Regular ArticleIncreased (3H) Phorbol Ester Binding in Rat Cerebellar Granule Cells by Polychlorinated Biphenyl Mixtures and Congeners: Structure-Activity Relationships
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Predicted versus observed activity of PCB mixtures toward the ryanodine receptor
2024, NeuroToxicologyNeurochemical effects of halogenated organic compounds: Possible adverse outcome pathways and structure–activity relationships
2023, Advances in NeurotoxicologyUnintentionally produced polychlorinated biphenyls in pigments: An updated review on their formation, emission sources, contamination status, and toxic effects
2021, Science of the Total EnvironmentCitation Excerpt :Potentially toxic effects of some typical pd-PCBs and their metabolites have been demonstrated by several in vivo and in vitro studies conducted over the last three decades (Table 6). CB-11, 4-OH-CB-11, and 4′-OH-CB-35 can exhibit neurotoxicity in human and rat cell lines via different pathways such as decreasing cell dopamine content (Shain et al., 1991), inducing reactive oxygen species (ROS) production (Brown et al., 1998; Dreiem et al., 2009; Zhu et al., 2013), perturbing protein kinase C (PKC) translocation (Kodavanti et al., 1995), and promoting dendritic growth (Sethi et al., 2018). CB-11 and its hydroxylated and sulfated metabolites and CB-35 have been found as agonists/antagonists of androgen, estrogen, and thyroid hormone receptors (Flor et al., 2016; Takeuchi et al., 2017; Pencikova et al., 2018; Ren et al., 2019; Sethi et al., 2019).
Integrating data gap filling techniques: A case study predicting TEFs for neurotoxicity TEQs to facilitate the hazard assessment of polychlorinated biphenyls
2019, Regulatory Toxicology and PharmacologyCitation Excerpt :The correlation coefficient between the individual experiments with the alternative NEF values derived in this work and NEF values derived by Simon et al. (2007) were very similar, with an exception to Kodavanti PEB (Kodavanti et al., 1996b), Pessah/Holland RyR1 (Pessah et al., 2006; Holland et al., 2017), Stenberg Dop (Stenberg et al., 2011) and Stenberg DAT (Stenberg et al., 2011) which correlated better with the alternative NEF values. The correlation coefficients derived by Simon et al. (2007) and NEF values from this work are: (0.50, 0.66) for protein kinase C translocation effect (Kodavanti et al., 1995), (0.73, 0.76) for reduction in dopamine content effect (Shain et al., 1991), (0.72, 0.69) and (0.82, 0.84) for microsomal and mitochondrial Ca+2-sequestration effect, respectively (Kodavanti et al., 1996a), (0.40, 0.70) for enhanced RyR1 activity (Pessah et al., 2006), inhibition of dopamine uptake (0.52, 0.85 - Stenberg Dop (Stenberg et al., 2011); 0.57, 0.69 – Stenberg DAT (Stenberg et al., 2011); 0.58, 0.49 – Wigestrand DAT (Wigestrand et al., 2013)). Overall, we derived alternative NEF values for 87 congeners that were used to develop QSAR models (Table 2).
Cell Signaling and Neurotoxicity
2018, Comprehensive Toxicology: Third EditionNeuroendocrine actions of organohalogens: Thyroid hormones, arginine vasopressin, and neuroplasticity
2010, Frontiers in NeuroendocrinologyCitation Excerpt :Based on the structure–activity relationships (SAR), Chauhan et al. [27] proposed two binding modes, one for lateral substituted PCBs and the other for ortho-substituted PCBs by overlaying the PCB molecule on T4 (Fig. 4). The binding potencies of several PCBs seem to follow their biological activities such as decreases in PC12-cellular dopamine content and PKC translocation in neuronal cells [27,127,130,224] with some exceptions where differential effects of PCBs on circulating TH are observed based on coplanarity. PCB congeners that are non-coplanar such as 2,2′,4,4′,5,5′-hexachlorobiphenyl (PCB153) decrease circulating T4 levels to a greater extent (>90%) than coplanar PCBs such as 3,3′,4,4′,5-pentachlorobiphenyl (PCB 126) [37].