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The dose- and time-dependent effects of perfluorooctanoic acid on rat liver

ABSTRACT: We reported the hepatic gene expression profiling in male Sprague-Dawley rats treated by different concentrations of perfluorooctanoic acid (PFOA) for 7, 14, and 28 days. We confirmed that PFOA induced liver tumor formation was mainly through the activation of peroxisome proliferator-activated receptor α (PPARα). We identified a panel of 7 genes (Cyp4a1, Nr1d1, Acot2, Vnn, Ehhadh, and Acot1) that might serve as the biomarkers for PPARα activation. We also meausred the apical endpoints of PPARα activation and found a good correlation with the expression level of these biomarker genes. Consitituitive androstane receptor mediated Cyp2b enzymatic activity and gene expression was also upregulated by PFOA in a dose-response manner. On the other hand, acyl hydrocarbon receptor (AhR) target gene Cyp1a2 were significantly downregulated at all time points studied. To our surprise, results of KEGG and Reactome pathway analyses suggested that PFOA did not drive the cell cycles and proliferations in the liver. While some of the DNA replication genes such as Pold2 and Mcm8 were upregulated by PFOA treatment, several key cyclin-dependent cell growth genes, including Ccnd1, Ccne2, Ccnb1, and Ccna2 were all significantly downregulated by PFOA in a dose-dependent manner, especailly at 28 days. Ingenuity Pathway Analysis also indicated that PFOA led to a suppression of liver cancer related pathways at later time points studied. These results suggest that while PFOA clearly induced PPARα activation, the increased cell growth (the second key event in the tumor mode of action), was transient and tightly regulated by feedback mechanisms. Whether such changes will eventually cause the formation of preneoplastic foci and liver tumors in rats remains unclear.

ORGANISM(S): Rattus norvegicus

PROVIDER: GSE125762 | GEO | 2020/01/31

REPOSITORIES: GEO

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Project description:Perfluorooctane sulfonate (PFOS) is a perfluoroalkyl acid (PFAA) and a persistent environmental contaminant found in the tissues of humans and wildlife. Although blood levels of PFOS have begun to decline, health concerns remain because of the long half-life of PFOS in humans. Like other PFAAs, such as perfluorooctanoic acid (PFOA), PFOS is an activator of peroxisome proliferator-activated receptor-alpha (PPARα) and exhibits hepatocarcinogenic potential in rodents. PFOS is also a developmental toxicant in rodents where, unlike PFOA, it’s mode of action is independent of PPARα. Wild-type (WT) and PPARα-null (Null) mice were dosed with 0, 3, or 10 mg/kg/day PFOS for 7 days. Animals were euthanized, livers weighed, and liver samples collected for histology and preparation of total RNA. Gene profiling was conducted using Affymetrix 430_2 microarrays. In WT mice, PFOS induced changes that were characteristic of PPARα transactivation including regulation of genes associated with lipid metabolism, peroxisome biogenesis, proteasome activation, and inflammation. PPARα-independent changes were indicated in both WT and Null mice by altered expression of genes related to lipid metabolism, inflammation, and xenobiotic metabolism. Such results are similar to prior studies done with PFOA and are consistent with modest activation of the constitutive androstane receptor (CAR) and possibly PPARγ and/or PPARβ/δ. Unique treatment-related effects were also found in Null mice including altered expression of genes associated with ribosome biogenesis, oxidative phosphorylation and cholesterol biosynthesis. Of interest was up-regulation of Cyp7a1, a gene which is under the control of various transcription regulators. Hence, in addition to its ability to modestly activate PPARα, PFOS induces a variety of “off-target” effects as well. PPARalpha-null and wild-type male mice at 6-9 months of age were dosed by gavage for 7 consecutive days with either 0, 3, or 10 mg/kg PFOS (potassium salt) in 0.5% Tween 20. Five biological replicates consisting of individual animals were included in each dosage group. Data were compared to results previously published by our group for PFOA and Wy-14,643, a commonly used agonist of PPARalpha (Rosen et al., Toxicol Pathol. 36:592-607, 2008; GSE9796)

Project description:Perfluorooctanoic acid (PFOA) is one of the most used perfluorinated compounds in numerous applications and can be detected in environmental samples from around the globe. The aquatic environment is an important site for PFOA deposit. Nevertheless, the exact mode of action and its resulting toxicological effects on aquatic organisms remain largely unknown. To gain a more extensive understanding of the mode of action of teleost PFOA toxicity, transcriptomics, proteomics, biochemical parameters and reproduction were integrated in the present study. Male and female zebrafish were exposed to nominal concentrations of 0.1; 0.5 and 1 mg/l PFOA for 4 and 28 days resulting in an accumulation which was higher in males compared to females. These gender-related differences were likely caused by different elimination rates due to distinct hormone levels and differences in transport activity by solute carriers. The general mode of action of PFOA was believed to be an increase of the mitochondrial membrane permeability which caused effects on the electron transport system at the biochemical level and resulted in alterations of the oxidative phosphorylation, oxidative stress and apoptosis at the gene transcript and protein level. As a consequence, evidence for the replacement of the affected cells and organelles to sustain tissue homeostasis was found at the molecular level. The higher energy demand, due to these adverse effects, was provided by lowering the glycogen stores. Despite this increase in metabolic expenditure, no effects on reproduction were found indicating that the fish seemed to cope with exposure to the tested concentrations of PFOA. Adult zebrafish (Danio rerio) were exposed to nominal concentrations of 0mg/l; 0.1mg/l; 1mg/l PFOA (perfluorooctanoic acid) for 28 days. Three different 25 litre aquaria per exposure concentration were used resulting in 3 biological replicates with each aquarium containing 8 male and 8 female zebrafish. The livers of 6 male fish and 6 female fish were pooled separately and snap frozen in liquid nitrogen. A reference sample was made by pooling equal amounts of RNA from all samples. A carriage wheel design was used in which all samples were connected to the reference sample and the main contrasts of interest were made directly on the same microarrays as frequently as possible. This design resulted in technical triplicates of each sample.