RESUMO
Citalopram, a selective serotonin reuptake inhibitor (SSRI), is often detected in aquatic ecosystems. In this investigation, developing zebrafish were continuously exposed to one nominal concentration of either 0, 10, or 1000 µg/L citalopram for 7 days. Ribonucleic acids were then extracted from zebrafish for RNA-sequencing using the NovoSeq 6000 (Illumina). Clean reads were obtained following the removal of both the adapter and poly-N sequences. Alignment and differential gene expression analysis was conducted using programs HISAT2 and StringTie assembler. Data were converted to FPKM to quantify differentially expressed transcripts. Significant clinical subnetworks enriched following citalopram exposure included sympathetic nerve activity, blood pressure, vascular tone, and arterial pressure. Regulated transcripts were related to diseases such as mechanical hyperalgesia, pain, inflammatory pain, obstructive hypertrophic cardiomyopathy, fatigue, Diamond-Blackfan anemia, and hypertrophic cardiomyopathy. Following exposure to 10 µg/L citalopram, several transcripts were linked to brain dysfunction like prostaglandin-endoperoxide synthase 2, microtubule associated protein tau, cathepsin B, and dystrophin. Genes related to cardiac dysfunction were altered in zebrafish following exposure to 1000 µg/L citalopram. Using literature and databases that describe gene interactions, molecular networks (clinical and disease networks) were constructed to understand effects of citalopram.
RESUMO
An over-active renin-angiotensin system (RAS) is characterized by elevated angiotensin II (Ang II). While Ang II can promote metabolic and mitochondrial dysfunction in tissues, little is known about its role in the gastrointestinal system (GI). Here, we treated rat primary colonic epithelial cells with Ang II (1-5000 nM) to better define their role in the GI. We hypothesized that Ang II would negatively affect mitochondrial bioenergetics as these organelles express Ang II receptors. Ang II increased cellular ATP production but reduced the mitochondrial membrane potential (MMP) of colonocytes. However, cells maintained mitochondrial oxidative phosphorylation and glycolysis with treatment, reflecting metabolic compensation with impaired MMP. To determine whether lipid dysregulation was evident, untargeted lipidomics were conducted. A total of 1949 lipids were detected in colonocytes spanning 55 distinct (sub)classes. Ang II (1 nM) altered the abundance of some sphingosines [So(d16:1)], ceramides [Cer-AP(t18:0/24:0)], and phosphatidylcholines [OxPC(16:0_20:5(2O)], while 100 nM Ang II altered some triglycerides and phosphatidylserines [PS(19:0_22:1). Ang II did not alter the relative expression of several enzymes in lipid metabolism; however, the expression of pyruvate dehydrogenase kinase 2 (PDK2) was increased, and PDK2 can be protective against dyslipidemia. This study is the first to investigate the role of Ang II in colonic epithelial cell metabolism.
Assuntos
Angiotensina II , Colo , Células Epiteliais , Metabolismo dos Lipídeos , Potencial da Membrana Mitocondrial , Animais , Angiotensina II/farmacologia , Angiotensina II/metabolismo , Metabolismo dos Lipídeos/efeitos dos fármacos , Colo/metabolismo , Colo/efeitos dos fármacos , Colo/citologia , Ratos , Células Epiteliais/metabolismo , Células Epiteliais/efeitos dos fármacos , Potencial da Membrana Mitocondrial/efeitos dos fármacos , Lipidômica , Mitocôndrias/metabolismo , Mitocôndrias/efeitos dos fármacos , Ratos Sprague-DawleyRESUMO
Citalopram is a selective serotonin reuptake inhibitor (SSRI) used to treat depression and is often detected in aquatic environments. Here, we measured the acute toxicity of citalopram at environmentally relevant concentrations to zebrafish embryos/larvae and utilized RNA-seq to reveal potential mechanisms of toxicity. We also assessed behavioral outcomes in larval zebrafish. Zebrafish embryos were exposed continuously to embryo rearing medium (ERM), or one concentration of 0.1, 1, 10, 100, and 1000 µg/L citalopram for 7 days post-fertilization (dpf). No acute toxicity was noted for citalopram over 7-days in developing zebrafish, nor were there any effects on hatch rates; however, exposure resulted in a dose-dependent decrease in heart rate at 2 dpf. Reactive oxygen species were also increased in 7-day old larvae zebrafish exposed to 100 µg/L citalopram. There were 29 genes differentially expressed in fish exposed to 10 µg/L citalopram [FDR <0.05] and 79 genes differentially expressed in fish exposed to 1000 µg/L citalopram [FDR <0.05]. In the 1000 µg/L citalopram treatment, there were several transcripts downregulated related to muscle function, including myhz2, myhz1, and myom1. Twenty-five gene set pathways were shared between exposure concentrations including 'IL6 Expression Targets', 'Thyroid Stimulating Hormone (TSH) Resistance in Congenital Hypothyroidism', and 'GFs/TNF - > Ion Channels.' Enrichment of KEGG pathways revealed that 1000 µg/L citalopram altered processes related to the proteosome and cardiac muscle contractions. Larval zebrafish at 7 dpf showed hypoactivity with exposure to ≥10 µg/L citalopram. This may be related to the downregulation of transcripts involved in muscle function. Overall, our results show that citalopram as a pharmaceutical pollutant may have an adverse influence on aquatic species' ability to survive by reducing their abilities to elude predators (e.g. cardiac output, locomotor activity). This study improves mechanistic understanding of the potential harm citalopram may cause fish and contributes to environmental risk assessments for SSRIs in aquatic species.
RESUMO
Pethoxamid, a member of the chloroacetamide herbicide family, is a recently approved chemical for pre- or post-emergence weed control; however, toxicity data for sublethal effects in aquatic organisms exposed to pethoxamid are non-existent in literature. To address this, we treated zebrafish embryos/larvae to pethoxamid over a 7-day period post-fertilization and evaluated several toxicological endpoints associated with oxidative stress and neurotoxicity. Continuous pethoxamid exposure did not affect survival nor hatch success in embryos/larvae for 7 days up to 1000 µg L-1. Exposure to pethoxamid did not affect embryonic ATP-linked respiration, but it did reduce non-mitochondrial respiration at the highest concentration tested. We also noted a significant increase in both apoptosis and levels of reactive oxygen species (ROS) in larvae zebrafish following exposure to pethoxamid. Increases in apoptosis and ROS, however, were not correlated with any altered gene expression pattern for apoptotic and oxidative damage response transcripts. To assess neurotoxicity potential, we measured behavior and several transcripts implicated in neural processes in the central nervous system. While locomotor activity of larval zebrafish was affected by pethoxamid exposure (hyperactivity was observed at concentrations below 1 µg L-1, and hypoactivity was noted at higher exposures to 10 and 100 µg L-1 pethoxamid), there were no effects on steady state mRNA abundance for neurotoxicity-related transcripts tested. This data contributes to knowledge regarding exposure risks for chloroacetamide-based herbicides and is the first study investigating sublethal toxicity for this newly registered herbicide.
Assuntos
Apoptose , Embrião não Mamífero , Herbicidas , Larva , Estresse Oxidativo , Espécies Reativas de Oxigênio , Peixe-Zebra , Animais , Peixe-Zebra/embriologia , Herbicidas/toxicidade , Embrião não Mamífero/efeitos dos fármacos , Espécies Reativas de Oxigênio/metabolismo , Apoptose/efeitos dos fármacos , Larva/efeitos dos fármacos , Estresse Oxidativo/efeitos dos fármacos , Acetamidas/toxicidade , Síndromes Neurotóxicas/etiologiaRESUMO
Antineoplastic medications are present in aquatic environments and are measured at relatively high concentrations in hospital sewage effluent. Thus, it is important to characterize risk associated with waterborne exposures to anticancer drugs. The drug 5-fluorouracil (5-FU) is used to treat several types of cancers, acting to inhibit cell division and cellular metabolism. The objectives of this study were to determine the effects of 5-FU on developmental endpoints and lipid composition in zebrafish. 5-FU did not negatively affect development nor survival in developing zebrafish at concentrations up to 1000 µg/L. However, 5-FU increased neutral lipid content in zebrafish larvae, indicating potential for lipid dysregulation. To further discern effects on lipids, lipidomics was conducted and a total of 164 lipids belonging to 14 lipid classes were identified. Significant changes (false discovery rate < 0.05) in abundance were detected for 19 lipids including some ceramides, ether-linked phosphatidylethanolamines, and sphingomyelins among others. We also measured the expression levels of 14 lipid-related enzymes and transporters (e.g., acox3, dgat1, fads2, fasn, elovl2) using real-time PCR; however, mRNA abundance levels were not affected, suggesting transcriptional changes may not be a primary mechanism underlying lipid dysregulation. Locomotor activity was measured in zebrafish as lipids are needed for swimming activity in larvae. Exposure to 5-FU did not affect locomotor activity up to 1000 µg/L. We conclude that lipids accumulate in larval zebrafish with exposure to 5-FU, which can subsequently affect lipid composition. These data reveal potential lipid signatures of 5-FU exposure and contribute to risk assessments for antineoplastic exposure in aquatic environments.
Assuntos
Fluoruracila , Larva , Poluentes Químicos da Água , Peixe-Zebra , Animais , Poluentes Químicos da Água/toxicidade , Larva/efeitos dos fármacos , Metabolismo dos Lipídeos/efeitos dos fármacos , Antineoplásicos/toxicidade , LipídeosRESUMO
Ifosfamide is an alkylating antineoplastic drug used in chemotherapy, but it is also detected in wastewater. Here, the objectives were to (1) determine teratogenic, cardiotoxic, and mitochondrial toxicity potential of ifosfamide exposure; (2) elucidate mechanisms of toxicity; (3) characterize exposure effects on larval behavior. Survival rate, hatch rate, and morphological deformity incidence were not different amongst treatments following exposure levels up to 1000⯵g/L ifosfamide over 7 days. RNA-seq reveled 231 and 93 differentially expressed transcripts in larvae exposed to 1⯵g/L and 100⯵g/L ifosfamide, respectively. Several gene networks related to vascular resistance, cardiovascular response, and heart rate were affected, consistent with tachycardia observed in exposed embryonic fish. Hyperactivity in larval zebrafish was observed with ifosfamide exposure, potentially associated with dopamine-related gene networks. This study improves ecological risk assessment of antineoplastics by elucidating molecular mechanisms related to ifosfamide toxicity, and to alkylating agents in general.
Assuntos
Antineoplásicos , Poluentes Químicos da Água , Animais , Peixe-Zebra/metabolismo , Ifosfamida/toxicidade , Ifosfamida/metabolismo , Frequência Cardíaca , Metabolismo Energético , Antineoplásicos/farmacologia , Larva , Embrião não Mamífero , Poluentes Químicos da Água/metabolismoRESUMO
Ifosfamide is a cancer-fighting chemotherapeutic that has been detected in aquatic ecosystems. Zebrafish larvae were exposed to either 0, 1 or 100 µg/L ifosfamide in the water for 7 days, and fish were subjected to total RNA extraction and RNA-seq analysis with the Illumina NovoSeq 6000 instrument. Raw sequence data were processed through fastp and clean reads obtained by removing adapter and poly-N sequences, as well as low quality reads. Differential gene expression was performed using the abundance of transcripts that mapped to the zebrafish genome. To uncover putative targets regulated by microRNAs, Pathway Studio 12.0 was used to conduct a subnetwork enrichment analysis. Expression data were used to predict which microRNAs were important for the response to ifosfamide exposure. There were 21 common microRNAs identified in both the "IFOS1" and "IFOS100" datasets. These were MIR150, MIR6515, MIR657, MIR216A, m_Mir741, MIRLET7E, miR-let-7, MIR2392, r_Mir3551, MIR181B1, MIR33A, MIR502, MIR193B, MIR146A, MIR431, MIR647, m_Mir1192, MIR297, MIR328, and MIR4717. Data can be re-used to advance adverse outcome pathways in regulatory toxicology and to refine biomarker discovery for antineoplastics in aquatic environments.