Abstract

Mercury is a heavy metal toxicant that is prevalent throughout the environment. Organic forms of mercury, such as methylmercury (MeHg), can cross the placenta and can lead to lasting detrimental effects in the fetus. The toxicological effects of MeHg on the placenta itself have not been clearly defined. Therefore, the purpose of the current study was to assess the transport of MeHg into placental syncytiotrophoblasts and to characterize the mechanisms by which MeHg exerts its toxic effects. Cultured placental syncytiotrophoblasts (BeWo) were used for these studies. The transport of radioactive MeHg was measured to identify potential mechanisms involved in the uptake of this compound. The toxicological effects of MeHg on BeWo cells were determined by assessing visible pathological change, autophagy, mitochondrial viability, and oxidative stress. The findings of this study suggest that MeHg compounds are transported into BeWo cells primarily by sodium-independent amino acid carriers and organic anion transporters. The MeHg altered mitochondrial function and viability, decreased mitophagy and autophagy, and increased oxidative stress. Exposure to higher concentrations of MeHg inhibited the ability of cells to protect against MeHg-induced injury. The findings show that MeHg is directly toxic to syncytiotrophoblasts and may lead to disruptions in the fetal/maternal transfer of nutrients and wastes.

Highlights

  • Mercury (Hg) is a naturally occurring heavy metal that is ubiquitous in the environment

  • While some Hg enters the environment from natural sources, a large fraction of environmental Hg is anthropogenic, i.e., the result of human activity

  • While this study provided some important information about the effects of MeHg on placental cells, we suggest that exposure to MeHg leads to additional, undocumented, toxicological effects in syncytiotrophoblasts

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Summary

Introduction

Mercury (Hg) is a naturally occurring heavy metal that is ubiquitous in the environment. While some Hg enters the environment from natural sources, a large fraction of environmental Hg is anthropogenic, i.e., the result of human activity. Coal-fired power plants and small-scale artisanal gold mining are major sources of environmental Hg. Approximately 80% of anthropogenic Hg is released into the air and subsequently deposits in soil and bodies of water. Microorganisms in soil and water methylate mercuric ions to form methylmercury (MeHg). MeHg bioaccumulates and biomagnifies within aquatic species, which leads to high levels of MeHg in the muscle tissue of large, predatory fish

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