zinc in adults, respectively. The various lifetime cancer risks for inorganic arsenic (maximum exposed individuals risk ranging from 9.93 ϫ 10 Ϫ6 to 3.11 ϫ 10 Ϫ4
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