Dataset Information

Population specific and shared transcriptional responses of fish embryos exposed to PCB153

ABSTRACT: Killifish (Fundulus heteroclitus) inhabiting the New Bedford Harbor (NBH) Superfund Site have evolved resistance to the toxic and biochemical effects of non-ortho (dioxin-like) polychlorinated biphenyls (DL-PCBs) and other compounds that act via the aryl hydrocarbon receptor (AHR) signaling pathway. However, the majority of PCBs in NBH are ortho-substituted (non-DL) PCBs (o-PCBs), and the impacts of these o-PCBs on fish populations are not well understood. To determine whether the NBH killifish population has adapted to o-PCBs, we performed a series of experiments involving exposure to killifish embryos and adults from NBH and a reference site (Scorton Creek; SC) to 2,2’,4,4’,5,5’-hexachlorobiphenyl (PCB-153), a model o-PCB. PCB-153 was not acutely embryotoxic to developing F2 killifish embryos (SC or NBH) at concentrations up to 28 µM. RNA-seq showed that SC embryos exposed to PCB-153 (28 µM for 6 hr at 10 days post fertilization) had changes in the expression of genes involved in glucose homeostasis. However, NBH embryos were much less sensitive to these effects of PCB-153. When adult killifish from SC and NBH were exposed to PCB-153 (20 mg/kg) and sampled 3 days later for gene expression, many more genes were affected in forebrains of SC fish than in NBH fish, in a sex-specific manner. Together, these results demonstrate that NBH killifish have evolved reduced sensitivity to o-PCBs, suggesting complex adaptation to chemical mixtures at a Superfund site.

ORGANISM(S): Fundulus heteroclitus

PROVIDER: GSE115863 | GEO | 2018/06/16

REPOSITORIES: GEO

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Project description:Hypoxia in coastal waters is an increasing concern, with the frequency of hypoxic events rising because of climate change and human-driven impacts such as eutrophication. The Atlantic killifish (Fundulus heteroclitus), an estuarine species known for its resilience to environmental stressors, provides a valuable model to investigate the physiological, transcriptional, and epigenetic mechanisms underlying adaptation. Some killifish populations, like those in New Bedford Harbor (NBH), Massachusetts, have evolved resistance to dioxin-like polychlorinated biphenyls (PCBs) due to chronic exposure. These populations offer a unique opportunity to investigate how toxicant resistance might influence responses to secondary stressors like hypoxia. The objective of this study is to characterize the impacts of evolved resistance to toxicants on the ability to cope with acute hypoxia. We compared hepatic gene expression and DNA methylation patterns in response to two levels of hypoxia in killifish from NBH and Scorton Creek (SC), a reference population from a relatively pristine environment. We hypothesized that NBH fish would exhibit altered molecular responses to hypoxia due to trade-offs associated with toxicant resistance. Our results revealed significant differences between the two populations. SC fish demonstrated a dose-dependent increase in gene expression in response to hypoxia, while NBH fish exhibited a muted transcriptional response to severe hypoxia, indicating potential impairment in their ability to cope with hypoxic stress. Interestingly, NBH fish showed significant DNA methylation changes in response to hypoxia, while SC fish did not exhibit notable epigenetic alterations. These findings suggest that toxicant-adapted killifish may face trade-offs in their response to additional environmental stressors, with potential consequences for their ability to survive in increasingly hypoxic coastal habitats. Further research is needed to elucidate the functional implications of these epigenetic modifications and their role in adaptive stress responses.

Project description:This study presents statistical analyses of gene expression in 5, 10 and 15 day post-fertilization (dpf) embryos of the teleost Fundulus heteroclitus treated with control vehicle (DMSO) or a potent non-ortho-PCB (PCB-126; 3,3’,4,4’,5-pentachlorobiphenyl). The embryos were from two populations: a clean, reference population (SC, Scorton Creek, MA USA) and a polluted Superfund population (N, New Bedford Harbor, MA USA). For each site, eggs from 8 females (~1100 total) were fertilized using minced testes from 5 males. After non-fertile eggs were culled, embryos were exposed to vehicle (DMSO; 0.1%) or PCB-126 (50 nM) in filtered seawater (salinity 25 part per thousand, 65 embros per 20 ml in glass petri dish) for 4 hr at 20º C. After exposure, the embryos were washed in filtered seawater and incubated at 20º C under a 14-h light, 10-h dark cycle. At 5-, 10-, and 15-dpf, embryos were collected as three pools of 20 embryos from each treatment group and flash frozen in liquid nitrogen and stored at -80º C until used for RNA isolation. A loop design was used for the microarray hybridizations where each sample is hybridized to 2 arrays using both Cy3 and Cy5 labeled fluorophores. We used three loops in which each loop consisted of Cy3- and Cy5-labeled embryo aRNAs from 12 samples: one sample from each population-treatment-time combination. Within a population-treatment-time, embryos were randomly assigned to one of the three loops. In total, 36 embryos were hybridized to 36 microarrays. The loops formed were SC5C→ SC5P → NBH5C→ NBH5P →SC10C→ SC10P→ NBH10C→ NBH10P → SC15C→ SC15P → NBH15C → NBH15P → SC5C, where each arrow represents a separate hybridization (array) with the biological sample at the base of the arrow labeled with Cy3 and the biological sample at the head of the arrow labeled with Cy5. SC represents the Scorton Creek, Sandwich, MA population (reference), NBH represents the New Bedford Harbor, MA population, C represents control dose (DMSO), P represents the PCB-126 dose, 5 represents 5 dpf, 10 represents 10 dpf and 15 represents 15 dpf.

Project description:Polychlorinated biphenyls (PCBs) are persistent and ubiquitously distributed environmental pollutants. Based on their chemical structure, PCBs are classified into non-ortho substituted and ortho-substituted congeners. Non-ortho-substituted PCBs are structurally similar to dioxin or TCDD (2,3,7,8-tetrachlorodibenzo-p-dioxin) and their mode of action and toxic effects are well established. In contrast, much less is known about the effects of ortho-substituted PCBs. Studies conducted so far have focused on tissue-specific effects but there is limited knowledge about the effects on the whole organism, particularly the sensitive developmental stages in vertebrates. Hence, in this study we investigated the effects of exposure to an environmentally relevant ortho-substituted PCB (2,2’,4,4’,5,5’-hexachlorobiphenyl; PCB153) on zebrafish embryos. We exposed zebrafish embryos to either DMSO (0.1%; solvent control) or three different concentrations of PCB153 (0.1, 1 and 10 μM) from 4 hours post-fertilization (hpf) to 120 hpf. At the end of the exposure, larvae were sampled for determining transcriptional changes (RNA sequencing) and the remaining embryos were maintained in contaminant-free environment. At 7 and 14 days post-fertilization (dpf), zebrafish larvae were assessed for locomotory behavior. We did not observe any overt phenotypes during the exposure period, but observed a spinal phenotype in the 10μM PCB153 treated group starting at 7 dpf. This phenotype was observed in a dose-dependent manner and majority of the embryos with this phenotype died by 14 dpf. RNA sequencing of 5 dpf larvae exposed to PCB153 also revealed dose-dependent changes in gene expression patterns. A total of 633, 2227, and 3378 differentially expressed genes were observed in 0.1, 1 and 10 μM PCB153 treated embryos, respectively. Among these, 301 genes were common to all treatment groups, and KEGG pathway analysis revealed enrichment of genes related to circadian rhythm, FOXO signaling and insulin resistance pathways. We are currently investigating the functions of genes that are uniquely altered by different PCB153 concentrations. Overall, these results suggest that developmental exposure to PCB153, a PCB congener highly prevalent in the environment, targets multiple physiological processes including photoperiod regulation and metabolism. [Funded by NIH P01ES021923 and NSF OCE-1314642].