暴露于全氟辛烷磺酸(PFAS)化学品会诱发肝脏脂肪变性中脂质代谢关键限速步骤的性别改变

IF 3.6 Q2 TOXICOLOGY
Archana Hari, M. AbdulHameed, Michele R Balik-Meisner, D. Mav, Dhiral P. Phadke, Elizabeth H. Scholl, Ruchir R. Shah, Warren Casey, Scott S. Auerbach, Anders Wallqvist, Venkat R. Pannala
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引用次数: 0

摘要

长期以来,具有在人类和动物体内生物累积潜力的有毒物质一直备受关注,特别是因为它们与多种疾病和器官损伤有关。全氟和多氟烷基物质(PFAS)以及多环芳烃(PAH)就是这样两类会进行生物累积并与肝脏脂肪变性有关的化学品。尽管 PFAS 和 PAH 已被列为受关注的化学品,但它们的毒性分子机制仍有待详细探索。在本研究中,我们旨在确定急性暴露于 PFAS 和 PAH 化学物质可诱发脂质积累的潜在机制,以及这种反应是否取决于化学类别、剂量和性别。为此,我们分析了从化学品与分子启动事件(MIE)结合开始的机制以及随之而来的转录组变化。我们利用之前开发的 ToxProfiler 工具和已发表的脂肪变性不良后果途径的预测结果,整理了潜在的 MIEs。大多数 MIEs 都是转录因子,我们通过挖掘 TRRUST 数据库收集了它们的靶基因。为了分析 PFAS 和 PAH 对脂肪变性机制的影响,我们对暴露于 PFAS 或 PAH 的雄性和雌性大鼠肝组织的高通量转录组测量结果进行了计算 MIE-靶基因分析。结果表明,过氧化物酶体增殖激活受体(PPAR)-α靶标基因的调控最为紊乱,大部分基因都出现了上调。此外,暴露于 PFAS 会干扰多个脂质代谢基因,包括脂肪酸氧化基因(Acadm、Acox1、Cpt2、Cyp4a1-3)的上调和脂质转运基因(Apoa1、Apoa5、Pltp)的下调。我们还发现了多个具有性别特异性的基因。值得注意的是,与雌性大鼠相比,雄性大鼠葡萄糖生成的限速基因(Pck1)和胆汁酸合成的限速基因(Cyp7a1)出现了特异性下调,而脂质合成的限速基因(Scd)则出现了 PFAS 特异性上调。结果表明,PPAR 信号通路在 PFAS 诱导的大鼠脂质积累中发挥了重要作用。总之,这些结果表明,接触 PFAS 会诱导一种性别特异性多因素机制,涉及葡萄糖生成和胆汁酸合成的限速基因,可能会导致脂肪变性不良后果途径的激活。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Exposure to PFAS chemicals induces sex-dependent alterations in key rate-limiting steps of lipid metabolism in liver steatosis
Toxicants with the potential to bioaccumulate in humans and animals have long been a cause for concern, particularly due to their association with multiple diseases and organ injuries. Per- and polyfluoro alkyl substances (PFAS) and polycyclic aromatic hydrocarbons (PAH) are two such classes of chemicals that bioaccumulate and have been associated with steatosis in the liver. Although PFAS and PAH are classified as chemicals of concern, their molecular mechanisms of toxicity remain to be explored in detail. In this study, we aimed to identify potential mechanisms by which an acute exposure to PFAS and PAH chemicals can induce lipid accumulation and whether the responses depend on chemical class, dose, and sex. To this end, we analyzed mechanisms beginning with the binding of the chemical to a molecular initiating event (MIE) and the consequent transcriptomic alterations. We collated potential MIEs using predictions from our previously developed ToxProfiler tool and from published steatosis adverse outcome pathways. Most of the MIEs are transcription factors, and we collected their target genes by mining the TRRUST database. To analyze the effects of PFAS and PAH on the steatosis mechanisms, we performed a computational MIE-target gene analysis on high-throughput transcriptomic measurements of liver tissue from male and female rats exposed to either a PFAS or PAH. The results showed peroxisome proliferator-activated receptor (PPAR)-α targets to be the most dysregulated, with most of the genes being upregulated. Furthermore, PFAS exposure disrupted several lipid metabolism genes, including upregulation of fatty acid oxidation genes (Acadm, Acox1, Cpt2, Cyp4a1-3) and downregulation of lipid transport genes (Apoa1, Apoa5, Pltp). We also identified multiple genes with sex-specific behavior. Notably, the rate-limiting genes of gluconeogenesis (Pck1) and bile acid synthesis (Cyp7a1) were specifically downregulated in male rats compared to female rats, while the rate-limiting gene of lipid synthesis (Scd) showed a PFAS-specific upregulation. The results suggest that the PPAR signaling pathway plays a major role in PFAS-induced lipid accumulation in rats. Together, these results show that PFAS exposure induces a sex-specific multi-factorial mechanism involving rate-limiting genes of gluconeogenesis and bile acid synthesis that could lead to activation of an adverse outcome pathway for steatosis.
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