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1.
Aquat Toxicol ; 221: 105423, 2020 Apr.
Article in English | MEDLINE | ID: mdl-32006756

ABSTRACT

Canada's oil sands industry continues to expand and the volume of diluted bitumen (dilbit) transported across North America is increasing, adding to spill risk and environmental contamination. Dilbit exposure is known to cause adverse effects in fish, but linking molecular and cellular changes with ecologically-relevant individual performance metrics is needed to better understand the potential consequences of a dilbit spill into the aquatic environment. Therefore, this study examined the effects of dilbit exposure on subcellular responses in cardiac and skeletal muscle in relation to swimming performance in a migratory fish species at risk of exposure, Atlantic salmon. Smolts were exposed subchronically to environmentally relevant concentrations of the water-soluble fraction of dilbit (WSFd) for 24 d, and then a subset of exposed fish underwent a depuration period of 7 or 14 d, for a total of 3 experimental time points. At each time point, repeat swimming performance was assessed using sequential critical swimming speed tests (Ucrit) separated by a 24 h rest period, and then several tissues were collected to determine biotransformation enzyme activation, energetic responses, and gene expression changes. Ucrit was unaffected in fish exposed to 67.9 µg/L total initial polycyclic aromatic compounds (PAC), but fish showed a decreased reliance on lipid metabolism for adenosine triphosphate (ATP) in the heart that was maintained through 7 d depuration. In contrast, Ucrit increased in fish exposed to 9.65 µg/L PAC, corresponding to an increased reliance on anaerobic metabolic pathways in cardiac and red skeletal muscle, with partial recovery after 7 d depuration. As expected, at both concentrations WSFd hepatic cyp 1A-mediated biotransformation reactions increased, as measured by EROD activity, which remained elevated for 7 d but not after 14 d depuration. Transcript abundance of cyp1a was also increased in muscle tissue and recovered by 14 d depuration. The expression of other stress-related genes increased in white muscle of dilbit-exposed fish, but were largely unchanged in cardiac and red muscle. The transcriptional profile of cardiac tissue was compared to that of sockeye salmon similarly exposed to WSFd in a previous experiment, and is provided in supplemental text. Combined, these results demonstrate that dilbit exposure alters gene expression and enzyme activities related to xenobiotic exposure, cellular stress, and muscle energetics in juvenile Atlantic salmon without impairing swimming performance, and that most of these changes are recoverable within 14 d depuration.


Subject(s)
Hydrocarbons/toxicity , Salmo salar/metabolism , Swimming , Water Pollutants, Chemical/toxicity , Animals , Cytochrome P-450 CYP1A1/metabolism , Gene Expression/drug effects , Heart/drug effects , Hydrocarbons/chemistry , Liver/drug effects , Liver/metabolism , Muscle, Skeletal/drug effects , Muscle, Skeletal/metabolism , Myocardium/metabolism , North America , Oil and Gas Fields , Salmo salar/genetics , Solubility , Water Pollutants, Chemical/chemistry
2.
Aquat Toxicol ; 221: 105419, 2020 Apr.
Article in English | MEDLINE | ID: mdl-32014643

ABSTRACT

Petrogenic chemicals are common and widespread contaminants in the aquatic environment. In Canada, increased extraction of bitumen from the oil sands and transport of the major crude oil export product, diluted bitumen (dilbit), amplifies the risk of a spill and contamination of Canadian waterways. Fish exposed to sublethal concentrations of crude oil can experience a variety of adverse physiological effects including osmoregulatory dysfunction. As regulation of water and ion balance is crucial during the seawater transition of anadromous fish, the hypothesis that dilbit impairs seawater acclimation in Atlantic salmon smolts (a fish at risk of exposure in Canada) was tested. Smolts were exposed for 24 d to the water-soluble fraction of dilbit in freshwater, and then transferred directly to seawater or allowed a 1 wk depuration period in uncontaminated freshwater prior to seawater transfer. The seawater acclimation response was quantified at 1 and 7 d post-transfer using established hematological, tissue, and molecular endpoints including gill Na+/K+-ATPase gene expression (nka). All smolts, irrespective of dilbit exposure, increased serum Na+ concentrations and osmolality within 1 d of seawater transfer. The recovery of these parameters to freshwater values by 7 d post-transfer was likely driven by the increased expression and activity of Na+/K+-ATPase in the gill. Histopathological changes in the gill were not observed; however, CYP1A-like immunoreactivity was detected in the pillar cells of gill lamellae of fish exposed to 67.9 µg/L PAC. Concentration-specific changes in kidney expression of a transmembrane water channel, aquaporin 3, occurred during seawater acclimation, but were resolved with 1 wk of depuration and were not associated with histopathological changes. In conclusion, apart from a robust CYP response in the gill, dilbit exposure did not greatly impact common measures of seawater acclimation, suggesting that significant osmoregulatory dysfunction is unlikely to occur if Atlantic salmon smolts are exposed sub-chronically to dilbit.


Subject(s)
Acclimatization/drug effects , Environmental Monitoring/methods , Hydrocarbons/toxicity , Salmo salar/physiology , Water Pollutants, Chemical/toxicity , Animals , Canada , Fresh Water/chemistry , Gills/drug effects , Gills/metabolism , Hydrocarbons/chemistry , Oil and Gas Fields , Petroleum/metabolism , Salmo salar/metabolism , Seawater/chemistry , Sodium-Potassium-Exchanging ATPase/metabolism , Solubility , Water Pollutants, Chemical/chemistry , Water-Electrolyte Balance/drug effects
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