Abstract

BackgroundUranium (U) is a naturally occurring radionuclide that has been found in the aquatic environment due to anthropogenic activities. Exposure to U may pose risk to aquatic organisms due to its radiological and chemical toxicity. The present study aimed to characterize the chemical toxicity of U in Atlantic salmon (Salmo salar) using depleted uranium (DU) as a test model. The fish were exposed to three environmentally relevant concentrations of DU (0.25, 0.5 and 1.0 mg U/L) for 48 h. Hepatic transcriptional responses were studied using microarrays in combination with quantitative real-time reverse transcription polymerase chain reaction (qPCR). Plasma variables and chromosomal damages were also studied to link transcriptional responses to potential physiological changes at higher levels.ResultsThe microarray gene expression analysis identified 847, 891 and 766 differentially expressed genes (DEGs) in the liver of salmon after 48 h exposure to 0.25, 0.5 and 1.0 mg/L DU, respectively. These DEGs were associated with known gene ontology functions such as generation of precursor metabolites and energy, carbohydrate metabolic process and cellular homeostasis. The salmon DEGs were then mapped to mammalian orthologs and subjected to protein-protein network and pathway analysis. The results showed that various toxicity pathways involved in mitochondrial functions, oxidative stress, nuclear receptor signaling, organ damage were commonly affected by all DU concentrations. Eight genes representative of several key pathways were further verified using qPCR No significant formation of micronuclei in the red blood cells or alterations of plasma stress variables were identified.ConclusionThe current study suggested that the mitochondrion may be a key target of U chemical toxicity in salmon. The induction of oxidative stress and uncoupling of oxidative phosphorylation may be two potential modes of action (MoA) of DU. These MoAs may subsequently lead to downstream events such as apoptosis, DNA repair, hypoxia signaling and immune response. The early toxicological mechanisms of U chemical toxicity in salmon has for the first time been systematically profiled. However, no other physiological changes were observed. Future efforts to link transcriptional responses to adverse effects have been outlined as important for understanding of potential risk to aquatic organisms.Electronic supplementary materialThe online version of this article (doi:10.1186/1471-2164-15-694) contains supplementary material, which is available to authorized users.

Highlights

  • Uranium (U) is a naturally occurring radionuclide that has been found in the aquatic environment due to anthropogenic activities

  • The top network found in this study showed that U regulated a group of differentially expressed genes (DEGs) associated with DNA replication, recombination and repair, representing transcriptional responses to potential DNA damage caused by U

  • The results from the present study suggested that ionic U species may accumulate in the liver and exert toxicity mainly through two potential modes of action (MoA), one was the induction of organellar or cellularwide oxidative stress, the other was the uncoupling of oxidative phosphorylation (OXPHOS) in the mitochondrion

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Summary

Introduction

Uranium (U) is a naturally occurring radionuclide that has been found in the aquatic environment due to anthropogenic activities. Exposure to U may pose risk to aquatic organisms due to its radiological and chemical toxicity. Uranium (U) is a naturally occurring heavy metal of the actinide series and decays by emitting alpha particles, exhibiting both chemical and radiological toxicity. Uranium is usually released anthropogenically to the aquatic environment through the nuclear fuel cycle, such as U mill tailings, mill and refining, effluent from conversion plants, and stack emissions [1]. Uranium may accumulate in bone, liver and kidney of an organism, but may not be biomagnified [5] In fish, such as Atlantic salmon and zebrafish (Danio rerio), U has been shown to accumulate in gill, liver, brain and skeletal muscles [6,7]. Due to the chemical and radioactive properties, U as a single substance may produce multiple-stressor effects in an organism, complicating the subsequent hazard assessment

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