High cytotoxicity of a degraded TBBPA, dibromobisphenol A, through apoptotic and necrosis pathways

Exposure of Bisphenols (BPA, BPB and BPC) in HepG2 Cells Results in Lysosomal Dysfunction and Lipid Accumulation

Nonalcoholic fatty liver disease poses a significant public health concern, as do the issues surrounding plastic usage. The bisphenols are reported to cause fat accumulation in the liver. However, literature is scanty about the effect of bisphenols on lysosomes or lysosomal functions. We predicted the interaction of bisphenols with lysosomal proteins available in the online databases using in silico tools. Molecular docking revealed that chosen Bisphenols interact with critical lysosomal proteins including lipid hydrolyzing enzymes. Following exposure of BPA, BPB and BPC to HepG2 cells fat accumulation and lysosomal functions were evaluated. Exposure to BPB and BPC results intracellular fat accumulation under experimental conditions like BPA. All three Bisphenols disturb lysosomal homeostasis perhaps by different mechanisms. Overall our results suggest that Bisphenols can also cause fat accumulation in liver by disturbing lysosomal homeostasis.

Effects and risk assessment of halogenated bisphenol A derivatives on human follicle stimulating hormone receptor: An interdisciplinary study

Halogenated bisphenol A (BPA) derivatives are produced during disinfection treatment of drinking water or are synthesized as flame retardants (TCBPA or TBBPA). BPA is considered as an endocrine disruptor especially on human follicle-stimulating hormone receptor (FSHR). Using a global experimental approach, we assessed the effect of halogenated BPA derivatives on FSHR activity and estimated the risk of halogenated BPA derivatives to the reproductive health of exposed populations. For the first time, we show that FSHR binds halogenated BPA derivatives, at 10 nM, a concentration lower than those requires to modulate the activity of nuclear receptors and/or steroidogenesis enzymes. Indeed, bioluminescence assays show that FSHR response is lowered up to 42.36 % in the presence of BPA, up to 32.79 % by chlorinated BPA derivatives and up to 27.04 % by brominated BPA derivatives, at non-cytotoxic concentrations and without modification of basal receptor activity. Moreover, molecular docking, molecular dynamics simulations, and site-directed mutagenesis experiments demonstrate that the halogenated BPA derivatives bind the FSHR transmembrane domain reducing the signal transduction efficiency which lowers the cellular cAMP production and in fine disrupts the physiological effect of FSH. The potential reproductive health risk of exposed individuals was estimated by comparing urinary concentrations (through a collection of human biomonitoring data) with the lowest effective concentrations derived from in vitro cell assays. Our results suggest a potentially high concern for the risk of inhibition of the FSHR pathway. This global approach based on FSHR activity could enable the rapid characterization of the toxicity of halogenated BPA derivatives (or other compounds) and assess the associated risk of exposure to these halogenated BPA derivatives.

Distribution, transformation, and toxic effects of the flame retardant tetrabromobisphenol S and its derivatives in the environment: A review

As widely used alternative brominated flame retardants, tetrabromobisphenol S (TBBPS) and its derivatives have attracted increasing amounts of attention in the field of environmental science. Previous studies have shown that TBBPS and its derivatives easily accumulate in environmental media and may cause risks to environmental safety and human health. Therefore, to explore the environmental behaviours of TBBPS and its derivatives, in this paper, we summarized relevant research on the distribution of these compounds in water, the atmosphere, soil and food/biota, as well as their transformation mechanisms (biological and nonbiological) and toxic effects. The summary results show that TBBPS and its derivatives have been detected in water, the atmosphere, soil, and food/biota globally, making them a ubiquitous pollutant. These compounds may be subject to adsorption, photolysis or biological degradation after being released into the environment, which in turn increases their ecological risk. TBBPS and its derivatives can cause a series of toxic effects, such as neurotoxicity, hepatotoxicity, cytotoxicity, thyrotoxicity, genotoxicity and phytotoxicity, to cells or living organisms in in vitro and in vivo exposure. Toxicological studies suggest that TBBPS as an alternative to TBBPA is not entirely environmentally friendly. Finally, we propose future directions for research on TBBPS and its derivatives, including the application of new technologies in studies on the migration, transformation, toxicology and human exposure risk assessment of TBBPS and its derivatives in the environment. This review provides useful information for obtaining a better understanding of the behaviour and potential toxic effects of TBBPS and its derivatives in the environment.

Different effects of TCBPA exposure on liver cancer cells and liver cells: two sides of the coin

Tetrachlorobisphenol A (TCBPA), widely used as a substitute for tetrabromobisphenol A (TBBPA), has been detected in various environmental media. Therefore, a detailed evaluation of the toxicological properties of TCBPA is necessary. In this study, we used hepatoma and normal liver cell models in vitro to investigate the effects of TCBPA. Our findings indicate that TCBPA promotes the proliferation of liver cancer cells, as evidenced by MTT and EdU assays, and enhances the expression levels of molecules related to hepatoma proliferation. Further investigation into the molecular mechanism revealed that TCBPA-induced hepatoma proliferation is regulated by an NLRP3-mediated inflammatory process. Additionally, TCBPA was found to promote the epithelial-mesenchymal transition (EMT) process in liver cancer cells. Conversely, TCBPA inhibited the proliferation of normal liver cells. Mechanistic studies showed that TCBPA induced cell pyroptosis in normal liver cells by evaluating a series of related markers, including NLRP3, IL-1β, ASC, GASDMD, and Caspase 1. In vivo models further showed that TCBPA causes liver tissue damage. In summary, this study demonstrates that TCBPA has a dual effect: promoting the occurrence and development of liver tumor cells in vitro, while inhibiting the proliferation of normal liver cells, like two sides of a coin. These opposite cellular outcomes are regulated by NLRP3-mediated inflammatory processes, providing valuable insights for evaluating the potential health impacts of TCBPA.

Decavanadate-Bearing Guanidine Derivatives Developed as Antimicrobial and Antitumor Species

To obtain biologically active species, a series of decavanadates (Hpbg)4[H2V10O28]·6H2O (1) (Htbg)4[H2V10O28]·6H2O; (2) (Hgnd)2(Hgnu)4[V10O28]; (3) (Hgnu)6[V10O28]·2H2O; and (4) (pbg = 1-phenyl biguanide, tbg = 1-(o-tolyl)biguanide, gnd = guanidine, and gnu = guanylurea) were synthesized and characterized by several spectroscopic techniques (IR, UV-Vis, and EPR) as well as by single crystal X-ray diffraction. Compound (1) crystallizes in space group P-1 while (3) and (4) adopt the same centrosymmetric space group P21/n. The unusual signal identified by EPR spectroscopy was assigned to a charge-transfer π(O)→d(V) process. Both stability in solution and reactivity towards reactive oxygen species (O2- and OH·) were screened through EPR signal modification. All compounds inhibited the development of Escherichia coli, Pseudomonas aeruginosa, Staphylococcus aureus, and Enterococcus faecalis bacterial strains in a planktonic state at a micromolar level, the most active being compound (3). However, the experiments conducted at a minimal inhibitory concentration (MIC) indicated that the compounds do not disrupt the biofilm produced by these bacterial strains. The cytotoxicity assayed against A375 human melanoma cells and BJ human fibroblasts by testing the viability, lactate dehydrogenase, and nitric oxide levels indicated compound (1) as the most active in tumor cells.