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Short-chain chlorinated paraffins (SCCPs) are known to disturb thyroid hormone (TH) homeostasis in rodents. However, the mechanism remains to be fully characterized. In this study, male Sprague Dawley rats received SCCPs (0, 1, 10, or 100mg/kg/day) via gavage once a day for consecutive 28days. Plasma and hepatic TH concentrations, thyrocyte structure, as well as thyroid and hepatic mRNA and protein levels of genes associated with TH homeostasis were examined. Moreover, we performed molecular docking to predict interactions between constitutive androstane receptor (CAR), a key regulator in xenobiotic-induced TH metabolism, with different SCCP molecules. Exposure to SCCPs significantly decreased the circulating free thyroxine (T 4 ) and triiodothyronine (T 3 ) levels, but increased thyroid-stimulating hormone (TSH) levels by a feedback mechanism. Decreased hepatic T 4 and increased hepatic T 3 levels were also seen after 100mg/kg/day SCCPs exposure. SCCPs didn't show any significant effects on the expression of thyroid TH synthesis genes or thyrocyte structure. However, stimulation effects were observed for mRNA and protein levels of hepatic uridine diphosphoglucuronosyl transferase (UGT) 1A1 and organic anion transporter 2, suggesting an accelerated TH metabolism in rat liver. The increased cytochrome P450 2B1 but not 1A1 mRNA and protein levels indicated that the CAR signaling was activated by SCCPs exposure. According to docking analysis, SCCPs form hydrophobic interactions with CAR and the binding affinity shows dependency on chlorine content. Overall, our data showed that CAR implicated enhancement of hepatic TH influx and degradation could be the main cause for SCCPs induced TH deficiency in male rats., (Copyright © 2017 Elsevier B.V. All rights reserved.)

Short-chain chlorinated paraffins (SCCPs) are ubiquitous in the environment and might cause adverse environmental and human health effects. Little is known about the relative toxicity of different SCCP compounds especially during development. The objective of this study was to characterize and compare effects of seven SCCP groups at environmentally relevant levels, using a zebrafish (Danio rerio) model. Observations on malformation, survival rates at 96 h post fertilization (hpf), and hatching rates at 72 hpf indicated that the C 10- groups (C 10 H 18 Cl 4 , 1,2,5,6,9,10-C 10 H 16 Cl 6 and C 10 H 15 Cl 7 ) were more toxic than the C 12- groups (C 12 H 22 Cl 4 , C 12 H 19 Cl 7 and 1,1,1,3,10,12,12,12-C 12 H 18 Cl 8 ) and Cereclor 63L. The C 10- groups were also more potent than C 12- groups and Cereclor 63L in decreasing thyroid hormone levels. Among the three compounds within the C 10- group, the compounds with less chlorine content had stronger effects on sub-lethal malformations but less effects on triiodothyronine (T3) and tetraiodothyronine (T4). Only C 10 H 18 Cl 4 significantly decreased the mRNA expression of tyr, ttr, dio2 and dio3 at a dose-dependent manner suggesting that the specific mode of actions differ with different congeners. The mechanisms of disruption of thyroid status by different SCCPs could be different. C 10 H 18 Cl 4 might inhibit T3 production through the inhibition effect on dio2. These results indicate that SCCP exposure could alter gene expression in the hypothalamic-pituitary-thyroid (HPT) axis and thyroid hormone levels. The mechanisms of disruption of thyroid status by different SCCPs could be different. Our results on the relative developmental toxicities of SCCPs will be useful to reach a better understanding of SCCP toxicity supporting environmental risk evaluation and regulation and used as a guidance for environmental monitoring of SCCPs in the future., (Copyright © 2016 Elsevier Ltd. All rights reserved.)

The effects of the polybrominated diphenyl ether (PBDE) congener 2,2'4, 4'-tetrabromodiphenylether (DE-47), and technical preparations of polychlorinated biphenyls (PCBs; Aroclor 1254) and chlorinated paraffins (CPs; Witaclor 171P) on thyroid hormone (TH) levels were examined in rats. To study possible interactive effects, also combinations of the three compounds were used. Thus, female Sprague-Dawley rats, 7 weeks old, were treated with approximately isomolar doses (ca. 30 micromol/kg bw per day) of DE-47 (6.0 mg/kg per day), Aroclor 1254 (4.0 mg/kg per day) and Witaclor 171P (6.8 mg/kg per day), alone or in combinations, daily for 14 days by gastric intubation. DE-47 was also administered in a higher (18 mg/kg per day) and lower (1.0 mg/kg per day) dose. In order to test possible mechanisms behind the TH effects, microsomal enzyme (cytochrome P-450 isozymes and uridine diphosphoglucuronyl transferase-UDPGT) activity (indicating both metabolic activation and/or biliary clearance), ex vivo-binding of 125I-T4 to plasma proteins (suggesting effects on peripheral TH transport) and light microscope morphology of the thyroid gland were studied. The observed degree of TH reduction after Aroclor 1254 and DE-47 exposure corresponded with a decrease in the ex vivo binding of 125I-T4 to the plasma TH-transporter transthyretin (TTR), and with induction of the microsomal phase I enzymes (ethoxy- and methoxy-resorufin dealkylases, EROD and MROD). The phase II enzyme UDPGT was also elevated, but only moderately. The thyroid morphology showed an activation of the epithelia, but no degenerative alternations, that was correlated to exposure to Aroclor 1254. In our model, the observed effects match the hypothesis that the T4 decrease is chiefly due to disturbances in serum transport, caused by binding of in vivo-formed Aroclor 1254 and DE-47 metabolites to TTR. However, decreased plasma TH levels due to increased glucuronidation activity may also be of some importance. The thyroid gland hyperactivity is probably a feed-back consequence of the T4 decrease, in spite of the lack of TSH alterations. In the mixed DE-47 and Witaclor 171P group synergistic effects were indicated on free T4 (FT4) and EROD induction levels, results that may suggest that such effects should be considered in risk assessment of mixtures of persistent organohalogens.

Juvenile rainbow trout (Oncorhynchus mykiss) were exposed to high dietary concentrations of six polychlorinated n-alkane (PCAs) (C(10)H(15.5)C(6.5), C(10)H(15.3)Cl(6.7),C(11)H(18.4)Cl(5.6),C(12)H(19.5)Cl(6.5),C(14)H(24.9)Cl(5.1) and C(14)H(23.3)Cl(6.7)) for 21 to assess their effects on behavior and liver and thyroid histology and for 85 days to assess histology for a longer term exposure. This is the first histological work using PCAs of known carbon chain length and chlorine content and the first effort to examine the histopathology of fish exposed to PCAs. PCAs, also known as chlorinated paraffins, are complex industrial products for which there is a lack of toxicological data on individual congeners. With the exception of trout exposed to C(14)H(24.9)Cl(5.1), which had much lower exposure concentrations, many of the trout exposed to the PCAs (whole fish concentrations 0.22-5.5 microg g(-1)) showed a diminished or no startle response, loss of equilibrium, and developed a dark coloration. These responses are indicative of a narcotic toxicological mode-of-action. Histopathological lesions were observed in the livers of trout from each exposure group. However, the most severe histopathologies were observed in the livers of fish exposed to C(10)H(15.3)Cl(6.7) and C(11)H(18.4)Cl(5.6) (whole fish concentrations 0.92 and 5.5 microg g(-1), respectively), in which extensive fibrous lesions were present that were not observed in any other exposure group. Other alterations observed in all treatment groups included hepatocyte necrosis, sites of inflammation, and glycogen/lipid depletion. The relative sizes of hepatocytes of PCA exposed trout were smaller than control trout, although only a few of the observed differences were statistically significant. No lesions were present in the thyroid, although trout exposed to C(10)H(15.5)Cl(6.5) (whole fish concentration 0.84 microg g(-1)) had slightly more active thyroids, as indicated by an increased mean thyroid epithelium cell height relative to controls. It would appear that PCA toxicity is inversely related to carbon chain length, as has been observed in similar studies using mammals. The concentrations in the fish from this experiment were at levels that have been reported in invertebrates and fish from contaminated sites in the Great Lakes. However, the exposure concentrations were likely much greater in these experiments compared with the environment and require further study.