Chemosphere

Obesity is increasing worldwide, particularly in rural communities, where people are likely exposed to high levels of pesticides. We here investigated whether six commonly used agricultural pesticides on corn and soy fields have adipogenic activity and act as obesogens. Exposure to two pesticides, the herbicides acetochlor and metolachlor, induced adipogenesis in vitro in mouse 3T3-L1 preadipocytes. The most potent compound, acetochlor, was selected for further studies in zebrafish. Acetochlor exposure caused morphological malformations and lethality in zebrafish larvae with an EC50 of 7.8 {micro}M and an LC50 of 12 {micro}M. Acetochlor exposure also resulted in lipid accumulation is zebrafish larvae when simultaneously fed a high cholesterol diet. To decipher the molecular mechanisms behind acetochlor action, we preformed transcriptomic and targeted lipidomic analysis of exposed animals. The combined omics results suggested that acetochlor exposure increased Nrf2 activity in response to reactive oxygen species, as well as induced lipid peroxidation and ferroptosis. We further discovered that acetochlor structurally shares a chloroacetamide group with known inhibitors of glutathione peroxidase 4 (GPX4). Computational docking analysis suggested that acetochlor covalently binds to the active site of GPX4. Consequently, Gpx4 activity was efficiently repressed by acetochlor, and lipid peroxidation was increased in zebrafish. We propose that acetochlor disrupts lipid homeostasis by inhibiting Gpx4, resulting in accumulation of lipid peroxidation, 4-hydroxynonenal, and reactive oxygen species in the cells, which in turn activate Nrf2. Because metolachlor, among other acetanilide herbicides, also contain the chloroacetamide group, inhibition of Gpx4 activity may represent a novel, common molecular initiating event of obesogens. SynopsisRural populations have a high prevalence of metabolic disease and are highly exposed to pesticides. This study reports that the herbicide acetochlor, heavily used on soy and corn fields, inhibits an enzyme that protects from oxidation of lipids in the cell membrane, oxidative stress and a type of cell death called ferroptosis, features that are linked to metabolic disruption and obesity.

The use of efficient screening strategies for the hazard assessment of chemicals is a current challenge to support regulatory requirements. Herein, we combined two eleuthero-embryo assays, a refined Fish Embryo Toxicity assay (OECD TG 236) and the EASZY assay (OECD TG 250), both using transgenic (tg) (cyp19a1b:GFP). The simultaneous performance of both assays provides complementary information about the acute toxicity, developmental effects, and estrogenic activity. A refined EASZY assay is however necessary to obtain accurate EC50. In this work we compared bisphenol A (BPA) and ten of its substitutes. In the refined FET, most of the selected bisphenols were more toxic than BPA, induced developmental effects on zebrafish embryos, some being identified as teratogenic compounds (BPF, BPS-MAE, BPC Cl, 4,4ODP), and ten of them induced GFP intensity. Endocrine activity of the BPs was further investigated in the EASZY assay at concentrations that do not affect the survival and the hatching rates or induce developmental toxicity based on the target concentrations used as previously defined in the refined FET. All bisphenols elicited an estrogenic activity with the notable exception of TCBPA. Most BPs were more estrogenic than BPA, acted as agonist ligands of zfER{beta}2 as shown in zebrafish-specific in vitro reporter gene assay and functional zfERs were required to induce brain aromatase. Interestingly, BPS-MAE and BPS-MPE behave as pro-estrogens as they were unable to transactivate zebrafish ER{beta}2 in vitro but induced brain aromatase in vivo. Overall, the implementation of the zebrafish eleuthero embryo-based screening strategy efficiently provided relevant data contributing to their environmental hazard. It also provides further evidence that bisphenols modulate cyp19a1b expression during early brain development whom potential short and long-term adverse effects need to be addressed. SYNOPSISa zebrafish eleuthero embryo-screening strategy based on OECD TGs was implemented for an efficient hazard assessment of bisphenols revealing that most of them are more toxic and/or estrogenic than BPA

Human health effects from chronic exposure to mixtures of pesticide residues are little investigated. We compared standard histopathology and serum biochemistry measures and multi-omics analyses in an in vivo subchronic toxicity test of a mixture of six pesticide active ingredients frequently detected in foodstuffs (azoxystrobin, boscalid, chlorpyrifos, glyphosate, imidacloprid and thiabendazole). Sprague-Dawley rats were administered with the pesticide mixture with each ingredient at its regulatory permitted acceptable daily intake. Analysis of water and feed consumption, body weight, histopathology and serum biochemistry showed little or no physiological effects from exposure to the pesticide mixture. In marked contrast, analysis of the host-gut microbiome axis using serum and caecum metabolomics revealed that nicotinamide and tryptophan metabolism were affected, which suggested the initiation of a cell danger response, including adaptation to oxidative stress. Only limited effects were detected on the caecum microbiota by shotgun metagenomics. Further analyses of in vitro bacterial cultures showed that growth of Lactobacillus rhamnosus and Escherichia coli strains was negatively impacted by the pesticide mixture at concentrations that were not inhibitory when exposure was to a single agent. Transcriptomics of the liver showed that 257 genes had their expression changed. Gene functions affected included those involved in the regulation of response to hormones and correlated with previously reported transcriptome changes following administration of nicotinamide. Genome-wide DNA methylation analysis of the same liver samples showed that 4255 CpG sites were differentially methylated (> 10% difference). Overall, we demonstrated that unlike standard blood biochemical and organ histological analysis, in-depth molecular profiling using a combination of high-throughput -omics methods in laboratory animals exposed to low concentrations of pesticides reveals metabolic effects on the gut-liver axis, which can potentially be used as biomarkers for the prediction of future negative health outcomes. Our data suggest that adoption of multi-omics as part of regulatory risk assessment procedures will result in more accurate outcome measures, with positive public health implications.

Pollution of aquatic environments poses an increasingly severe threat to ecosystems worldwide, and understanding its molecular consequences for aquatic organisms requires extensive research and the development of advanced analytical tools. Phosphoproteomics can be particularly valuable for this purpose, as shifts in phosphorylation states can serve as early molecular indicators of toxic exposure. The cladoceran Daphnia is a keystone species in aquatic ecosystems, linking lower and higher trophic levels, and is therefore widely used as a model organism in ecotoxicology to study biological consequences of pollution. Here, we present a simple and effective strategy to analyse the phosphoproteome of Daphnia magna, a commonly used Daphnia species in ecotoxicology. Following TiO2-based phosphopeptide enrichment and LC-MS/MS analysis, we identified a comprehensive dataset of 3,532 phosphorylation sites across 1,329 phosphoproteins. These proteins were especially involved in signaling pathways and cellular structure and the vast majority have not yet been demonstrated in other Daphnia species. In conclusion, our results demonstrate that a straightforward phosphoproteomic LC-MS/MS workflow in D. magna can serve as a powerful tool for investigating adverse molecular effects caused by anthropogenic pollution, such as microplastics or pharmaceuticals. Statement of significanceThe dataset presented here demonstrates the feasibility of a simple yet effective strategy to perform phosphoprotemics in Daphnia magna, and it will be particularly valuable for future ecotoxicoproteomics research using this model organism.

Environmental exposure to polycyclic aromatic hydrocarbons (PAHs) causes metabolic dysfunction, but reliable biomarkers are still needed to assess human health effects. This study used 21-day matured human HepG2 spheroids, a metabolically competent three-dimensional (3D) liver model, to assess metabolic responses to graded, non-cytotoxic concentrations of benzo[a]pyrene (BaP) and benzo[b]fluoranthene (BBF) after 24- and 96-h exposure. Untargeted liquid chromatography-mass spectrometry (LC-MS) metabolomics, combined with multivariate and network analyses, identified compound- and time-specific metabolic signatures. At 24 hours, no metabolites showed significant changes. In contrast, at 96 hours, both PAHs consistently altered seven robust metabolites linked to polyamine metabolism, membrane dynamics, mitochondrial energy, and DNA-repair pathways. Network analysis showed BBF caused broader and more connected changes than BaP, indicating distinct toxicodynamics. These findings underscore the importance of extended exposure in revealing metabolic disruption and support a set of candidate biomarkers for future low-dose studies and improved risk assessment of airborne toxicants.

The regulation of appetite is of growing interest due to the significant rise in global obesity rates. Hunger and satiety are controlled by two hormones with functional activity in the brain; leptin, which is produced in adipocytes and suppresses food intake, and ghrelin, which is produced and released mainly by the stomach and functions as an appetite-stimulatory signal. In this study, zebrafish-based in vivo assays were used to examine whether BPA and five of its analogues, BPAF, BPE, BPC, BPC-CL, and BPS affect appetite regulation. The effect of bisphenol exposure on eating behavior was first examined. Four to six days old zebrafish larvae were exposed to a concentration range of the bisphenols and 17{beta}-estradiol, followed by being fed a stained egg yolk powder at day six. After an hour of feeding, the feed in the gut was imaged by microscopy. Quantitative PCR was used to analyze the gene expression of leptin and ghrelin, as well as eleven other genes involved in appetite control. Exposures to BPA, BPAF, BPE, BPC, BPC-Cl and BPS, resulted in increased amounts of feed in the gut of the larvae in a concentration dependent manner. The qPCR results suggested that leptin mRNA expression was downregulated with the increasing concentrations of BPA, BPAF and BPC-Cl, whereas ghrelin mRNA expression was upregulated. The expression of several additional anorexigenic genes were downregulated by BPAF and BPC-Cl exposure, whereas orexigenic genes were upregulated. In conclusion, bisphenol exposures resulted in an increased eating behavior in zebrafish larvae, which correlated to increased mRNA expression of appetite-stimulatory genes and decreased expression of satiety-inducing genes. In addition, the results suggest that zebrafish larvae can be used to efficiently assess obesogenic capacity of environmental pollutants.

Understanding the biological impact of chemicals is hindered by the high number and diversity of compounds in the market. To simplify the chemical risk assessment, the adverse outcome pathway (AOP) method has arisen as a framework to predict the impact of chemical exposure on human and environmental health. The development of this predictive tool requires knowledge of the molecular interaction between chemicals and protein targets. Those molecular initiating events connect alterations of cellular function with physiological impairment. This strategy aims to focus on the complex biological interaction to predict the impact on health. The high-throughput identification of all chemical targets can be obtained by a proteomics-based thermal shift assay, however, selecting the priority target candidate is a biased process strongly dependent on expert knowledge and literature. Here, we unravel new molecular initiating event from a tested chemical combining the target deconvolution by the proteome integral solubility alteration (PISA) assay, and the target selection by an analytical hierarchy process (AHP) approach. In the proof-of-concept study, we identified by PISA assay 8 protein targets for 2,3,7,8 tetrachlorodibenzo-p-dioxin (TCDD) from the soluble proteome from hepatic cells containing 2824 proteins. The definition of the AHP approach facilitates the selection of heat shock protein beta-1 (Hspb1) as the most suitable protein for developing AOPs. Our results demonstrated that the process of target identification is independent from a chemical characterization, and that the process of data curation and target selection is less sensitive to lack of toxicological information. We anticipate that this innovative integration of methods could decipher the chemical-protein interactions from new chemicals including the new alternative chemicals designed for chemical replacement and that would discover new molecular initiating events to support more sustainable methodologies to gain time and resources in chemicals assessment. SYNOPSISOur combined methodologies can determine the most suitable target to develop adverse outcome pathways from the proteome-wide protein target identification.

Chronic exposure to pesticide mixtures through diet is common, yet their combined metabolic effects and interactions with dietary factors remain unclear. We identified four pesticides prevalent in human exposure (imazalil, thiabendazole, boscalid, lambda-cyhalothrin) and assessed their combined impacts on hepatic metabolism and metabolic homeostasis using human liver cells and male mice fed standard chow or western diets. We found that the pesticide mixture induced metabolic perturbations in human hepatocytes. In addition, the pesticide mixture altered hepatic gene expression in chow-fed mice and exacerbated western diet-induced glucose intolerance, fasting hyperglycemia, and insulin resistance without affecting body weight or liver steatosis. These findings reveal that dietary context influences the metabolic consequences of pesticide mixtures, highlighting the need to consider nutritional status when evaluating environmental contaminant risks. Our results suggest that pesticide mixtures at reference doses may contribute to metabolic dysregulation, particularly under obesogenic dietary conditions. Highlights- Four common pesticides in mixture disrupt metabolism in liver cells - Dietary exposure to this pesticide mixture alters hepatic gene expression in mice - The pesticide mixture exacerbates WD-induced disruptions in glucose homeostasis - Pesticides and diet interact in producing the metabolic effects of a pesticide mixture

The grouping of chemicals based on shared properties or molecular mechanisms of action is pivotal for advancing regulatory toxicology, reducing data gaps, and enabling cumulative risk assessments. This study introduces a novel framework usingChemical-Gene-Phenotype-Disease (CGPD) tetramers derived from the Comparative Toxicogenomics Database (CTDbase). Our approach integrates toxicogenomics data to identify and cluster chemicals with similar molecular and phenotypic effects across diverse categories, including pesticides, pharmaceuticals, and industrial chemicals such as bisphenols and per- and poly-fluoroalkyl substances (PFAS). We validated our method by comparing CGPD Tetramer-based clusters with cumulative assessment groups (CAGs) for pesticides, demonstrating strong overlap with established groupings while identifying additional compounds relevant for risk assessment. Key examples include clusters associated with endocrine disruption and metabolic disorders.By bridging omics-derived molecular data with phenotypic and disease endpoints, this framework provides a comprehensive tool for chemical grouping and supports evidence-based regulatory decision-making, facilitating the transition to next-generation risk assessment methodologies.

The regulatory assessment of endocrine disrupting chemicals (EDCs) is complex due to the lack of a standardized definition of EDCs and validated testing criteria. In spite of these challenges, there is growing scientific interest in EDCs which has resulted in the rapid expansion of published literature on endocrine disruption upon chemical exposure. Here, we explore how academic research leading to curated knowledgebases can inform current chemical regulations on EDCs. To this end, we present an updated knowledgebase, DEDuCT 2.0, containing 792 potential EDCs with supporting evidence from 2218 research articles. Thereafter, we study the distribution of potential EDCs across several chemical lists that reflect guidelines for use or regulations. Further, to understand the scale of possible exposure to the potential EDCs present in chemical lists, we compare them with high production volume chemicals. Notably, we find many potential EDCs are in use across various product categories such as Food additives and Food contact materials and Cosmetics and household products. Several of these EDCs are also produced or manufactured in high volume across the world. Lastly, we illustrate using an example how diverse information in curated knowledgebases such as DEDuCT 2.0 can be helpful in the risk assessment of EDCs. In sum, we highlight the need to bridge the gap between academic and regulatory aspects of chemical safety, as a step towards the better management of environment and health hazards such as EDCs.

This study presents a comprehensive analysis of the effects of perfluorooctane sulfonate (PFOS) exposure on zebrafish embryos, focusing on the differential responses between wild-type (WT) and oatp1d1 mutant embryos. The findings improve our understanding of the toxicokinetic and toxicodynamic mechanisms of PFOS, a persistent and bioaccumulative member of the per- and polyfluoroalkyl substances (PFAS) family. The study revealed significant differences in mortality rates with calculated LC50 values of 23.57 {micro}M for WT and 16.71 {micro}M for oatp1d1 mutants, indicating a higher susceptibility of the mutants to PFOS toxicity. This indicates the crucial role of the Oatp1d1 transporter in mediating the toxic effects of PFOS, possibly related to detoxification processes or regulation of bioavailability. Developmental abnormalities, particularly in the swim bladder, were more pronounced in mutant embryos, indicating the role of the transporter in mitigating PFOS-induced developmental toxicity. Gene expression analysis showed differential modulation of biotransformation genes, including cytochrome P450 (cyp) and glutathione S-transferase (gst) genes, underscoring the complexity of PFOS toxicity. The study also highlighted disruptions in lipid metabolism with altered expression of genes involved in lipid synthesis and oxidation, leading to abnormal lipid accumulation. These findings have significant implications for aquatic ecosystems and human health, as PFOS is persistent and bioaccumulative in the environment. The study emphasizes the need for stringent regulatory measures and effective remediation strategies to address PFOS contamination and protect both aquatic life and human populations.

Understanding the nature of co-formulants and toxic effects of major glyphosate-based herbicide (GBH) formulations is considered a research priority. Indeed, the toxicity of the co-formulants present in GBHs have been widely discussed and the European Union recently banned the co-formulant polyoxyethylene tallow amine (POEA). We provide a foundation for the development of new environmental epidemiological studies by reporting the presence of the most commonly used POEA, known as POE-15 tallow amine, in the widely used US GBH RangerPro. In order to understand if POE-15 tallow amine is present in RangerPro at a concentration at which it can exert toxic effects, we also tested the cytotoxicity of this GBH compared to glyphosate and POE-15 tallow amine in the human epithelial cell line Caco-2, a representative of the human intestinal epithelium, and the first to be exposed from the human diet to glyphosate herbicides. The lethal concentration 50 for each of these substances was 125 g/ml, 17200 g/ml, and 5.7 g/ml, for RangerPro, glyphosate and POE-15, respectively. The Caco-2 cell cytotoxicity assay indicated that RangerPro is more cytotoxic than glyphosate, suggesting that its toxicity can be due to the presence of the POE-15 surfactant. RangerPro and POE-15 tallow amine but not glyphosate exerted cell necrotic effects, but did not induce oxidative stress. We show that RangerPro contains POE-15 tallow amine at a concentration at which it could exert toxic effects, which offers a starting point for conducting surveys of co-formulant exposure in human populations.

BackgroundAryl phosphate esters (APEs), a main class of organophosphorus ester molecules, are widely used and commonly present in the environment. Health hazards associated with these compounds remain largely unknown and the effects of diphenyl phosphate (DPhP), one of their most frequent derivatives in human samples, are poorly characterised. ObjectiveOur aim was to investigate whether DPhP per se may represent a more relevant marker of exposure to APEs and determine its potential deleterious biological effects in chronically exposed mice. MethodsConventional animals (FVB mice) were acutely (intravenous or oral gavage) or chronically (0.1 mg.mL-1, 1 mg.mL-1, 10 mg.mL-1 in drink water) exposed to relevant doses of DPhP or triphenyl phosphate (TPhP), one of its main precursors in the environment. Both molecules were measured in blood and other relevant tissues by liquid chromatography-mass spectrometry (LC-MS). Biological effects of chronic DPhP exposure were addressed through liver multi-omics analysis combining mRNA extraction and sequencing to high resolution LC-MS to determine the corresponding metabolic profile. Deep statistical exploration was performed to extract correlated information, guiding further physiological analyses (immunohistochemistry (IHC) and animal growth measurement). ResultsAcute and chronic exposure to DPhP led to significant levels of this molecule in blood and other tissues, an effect missing with TPhP. Multi-omics analysis confirmed the existence of biological effects of DPhP, even at a very low dose of 0.1 mg.mL-1 in drinking water. Chemical structural homology and pathway mapping demonstrated a clear reduction of the fatty-acid catabolic processes centred on acylcarnitine and mitochondrial {beta}-oxidation. Interestingly, mRNA expression confirmed and extended these observations by demonstrating at all tested doses the overall repression of genes involved in lipid catabolic processes and regulated by PPAR, a master regulator of {beta}-oxidation and its associated ketogenesis. IHC analysis confirmed the alteration of these pathways by showing a specific downregulation of Hmgcs2, a kernel target gene of PPAR, at all doses tested, and surprisingly, a strong reduction of the lipid droplet content only at the highest dose. Overall, DPhP absorption led to weight loss, which was significant using the highest dose. ConclusionsOur results suggest that in mice, the effects of chronic exposure to DPhP, even at a low dose, are not negligible. Fatty acid metabolism in the liver in particular is essential for controlling fast and feast periods with adverse consequences on the overall physiology. Therefore, the impact of DPhP on circulating fat, cardiovascular and metabolic disease incidence deserves, in light of our results, further investigations.

There has been limited research into arsenolipid toxicological risks and health-related outcomes due to challenges with their separation, identification, and quantification within complex biological matrices (e.g., fish, seaweed). Analytical approaches for arsenolipid identification such as suspect screening have not been well documented and there are no certified standard reference materials, leading to issues with reproducibility and uncertainty regarding the accuracy of results. In this study, a detailed workflow for the identification of arsenolipids utilizing suspect screening coupled with data independent analysis is presented and applied to three commercially available standard reference materials (Hijiki seaweed, dogfish liver, and tuna). Hexane and dichloromethane/methanol extraction, followed by reversed-phase high-performance liquid chromatography-inductively coupled plasma mass spectrometry and liquid chromatography-electrospray ionization-quadrupole time-of-flight mass spectrometry. Using the workflow developed, mass fragmentation matching, mass error calculations, and retention time matching were performed to identify suspect arsenolipids. Arseno-fatty acids (AsFAs), arsenohydrocarbons (AsHCs), and arsenosugar phospholipids (AsSugPLs) were identified with high confidence; AsHC332, AsHC360, and AsSugPL720 in seaweed, AsHC332 in tuna, and AsFA474 and AsFA502 in the dogfish liver. AsHC332, AsHC360, and AsFA502 were identified as promising candidates for further work on synthesis, quantification using MS/MS, and toxicity testing.

Organisms ingest microplastics directly from environments and indirectly from food sources. Ingesting microplastics can lead to an organism accumulating plastic-derived chemicals. However, the relative contributions of the two exposure routes (direct ingestion vs. indirect ingestion) to plastic-derived chemical accumulation in an organism are unknown. Using microplastics containing different types of plastic additives, we performed exposure experiments to compare chemical accumulation patterns in fish (Myoxocephalus brandti) between the exposure from the water and prey (Neomysis spp.). We found significantly higher brominated flame retardant concentrations in fish fed microplastic-contaminated prey than fish exposed to microplastics suspended in the water. The results indicate that prey-mediated ingestion of microplastics can be a more significant route for organisms accumulating plastic-derived chemicals, suggesting that organisms at higher trophic levels are more exposed to microplastics and associated chemicals than organisms at lower trophic levels.

Of the cytochrome P450 enzymes, CYP3A4 is the most abundant isoform in the human liver, and this enzyme plays a dominant role in the metabolism of a wide range of clinical drugs and xenobiotics. Previous studies have demonstrated that CYP3A4 participates in the oxidative metabolism of several organophosphorus (OP) pesticides involving both thion (P=S) and oxon (P=O) forms. In the present study, we evaluated the capacity of CYP3A4 to metabolize a structurally diverse set of OP compounds using LC-MS/MS methods and assessed their potential to inhibit CYP3A4 activity using previously developed pFlour50 fluorogenic assay. Our results demonstrate that CYP3A4 preferentially metabolizes thions, as compared to oxons, and several OP compounds were also found to inhibit CYP3A4 activity in a time-dependent manner. To gain further mechanistic structural insight into the CYP3A4-OP interactions, molecular docking studies were performed using a crystal structure of CYP3A4 (PDB ID: 3NXU). Linear correlation analysis between in silico parameters like molecular weight or binding energy correlated with experimental data including inhibition data for 10 or 30 minutes or the LC-MS/MS data showing the degradation at 1 or 2 hours showed moderate but significant correlation. Soman surrogate PiMP, and cyclosarin surrogate CMP, were both effectively metabolized by CYP3A4, while docking of these surrogates and authentic agents with CYP3A4 receptor revealed very similar binding poses and interactions. Collectively, these findings highlight the important role of CYP3A4 in OP metabolism and support the potential of integrating experimental and in silico data to predict CYP3A4-mediated metabolism of existing and emerging OP compounds, including those of toxicological and chemical warfare relevance.

Per- and polyfluoroalkyl substances (PFAS) are globally recognised as emerging contaminants of concern due to their persistence, toxicity, endocrine-disrupting and immunosuppressive effects. Because of their extensive industrial use, PFAS are now widespread across ecosystems and accumulate in marine environments. Despite their ubiquity, the extent and drivers of PFAS contamination remain poorly characterised, particularly in marine systems. Odontocetes (toothed whales) are effective bioindicators of marine pollution, integrating contamination across regions, time, and trophic levels. Here, we present the first global assessment of factors influencing PFAS contamination in marine ecosystems by analysing standardised PFAS concentrations of PFNA, PFDA, PFUnDA, PFDoDA and PFOS reported for 713 liver samples across 33 odontocete species spanning 13 countries from 2000 to 2023. Using generalised linear mixed models, we evaluated the effects of genus, location, sex, life stage, and sampling year on PFAS concentrations, combining published datasets with new samples from Australia. Genus and location were the strongest predictors, suggesting that interspecific ecological and physiological traits likely contribute to PFAS accumulation. Concentrations were highest in males and younger individuals, consistent with maternal offloading and possible age-related dilution. Spatio-temporal trends indicate that PFAS contamination is widespread and increasing globally, with highest concentrations reported in the Pacific. This study provides a critical baseline for understanding global PFAS exposure in marine mammals, which underscores the need for coordinated monitoring and further research to address regional data gaps and potential unrecognised biological effects. HighlightsO_LIHigh genus-specific and spatial differences in PFAS contamination across odontocetes globally. C_LIO_LIIncreased contamination in younger/smaller individuals. C_LIO_LISex-specific trends, including higher PFAS levels in male odontocetes. C_LIO_LISpatio-temporal trends suggesting increased PFAS concentration despite global regulatory efforts, with highest concentrations in the Pacific Ocean. C_LI

Per-and polyfluoroalkyl substances (PFAS) are ubiquitous environmental contaminants that have been associated with adverse health effects in highly exposed populations. Manufacturers have taken steps to replace toxic long-chain perfluoroalkyl acids (PFAAs) with short-chain PFAAs and perfluoroether acids (PFEAs). There is little to no toxicity data for many of these chemicals. Most of the data that are available are taken from studies that do not account for the pH of highly concentrated PFAS solutions, resulting in highly acidic conditions that do not accurately reflect real-world exposures. The goal of this study was to evaluate the lethality and developmental toxicity of 17 structurally diverse PFAS in zebrafish in a pH-neutral environment. We then compared results to determine the impacts of chain length, head group, and ether linkages on toxicity. The potency of PFAS to induce mortality and developmental toxicity endpoints increased with chain length, and sulfonic acids were more potent than carboxylic acids. The inclusion of ether oxygens was associated with reduced potency relative to PFAAs with equal chain length and head group. Perfluorooctane sulfonic acid (PFOS) was the most potent compound, followed by perfluoroundecanoic acid (PFUnDA) and perfluorododecanoic acid (PFDoDA). Short-chain compounds perfluoro-2-methoxyacetic acid (PFMOAA) and perfluorobutanoic acid (PFBA) were the least potent. These data were used to construct a multiple linear regression model for PFAS potency. Failed swim bladder inflation was the most sensitive developmental toxicity endpoint for all assessed chemicals. Other common phenotypes included spinal curvature, edema, craniofacial malformations, and ocular malformations. Ocular malformations were more common in response to sulfonic acids. No other phenotypes exhibited significant structural specificity. Our study provides new toxicity data for a diverse set of PFAS under environmentally relevant conditions. Future studies should be expanded to include more branched structures and head groups not present in our testing set to allow for improved understanding of how other structural features impact toxicity.

The ubiquitously occurring food contaminants altenuene (ALT) and tentoxin (TEN) are recognized as emerging Alternaria mycotoxins, yet substantial data gaps remain when it comes to their toxicological behavior and toxicokinetic characteristics. This study aimed to compare and generate quantitative data on their hepatic metabolism and to obtain semi-quantitative insights into their metabolite profiles. To this end, primary rat and human hepatocytes were incubated with 10 {micro}M ALT or TEN over multiple time points up to 4 h. Both substrate depletion and metabolite identification revealed pronounced interspecies differences. The extent of ALT metabolism was significant, with an 88% and 57% decrease in rat and human hepatocytes after 4 h, respectively. In contrast, TEN showed extensive biotransformation in rats (67%) but only modest turnover in humans (27%) over the same period. Hepatocellular clearances were consistently higher for ALT than TEN, with hepatic extraction ratios indicating intermediate extraction for ALT and low extraction for TEN. High-resolution mass spectrometry combined with targeted analysis of selected metabolites annotated phase II conjugation as the predominant metabolic pathway for ALT and phase I oxidative metabolism for TEN, including mono- and double-metabolized species for the latter. Overall, these results provide a comprehensive characterization of ALT- and TEN-metabolism in hepatocytes, offering a foundation for future studies on their toxicological relevance and impact on human health.

Per- and polyfluoroalkyl substances (PFAS) are a class of emerging contaminants that are widely distributed and persistent in the environment, accumulated in biological organisms and associated with adverse health outcomes. Evidence has shown a wide existence of branched PFAS isomers from source to applications. Notably, linear and branched isomeric PFAS structures are associated with differential toxicity outcomes and health effects. Herein, we investigated distribution of perfluorooctane sulfonate (PFOS) isomers in mouse liver tissue after exposure using matrix-assisted laser desorption/ionization-trapped ion mobility spectrometry-mass spectrometry imaging (MALDI-TIMS-MSI). Mice were treated with vehicle control or commercially sourced PFOS, a mixture of linear and branched isomers, at concentrations to achieve doses of 0.1 and 1 mg/kg/day for 84 days. Liver tissues were collected, followed by sample preparation and MALDI-TIMS-MSI analysis. Using a TIMS ramp time of 150 ms, we successfully separated linear and branched isomers on-tissue. Coupling with post-MALDI immunofluorescence imaging of canonical zonation markers, we discovered hepatic zonation-specific distribution for linear isomer but more homogenous distribution of branched PFOS. Dual-polarity MSI was performed on the same tissue for hepatic metabolites and lipids, and results showed concomitant alteration of liver lipid zonation upon PFOS exposure. With MALDI-TIMS-MSI, our results for the first time demonstrated on-tissue differentiation of PFOS isomers. Multi-modal imaging revealed isomer-specific PFOS distribution and spatial lipidomic changes, both mapped to canonical hepatic zonation markers, to reveal zone-selective PFOS toxicokinetics/toxicodynamics. Together our results demonstrate the critical need for further investigating isomer-specific PFAS toxicity.