BACKGROUND: Firefighting foam-contaminated ground water, which contains high levels of perfluoroalkyl substances (PFAS), is frequently found around airports. In 2018 it was detected that employees at a municipal airport in northern Sweden had been exposed to high levels of short-chain PFAS along with legacy PFAS (i.e., PFOA, PFHxS, and PFOS) through drinking water. OBJECTIVES: In this study, we aimed to describe the PFAS profile in drinking water and biological samples (paired serum and urine) and to estimate serum half-lives of the short-chain PFAS together with legacy PFAS. METHODS: Within 2 weeks after provision of clean water, blood sampling was performed in all 26 airport employees. Seventeen of them were then followed up monthly for 5 months. PFHxA, PFHpA, PFBS, PFPeS, and PFHpS together with legacy PFAS in water and biological samples were quantified using LC/MS/MS. Half-lives were estimated by assuming one compartment, first-order elimination kinetics. RESULTS: The proportions of PFHxA, PFHpA, and PFBS were higher in drinking water than in serum. The opposite was found for PFHxS and PFOS. The legacy PFAS accounted for about 50% of total PFAS in drinking water and 90% in serum. Urinary PFAS levels were very low compared with serum. PFBS showed the shortest half-life {average 44 d [95% confidence interval (CI): 37, 55 d]}, followed by PFHpA [62 d (95% CI: 51, 80 d)]. PFPeS and PFHpS showed average half-lives as 0.63 and 1.46 y, respectively. Branched PFOS isomers had average half-lives ranging from 1.05 to 1.26 y for different isomers. PFOA, PFHxS, and linear PFOS isomers showed average half-lives of 1.77, 2.87, and 2.93 y, respectively. DISCUSSION: A general pattern of increasing half-lives with increasing chain length was observed. Branched PFOS isomers had shorter half-lives than linear PFOS isomers.
We report the results of the first intensive survey of polychlorinated biphenyls (PCBs) in the surficial sediment of the Indiana Harbor and Ship Canal (IHSC) in East Chicago, Indiana, a part of the Calumet River tributary of Lake Michigan that will be dredged to maintain depth for ship traffic. The tributary has previously been reported to be a large source of PCBs to Lake Michigan. PCB congeners were measured using tandem mass spectrometry in multiple reaction monitoring mode, a method that provides a high level selectivity and sensitivity for PCBs in complex environmental samples. The PCB concentrations (sum of 163 congeners or coeluting peaks) range from 53 to 35,000 ng g−1 d.w. and are comparable to other PCB concentrations at contaminated tributaries in the United States, most of them (although not IHSC) established by law as Superfund sites. The PCB congener signal strongly resembles the original technical mixture Aroclor 1248 that has experienced a small amount of weathering — less than 2.5% by mass for the statistically different congeners - consistent with desorption, volatilization, and microbial dechlorination. The origin of the PCBs in IHSC is not known but Aroclor 1248 was used in hydraulic fluids, vacuum pumps, plasticizers and adhesives. Possible uses of this mixture in East Chicago included the equipment and auxiliary services for the adjacent steel mill and gas refinery and/or lubrication for the drawbridges spanning the canal.
Humans are exposed to different mixtures of PCBs depending on the route of exposure. In this study we investigated the potential contribution of inhalation to the overall human exposure to PCBs in an urban area. For this purpose, the mechanistically based, non-steady state bioaccumulation model ACC-HUMAN was applied to predict the PCB body burden in an adult living in the Midwestern United States who eats a typical North American diet and inhales air contaminated with PCBs. Dietary exposure was estimated using measured data for eighteen PCB congeners in different food groups (fish, meat and egg, dairy products). Two scenarios for inhalation exposure were evaluated: one using air concentrations measured in Chicago, and a second using air measurements in a remote area on Lake Michigan, Sleeping Bear Dunes. The model predicted that exposure via inhalation increases the accumulated mass of PCBs in the body by up to thirty percent for lower chlorinated congeners, while diet is by far the dominant source of exposure for those PCB congeners that accumulate most in humans.
A pressurized liquid extraction-based method for the simultaneous extraction and in situ clean-up of polychlorinated biphenyls (PCBs), hydroxylated (OH)-PCBs and methylsulfonyl (MeSO2)-PCBs from small (< 0.5 gram) tissue samples was developed and validated. Extraction of a laboratory reference material with hexane:dichloromethane:methanol (48:43:9, v/v) and Florisil as fat retainer allowed an efficient recovery of PCBs (78–112%; RSD: 13–37%), OH-PCBs (46±2%; RSD: 4%) and MeSO2-PCBs (89±21%; RSD: 24%). Comparable results were obtained with an established analysis method for PCBs, OH-PCBs and MeSO2-PCBs.
Several nonsymmetric polychlorinated biphenyl (PCB) congeners form atropisomers due to steric hindrance of free rotation around the phenyl-phenyl bond. It is evident from the literature that both chiral PCB congeners and their atropisomeric methylsulfonyl-PCB metabolites, formed in higher animals and in humans, are present in biota as nonracemic mixtures. Chiral methylsulfonyl-PCBs are strongly dominated by one of the atropisomers in mammalian tissues. The aim of the present study is to examine enantioselective metabolism, retention, and excretion of 2,2',3,3',4,6'-hexachlorobiphenyl (CB-132) in rat by administration of a CB-132 racemate and pure atropisomers. Chemical analysis of liver, lung, and adipose tissue from the rats showed a strong retention of one of the CB-132 atropisomers and a similar, but even more pronounced, accumulation of one of the atropisomers of the meta- and para-methylsulfonyl-substituted CB-132 metabolites in these tissues. Metabolites with R structures were predominately formed from one of the atropisomers of CB-132. The slower metabolism of the other atropisomer of CB-132 and its pronounced excretion in feces suggest an enantioselective metabolism. The results indicate enantio-selective formation of the methylsulfonyl-CB132 metabolites and confirm the critical role of stereochemistry of chemicals for their metabolism.
Hormonally-sensitive tissues, like the prostate, ovary and breast, increasingly studied as targets of environmental chemicals, are sources of an enzyme potentially capable of transforming and activating xenobiotics to highly reactive metabolites. Our study specifically addresses the question of whether prostaglandin H synthase (PGHS) can activate phenolic metabolites of polychlorinated biphenyls (PCBs). We found that human recombinant PGHS-2 catalyzed the oxidation of ortho (2′, 3′-, 3′,4′-) and para (2′,5′-) dihydroxy 4-chlorobiphenyl metabolites to their corresponding quinones. These were trapped in situ with N-acetyl cysteine and the reaction products were isolated and characterized by liquid chromatography coupled mass spectrometry and 1 H and heteronuclear ( 1 H-13 C) nuclear magnetic resonance spectroscopy. Both mono-and di-N-acetyl cysteine Michael addition adducts were identified, with the 2′,3′-, and 2′,5′-dihydroxy metabolites predominantly forming mono-N-acetyl cysteine adducts, while the 3′,4′-dihydroxy predominantly formed disubstituted N-acetyl cysteine adducts. These studies clearly demonstrate that the phenolic metabolites of these environmental pollutants are activated by PGHS, as co-substrates, to highly reactive electrophilic PCB quinones, with a potential for protein and DNA damage, especially in non-hepatic tissues where the enzyme is found.
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