Elsevier

Environmental Pollution

Volume 242, Part A, November 2018, Pages 952-961
Environmental Pollution

0# Diesel water-accommodated fraction induced lipid homeostasis alteration in zebrafish embryos

https://doi.org/10.1016/j.envpol.2018.07.055Get rights and content

Highlights

  • 0# diesel WAF altered transcription of genes are related to lipid metabolism.

  • 0# diesel WAF could inhibit transcription of genes involved in cholesterol synthesis.

  • 0# diesel WAF reduced levels of several lipid species of zebrafish embryos.

Abstract

To investigate the developmental effects and corresponding molecular mechanism of diesel in freshwater organisms, zebrafish embryos were exposed to 0# diesel water-accommodated fraction (WAF) at different concentrations. Mortality, embryonic morphological endpoints, transcriptional profile and lipid profile were evaluated after exposure. Exposure to 0# diesel WAF had no significant effect on the survival of zebrafish embryos from 1.5 to 96 hpf. However, a significant increase in mortality was observed at 144 and 196 hpf in the groups of 20 and 40 mg/L 0# diesel WAF. RNA-Seq results demonstrated that 0# diesel WAF could induce significant alterations in transcription profile at concentrations of 0.05 mg/L (the limit for petroleum hydrocarbon concentration in surface water in China) and 5 mg/L. Gene Ontology enrichment and similarity analysis indicated that lipid metabolism, lipid synthesis, biological transport, drug metabolism and homeostatic processes were the most altered biological processes after exposure to 0# diesel WAF. Further, transcription levels of genes involved in cholesterol and fatty acid synthesis were significantly inhibited by diesel WAF according to qPCR results. Lipidomics results also indicated that several lipid species (cholesterol ester, fatty acid, diglyceride and triglyceride) decreased after 0# diesel WAF exposure. These results reflect the potential risk of diesel pollution in freshwater ecosystems especially on the alteration of lipid homeostasis and enable a better understanding of the molecular pathways underlying the action of diesel WAF in zebrafish embryos.

Introduction

Recently (January 6, 2018) a ship collision accident occurred near the estuary of Yangtze River, resulting in large amount condensate and fuel oil into the offshore of the East China Sea. Although condensate evaporates quickly from seawater, the potential risk of remaining fuel oil towards marine and freshwater ecosystems has aroused widespread concern>.

The occurrence of oil originating from ship accidents or other anthropogenic activities (e.g., ship operation, oil drilling, pipe cracks and transport of bunker fuel) in water environments may have negative effects on aquatic ecosystems (Crone and Tolstoy, 2010; Miljeteig et al., 2013; Won et al., 2016). In a typical freshwater oil spill, approximately 4 million liters of oil were accidentally discharged into the Arroio Saldanha River in 2000, affecting an area of 2.5 km2, including rivers and small streams in Barigui and Iguacu (Silva et al., 2009). Although these kinds of large oil spills are widely covered in the media, the main source of petroleum contamination in inland waters is thought to be ship leaks into surface water along with small, continuous leakages from underground bulk storage tanks, which reach groundwater and later rivers (Tiburtius et al., 2005). Previous studies have found that crude and fuel oil exposure can induce multiple responses (e.g., oxidative stress, reproductive toxicity, DNA damage, behavioral effects and immune response) in mammals, fish, crustaceans and phytoplankton in marine environments (Monson et al., 2011; Dubansky et al., 2013; Mager et al., 2014; Alloy et al., 2015; Ozhan et al., 2014).

Oil contamination poses considerable threats to the yield and quality of aquatic production as well as the personal health of consumers. In consideration of the impact of petroleum hydrocarbon pollution on aquatic organisms, the Chinese government imposed a maximum oil level in surface water of 0.05 mg/L (Ministry of Environment Protection, 2002). However, according to the environmental monitoring results obtained in major fisher areas in China, petroleum hydrocarbon contents exceeding this threshold have been detected in recent years (Ministry of Agriculture and Ministry of Environment Protection, 2014–2016). Therefore, it is necessary to investigate the toxic effects of petroleum contaminants in aquatic organisms to determine the ecological risks of oil pollution.

0# diesel is widely used as a fuel for the diesel engines of ships and vehicles and is one of the main sources of petroleum hydrocarbons in freshwater. Exposure to diesel or its derivatives can induce a variety of toxic symptoms in animals. Studies on goldfish (Carassius auratus) have shown that the water-soluble fraction of diesel oil can significantly induce antioxidant defenses at concentrations of 0.05 and 0.1 mg/L over 40 days of exposure (Zhang et al., 2004). Geraudie et al. (2016) reported that diesel shows neurotoxicity towards Icelandic scallops (Chlamys islandica) after seven days of exposure. Studies on mammals have also indicated that diesel pollutants cause inflammation, reproductive toxicity and immune response in various organisms (Kisin et al., 2015; Yanamala et al., 2013; Cole et al., 2016). Despite the reported toxicity data, the lipid homeostasis alteration and developmental effects of diesel pollutants remain uncharacterized.

The water-accommodated fraction (WAF) of oil is the fraction that contains the largest amount of water-soluble hydrocarbons, and WAF exposure is considered as an alternative method to evaluate the toxic effects of oil (Mager et al., 2014; Singer et al., 2000; Temkin et al., 2016). Currently, aquatic bioassay has been an frequently approach to evaluate the impacts of hazardous chemicals (Qiao et al., 2016), and zebrafish (Danio rerio) embryo is one of the most widely used model for eco-toxicological investigations (Mu et al., 2018; Batel et al., 2018; Kim et al., 2018). In the present study, the mortality, developmental effects, lipid homeostasis alteration and corresponding biological pathways of 0# diesel WAF are investigated using zebrafish embryos as a model. These results reflect the potential risk of diesel pollution to freshwater animals and enable a better understanding of the molecular mechanism of diesel WAF in zebrafish embryos.

Section snippets

Zebrafish maintenance and embryo collection

Adult wild-type AB zebrafish (10 months old) were obtained from China Zebrafish Resource Center (Wuhan, China). All adult zebrafish were maintained in flow-through feeding equipment (Esen Corp.) at 26 °C with a 14/10 h (light/dark) photoperiod and fed daily with live brine shrimp (Artemia salina). The preparation of zebrafish embryos was carried out as described in our previous work (Mu et al., 2013).

Chemicals and reagents

Commercial 0# diesel was purchased from a local fuel supplier. Standard water was prepared in

Exposure validation

The total PH content in the exposure media was validated by UV spectrophotometric determination (Figs. S1–S2). According to the water analysis results, the nominal oil concentrations of 10 mg/L and higher could basically represent the actual oil level in the exposure solution (the deviation between nominal and actual oil concentrations was less than 30%, Tables S1–S3). However, for dosages of 5 mg/L and lower, large fluctuations in the detected level of oil were observed during the exposure

Discussion

Diesel fuel can harm environmental health via multiple media, including air, soil, seawater and freshwater (Rundle et al., 2012; Balliana et al., 2017; Sagerup et al., 2016; Simonato and Guedes., 2008). The negative effects of diesel exhaust particles on environmental organisms and particularly mammals have been intensively investigated in recent years (Bengalli et al., 2017; Trindade et al., 2017). In addition, the toxic effects of diesel-contaminated soils on earthworms (Eudrilus eugeniae),

Conclusion

Based on the zebrafish embryo developmental test, the current oil limit of 0.05 mg/L is basically safe for freshwater creatures since the effective dosage (5 mg/L) is far from the limit. However, it is worth noting that the transcriptional profiles of zebrafish embryos were altered after exposure to 0.05 mg/L 0# diesel WAF, which reflects the potential to alter different biological pathways, including lipid metabolism, the endocrine system and amino acid metabolism. Furthermore, cholesterol

Author declaration

We declare that we have no actual or potential competing financial interest, and that no part of this paper has published or submitted elsewhere.

Acknowledgements

This research work was supported by the Special Funds of Key Technology in Oil Spills and the Special Funds of Conservation of Species Resources from the Chinese Ministry of Agriculture “Ecological Environment Monitoring of Chinese Fishery Water Areas.”

References (62)

  • X. Mu et al.

    Evaluation of acute and developmental effects of difenoconazole via multiple stage zebrafish assays

    Environ. Pollut.

    (2013)
  • X. Mu et al.

    The developmental effect of difenoconazole on zebrafish embryos: a mechanism research

    Environ. Pollut.

    (2016)
  • H.F. Olivares-Rubio et al.

    Lipid metabolism and pro-oxidant/antioxidant balance of Halamphora oceanica from the Gulf of Mexico exposed to water accommodated fraction of Maya crude oil

    Ecotoxicol. Environ. Saf.

    (2018)
  • P. Perez et al.

    Fuel toxicity on Isochrysis galbana and a coastal phytoplankton assemblage: growthratevs. variable fluorescence

    Ecotoxicol. Environ. Saf.

    (2010)
  • Q. Qiao et al.

    An integrated omic analysis of hepatic alteration in medaka fish chronically exposed to cyanotoxins with possible mechanisms of reproductive toxicity

    Environ. Pollut.

    (2016)
  • S. Raimondo et al.

    Developmental toxicity of Louisiana crude oil-spiked sediment to zebrafish

    Ecotoxicol. Environ. Saf.

    (2014)
  • K. Sagerup et al.

    Biological effects of marine diesel oil exposure in red king crab (Paralithodes camtschaticus) assessed through a water and foodborne exposure experiment

    Mar. Environ. Res.

    (2016)
  • C.A. Silva et al.

    Evaluation of waterborne exposure to oil spill 5 years after an accident in Southern Brazil

    Ecotoxicol. Environ. Saf.

    (2009)
  • J.D. Simonato et al.

    Martinez, CBR. Biochemical, physiological, and histological changes in the neotropical fish Prochilodus lineatus exposed to diesel oil

    Ecotoxicol. Environ. Saf.

    (2008)
  • M.M. Singer et al.

    Standardization of the preparation and quantitation of water-accommodated fractions of petroleum for toxicity testing

    Mar. Pollut. Bull.

    (2000)
  • N. Yanamala et al.

    Biodiesel versus diesel exposure: enhanced pulmonary inflammation, oxidative stress, and differential morphological changes in the mouse lung

    Toxicol. Appl. Pharmacol.

    (2013)
  • J.F. Zhang et al.

    Effects of water-soluble fractions of diesel oil on the antioxidant defenses of the goldfish, Carassius auratus

    Ecotoxicol. Environ. Saf.

    (2004)
  • E. Agamy

    Histopathological changes in the livers of rabbit fish (Siganus canaliculatus) following exposure to crude oil and dispersed oil

    Toxicol. Pathol.

    (2012)
  • M.M. Alloy et al.

    Photo-induced toxicity of deepwater horizon slick oil to blue crab (Callinectes sapidus) larvae

    Environ. Toxicol. Chem.

    (2015)
  • A.G. Balliana et al.

    Development of Canavalia ensiformis in soil contaminated with diesel oil

    Environ. Sci. Pollut. Res. Int.

    (2017)
  • C. Barton

    Paramecium recipes for large and small facilities. The zebrafish book

  • A.P. Carll et al.

    Diesel exhaust inhalation increases cardiac output, bradyarrhythmias, and parasympathetic tone in aged heart failure-prone rats

    Toxicol. Sci.

    (2013)
  • M.G. Carls et al.

    Sensitivity of fish embryos toweathered crude oil: part I. Low-level exposure during incubationcauses malformations, genetic damage, and mortality in larval pacificherring (Clupea pallasi)

    Environ. Toxicol. Chem.

    (1999)
  • T.J. Crone et al.

    Magnitude of the 2010 Gulf of Mexico oil leak

    Science

    (2010)
  • B. Dubansky et al.

    Multitissue Molecular, genomic, and developmental effects of the deepwater horizon oil spill on resident gulf killifish (Fundulus grandis)

    Environ. Sci. Technol.

    (2013)
  • O.A. Ekperusi et al.

    Bioremediation of heavy metals and petroleum hydrocarbons in diesel contaminated soil with the earthworm: eudrilus eugeniae

    SpringerPlus

    (2015)
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