Juvenile Male Rats Exposed to a Low-Dose Mixture of Twenty-Seven Environmental Chemicals Display Adverse Health Effects.

Humans are exposed to a large number of environmental chemicals in their daily life, many of which are readily detectable in blood or urine. It remains uncertain if these chemicals can cause adverse health effects when present together at low doses. In this study we have tested whether a mixture of 27 chemicals administered orally to juvenile male rats for three months could leave a pathophysiological footprint. The mixture contained metals, perfluorinated compounds, PCB, dioxins, pesticides, heterocyclic amines, phthalate, PAHs and others, with a combined dose of 0.16 (Low dose), 0.47 (Mid dose) or 1.6 (High dose) mg/kg bw/day. The lowest dose was designed with the aim of obtaining plasma or urine concentrations in rats at levels approaching those observed in humans. Some single congeners were administered at doses representative of combined doses for chemical groups. With this baseline, we found effects on weight, histology and gene expression in the liver, as well as changes to the blood plasma metabolome in all exposure groups, including low-dose. Additional adverse effects were observed in the higher dosed groups, including enlarged kidneys and alterations to the metabolome. No significant effects on reproductive parameters were observed.

Endocrine-disrupting chemicals, risk of type 2 diabetes, and diabetes-related metabolic traits: A systematic review and meta-analysis.

BACKGROUND: Elevated blood or urinary concentrations of endocrine-disrupting chemicals (EDCs) may be related to increased risk of type 2 diabetes (T2D). The aim of the present study was to assess the role of EDCs in affecting risk of T2D and related metabolic traits. METHODS: MEDLINE was searched for cross-sectional and prospective studies published before 8 March 2014 into the association between EDCs (dioxin, polychlorinated biphenyl [PCB], chlorinated pesticide, bisphenol A [BPA], phthalate) and T2D and related metabolic traits. Three investigators independently extracted information on study design, participant characteristics, EDC types and concentrations, and association measures. RESULTS: Forty-one cross-sectional and eight prospective studies from ethnically diverse populations were included in the analysis. Serum concentrations of dioxins, PCBs, and chlorinated pesticides were significantly associated with T2D risk; comparing the highest to lowest concentration category, the pooled relative risks (RR) were 1.91 (95% confidence interval [CI] 1.44-2.54) for dioxins, 2.39 (95% CI 1.86-3.08) for total PCBs, and 2.30 (95% CI 1.81-2.93) for chlorinated pesticides. Urinary concentrations of BPA and phthalates were also associated with T2D risk; comparing the highest to lowest concentration categories, the pooled RR were 1.45 (95% CI 1.13-1.87) for BPA and 1.48 (95% CI 0.98-2.25) for phthalates. Further, EDC concentrations were associated with indicators of impaired fasting glucose and insulin resistance. CONCLUSIONS: Persistent and non-persistent EDCs may affect the risk of T2D. There is an urgent need for further investigation of EDCs, especially non-persistent ones, and T2D risk in large prospective studies.

Surveillance program for former PCB-exposed workers of a transformer and capacitor recycling company, family members, employees of surrounding companies, and area residents--executive summary.

In a German company polychlorinated biphenyls (PCB)-containing transformers and capacitors were recycled on a large scale. Human biomonitoring revealed a high PCB body burden in workers of the recycling company, in surrounding locations of this plant, in companies in the neighborhood of this plant, and in family members of these employees. In order to clarify whether possible adverse health effects occurred or may occur in the future, a prospective surveillance program was initiated. After an extensive literature search, an interdisciplinary group of experts developed a surveillance program based on current knowledge with respect to possible adverse health effects that might occur in the recycling process of transformers and capacitors. Exposure to various hazardous substances (PCB, polychlorinated dibenzo-p-dioxins and dibenzo-furans [PCDD/F], metals, solvents) was considered. Criteria derived from human biomonitoring results of PCB were used for admission to the program. Participants in the surveillance program are first informed about risks and aims of the program. Subsequently, physicians started a detailed documentation of participants' general and occupational history, with their complaints, diseases, and nutritional habits, as well as information regarding their living areas, by means of a standardized questionnaire. In addition, separate examinations were performed to detect possible neurological, immunological, (neuro)psychological, hormonal, and skin effects. Moreover, DNA exposure as assessed by the comet assay and antioxidative status were determined. The program will be offered at yearly intervals for 3 years, and then at 5 and 10 years after program onset. Until now the program has proved to be feasible, and acceptance among workers and their families has been high. Based on the results, criteria will be developed to define adverse health effects that might be attributable to a hazardous substance exposure.

Multiple species metabolism of PHA-568487, a selective alpha 7 nicotinic acetylcholine receptor agonist.

The quinuclidine PHA-0568487(1) is an agonist of the alpha 7 nicotinic acetylcholine receptor that was designed to mitigate the bioactivation associated with the core scaffold and subsequently remove associated liabilities with in vivo tolerability. The drug metabolites of 1 in nonclinical species were identified in plasma and urine of rats, dogs and monkeys receiving oral administrations of 1. The in vitro biotransformation of 1 was subsequently investigated in multiple species employing cryopreserved hepatocytes, hepatic subcellular fractions and recombinantly-expressed human P450 enzymes. In addition, in vitro metabolism of synthetically prepared metabolite precursors were instrumental in the elucidation of several secondary metabolites. The results indicated that the principal biotransformation of 1 was oxidation of the benzo[1,4]dioxane moiety (M8, M10) followed by subsequent oxidation to a range of secondary metabolites (M1-7, M9, M11, M13-15, and M17-18). The carboxylic acids M1 and M2 resulting from the oxidative cleavage of the dioxane ring were the principal metabolites observed in the plasma, urine and hepatocyte incubations across all species (M1 & M2). Quinuclidine oxidation was another pathway of importance, yielding an N-oxide (M12) which was also observed in all species.P450 2D6 and FMO1 catalyze the oxidation of the quinuclidine nitrogen. The N oxidation of the quinuclidine moiety is consistent with previously published accounts of this scaffold's metabolism and, interestingly, may implicate the uncommon quinuclidine moiety as an entity directing the metabolism of this scaffold (e.g., 1) via FMO1 and P450 2D6 oxidation.

Impact of iron and steel industry and waste incinerators on human exposure to dioxins, PCBs, and heavy metals: results of a cross-sectional study in Belgium.

We evaluated the impact of two iron and steel plants and two municipal solid waste incinerators (MSWI) in Wallonia (Belgium) on the exposure of residents to dioxins, polychlorinated biphenyls (PCBs), and heavy metals. In total, 142 volunteers living around these facilities were recruited and compared with 63 referents from a rural area with no industrial source of pollution. Information about smoking habits, dietary habits, anthropometric characteristics, residential history, and health status was obtained from a self-administered questionnaire. The volunteers provided blood under fasting conditions in order to evaluate the body burden of dioxins (17 polychlorinated dibenzo-p-dioxins/dibenzofurans [PCDD/Fs] congeners) and PCBs. Samples of blood and urine were also taken for the determination of cadmium, mercury, and lead. After adjustment for covariates, concentrations of cadmium, mercury, and lead in urine or blood were not increased in subjects living in the vicinity of MSWIs or sinter plants by comparison with referents. Residents around the sinter plants and the MSWI located in the industrial area had concentrations of dioxins and PCBs in serum similar to that of referents. By contrast, subjects living in the vicinity of the MSWI in the rural area showed significantly higher serum levels of dioxins (geometric mean, 38 vs. 24 pg TEQ/g fat) and coplanar PCBs (geometric mean, 10.8 vs. 7.0 pg TEQ/g fat). Although age-adjusted dioxin levels in referents did not vary with local animal fat consumption, concentrations of dioxins in subjects living around the incinerators correlated positively with their intake of local animal fat, with almost a doubling in subjects with the highest fat intake. These results indicate that dioxins and coplanar PCBs emitted by MSWIs can indeed accumulate in the body of residents who regularly consume animal products of local origin.

Negative association between serum dioxin level and oxidative DNA damage markers in municipal waste incinerator workers.

OBJECTIVES: To investigate the effect of dioxin on the formation of oxidative DNA damage and urinary mutagenicity, we measured the concentrations of serum dioxins and lymphocytic 8-hydroxydeoxyguanosine (8-OH-dG) in 57 male waste incinerator workers, urinary 8-OH-dG and urinary mutagenicity in 29 male waste incinerator workers. METHODS: Information about the subjects was obtained from a questionnaire. Concentrations of polychlorinated dibenzo-p-dioxin (PCDD), polychlorinated dibenzofuran (PCDF), and coplanar-polychlorinated-biphenyl (Co-PCB) in serum samples from the workers were measured with a high-resolution gas chromatograph /high-resolution mass spectrometer. Lymphocytic and urinary 8-OH-dG levels were measured with a high-performance liquid chromatography-electrochemical detector system. The urinary mutagenicity was measured with umu assay. RESULTS: The lymphocytic 8-OH-dG level showed a negative association with the serum dioxin level (total value of TEQ-PCDD, PCDF, and Co-PCB). Urinary 8-OH-dG did not show correlation with serum dioxin level, but showed positive correlation with the smoking index. CONCLUSIONS: With respect to the subjects' serum dioxin level, dioxin did not increase the urinary 8-OH-dG level by oxidative DNA damage, but upregulation of the primary defenses with oxidative damage and/or DNA repair system activity might have occurred.

Disposition and excretion of intravenous 2,3,7,8-tetrabromodibenzo-p-dioxin (TBDD) in rats.

Polybrominated dibenzodioxins and dibenzofurans are of toxicologic interest due to potential occupational and environmental exposure and because of their structural similarity to the highly toxic chlorinated analogues. The excretion and terminal tissue distribution of [3H]TBDD was studied in male F344 rats for 56 days following single iv doses of .001 or 0.1 mumol/kg. The major tissue depots of radioactivity were liver, adipose tissue, and skin, and tissue distribution was dose-dependent. At 56 days, liver concentrations in the high dose group were disproportionately increased compared to those of the low dose group. Liver:adipose tissue concentration ratios were 0.2 and 2.6 at the low and high doses, respectively. Elimination of radioactivity in the feces, the major route of excretion, and urine was also nonlinear with respect to dose. By Day 56, feces accounted for approximately 50% of the administered dose at the low dose versus 70% at the high dose. Based on fecal excretion, the apparent terminal whole body half-life was estimated to be 18 days for both dose groups. The time-dependent pattern of tissue disposition was characterized at the low dose over a 56-day period. Blood levels of radioactivity declined rapidly with 2% remaining in the blood by 24 hr. Radioactivity levels in the liver peaked by 7 hr and then gradually declined concomitant with a slow accumulation in adipose tissue. The terminal excretion half-life of radioactivity in adipose tissue was estimated to be 60 days. Liver:adipose tissue concentration ratios declined with time. Thus, the overall disposition of TBDD appears similar to that observed for the chlorinated analogue, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). The results of these studies are consistent with the hypothesis that TBDD, like TCDD, induces a binding species in the liver which accounts for higher liver:adipose tissue concentration ratios at the high dose. The dose-dependent tissue disposition and excretion kinetics of these compounds suggest important considerations for extrapolations from high to low doses.

Fate of 2,3,7,8-tetrachlorodibenzo-p-dioxin metabolites from dogs in rats.

1. Metabolites of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) were extracted from the bile of TCDD-treated dogs and administered by gavage to bile-duct-cannulated rats and also to an intact rat. 2. Radioactivity of the TCDD metabolites was rapidly cleared from the body of the rats, indicating that bioaccumulation of these compounds does not occur. 3. Biliary excretion was the most important route of elimination in the cannulated rats and amounted to greater than 30% of the administered dose within 24h. TCDD metabolites were also eliminated to a minor extent by the kidneys. The combined recovery of radioactivity in faeces, bile and urine after 24h accounted for greater than 85% of the dose. 4. The intact animal exhibited a somewhat different kinetic behaviour in that only 13% dose was excreted in faeces and urine after 24h, which indicates enterohepatic circulation. The administered radioactivity was completely recovered after 72h. 5. Results from the present experiments indicate that metabolism of TCDD is the rate-limiting step in elimination of TCDD from the liver. Interspecies variability in the toxicity of TCDD may in part be attributable to different rates at which the species metabolize and excrete TCDD.

Structural identification of p-dioxane-2-one as the major urinary metabolite of p-dioxane.

Analysis by gas chromatography (GC) of the volatile compounds present in the urine from rats administered dioxane, a hepatic carcinogen to this species, revealed a major metabolite. The appearance of the metabolite was pH-dependent, undetectable at high pH; reacidification of the urine sample brought about the reappearance of the metabolite. The amount excreted was dose-dependent and time-dependent, reaching a maximum between 20 and 28 h after dioxane administration. Diethylene glycol administered to rats gave rise to the same metabolite. When isolated and purified from lyophilized urine by preparative GC, the metabolite exhibited an intense carbonyl band at 1750 cm-1 in the infrared spectrum. Nuclear magnetic resonance spectrum showed two triplets and one singlet with equal intensity at delta 3.85, 4.48 and 4.37, respectively. GC-mass spectrometric studies indicated a parent peak at m/e 102. The metabolite was identified as p-dioxane-2-one. Synthetic reference compound exhibited identical IR, NMR, and GC-mass spectra as the metabolite. The tentative pathway and the biological significance of dioxane metabolism are discussed.