Effects of hypoxia on rainbow trout (Oncorhynchus mykiss): intraerythrocytic phosphates

Transcriptome Analysis Provides Insights Into the Adaptive Responses to Hypoxia of a Schizothoracine Fish (Gymnocypris eckloni)

The schizothoracine fish endemic to the Qinghai-Tibetan Plateau are comparatively well adapted to aquatic environments with low oxygen partial pressures. However, few studies have used transcriptomic profiling to investigate the adaptive responses of schizothoracine fish tissues to hypoxic stress. This study compared the transcriptomes of Gymnocypris eckloni subjected to 72 h of hypoxia (Dissolved oxygen, DO = 3.0 ± 0.1 mg/L) to those of G. eckloni under normoxia (DO = 8.4 ± 0.1 mg/L). To identify the potential genes and pathways activated in response to hypoxic stress, we collected muscle, liver, brain, heart, and blood samples from normoxic and hypoxic fish for RNA-Seq analysis. We annotated 337,481 gene fragments. Of these, 462 were differentially expressed in the hypoxic fish as compared to the normoxic fish. Under hypoxia, the transcriptomic profiles of the tissues differed, with muscle the most strongly affected by hypoxia. Our data indicated that G. eckloni underwent adaptive changes in gene expression in response to hypoxia. Several strategies used by G. eckloni to cope with hypoxia were similar to those used by other fish, including a switch from aerobic oxidation to anaerobic glycolysis and the suppression of major energy-requiring processes. However, G. eckloni used an additional distinct strategy to survive hypoxic environments: a strengthening of the antioxidant system and minimization of ischemic injury. Here, we identified several pathways and related genes involved in the hypoxic response of the schizothoracine fish. This study provides insights into the mechanisms used by schizothoracine fish to adapt to hypoxic environments.

Long-term hypoxia exposure alters the cardiorespiratory physiology of steelhead trout (Oncorhynchus mykiss), but does not affect their upper thermal tolerance

It has been suggested that exposure to high temperature or hypoxia may confer tolerance to the other oxygen-limited stressor (i.e., 'cross-tolerance'). Thus, we investigated if chronic hypoxia-acclimation (>3 months at 40% air saturation) improved the steelhead trout's critical thermal maximum (CT_Max), or affected key physiological variables that could impact upper thermal tolerance. Neither CT_Max (24.7 vs. 25.3°C) itself, nor oxygen consumption ( [Formula: see text] ), haematocrit, blood haemoglobin concentration, or heart rate differed between hypoxia- and normoxia-acclimated trout when acutely warmed. However, the cardiac output (Q̇) of hypoxia-acclimated fish plateaued earlier compared to normoxia-acclimated fish due to an inability to maintain stroke volume (S_V), and this resulted in a ~50% lower maximum Q̇. Despite this reduced maximum cardiac function, hypoxia-acclimated trout were able to consume more O₂ per volume of blood pumped as evidenced by the equivalent [Formula: see text] . These results provide additional evidence that long-term hypoxia improves tissue oxygen utilization, and that this compensates for diminished cardiac pumping capacity. The limited S_V in hypoxia-acclimated trout in vivo was not associated with changes in cardiac morphology or in vitro maximum S_V, but the affinity and density of myocardial ß-adrenoreceptors were lower and higher, respectively, than in normoxia-acclimated fish. These data suggest that alterations in ventricular filling dynamics or myocardial contractility constrain cardiac function in hypoxia-acclimated fish at high temperatures. Our results do not support (1) 'cross-tolerance' between high temperature and hypoxia when hypoxia is chronic, or (2) that cardiac function is always the determinant of temperature-induced changes in fish [Formula: see text] , and thus thermal tolerance, as suggested by the oxygen- and capacity-limited thermal tolerance (OCLTT) theory.

The effects of hypoxia acclimation, exercise training and fasting on swimming performance in juvenile qingbo (Spinibarbus sinensis)

To investigate the effects of hypoxia acclimation, exercise training and fasting on the swimming performance of juvenile qingbo (Spinibarbus sinensis), we measured the critical swimming speed (U (crit)), resting and excess post-exercise oxygen consumption (EPOC) of control, hypoxia-acclimated, exercise-acclimated and fasting fish at 25°C. The muscle and plasma metabolites before and after a bout of exhaustive exercise (produced by chasing) were also measured. The fish were acclimated to hypoxia (48 h at 1.0 mg L(-1), 12.5% air saturation), exercise training (2 weeks at 60% of U (crit), 6 h daily) or fasting (2 weeks). All treatments resulted in significantly lower resting oxygen consumption ([Formula: see text]O(2rest)) but had no effect on the magnitude of EPOC. Hypoxia acclimation had no effect on U (crit) or peak post-exercise oxygen consumption ([Formula: see text]O(2peak)) but produced a higher depletion of muscle [glycogen] post-chasing (P < 0.05). Exercise training produced a significant increase in U (crit), higher liver [glycogen] pre-chasing and higher depletion of muscle [glycogen] post-chasing. Fasting resulted in a significant decrease in U (crit), [Formula: see text]O(2peak), muscle and liver [glycogen]. These results suggested that hypoxia acclimation had no effect on swimming performance in qingbo. Exercise training produced improved swimming performance by increasing the stored energy and the metabolic capacity of muscle. Fasting had a profound effect on swimming performance through both decreased respiratory capacity and a depleted energy store.

The effect of acclimation to hypoxia and sustained exercise on subsequent hypoxia tolerance and swimming performance in goldfish (Carassius auratus)

The objective of this study was to determine whether acclimation to hypoxia and sustained exercise would increase hypoxia tolerance (as indicated by a decrease in critical oxygen tension, Pcrit) and swimming performance in goldfish (Carassius auratus), and to investigate the relationship between changes in performance and gill remodelling and tissue metabolic capacity. Goldfish were acclimated to either hypoxia (48 h at 0.3 mg O2 l–1) or sustained exercise (48 h at 70% of critical swimming speed, Ucrit) and then Pcrit and Ucrit were determined in normoxia (10 mg O2 l–1) and hypoxia (1 mg O2 l–1) and compared with values from control fish. Acclimation to both hypoxia and sustained exercise improved hypoxia tolerance (Pcrit was reduced by 49% and 39%, respectively), which was associated with an increase in lamellar surface area (71% and 43%, respectively) and an increase in blood [Hb] (26% in both groups). Exercise acclimation also resulted in a decrease in routine (). Acclimation to both hypoxia and sustained exercise resulted in a significant increase in Ucrit in hypoxia (18% and 17%, respectively), which was associated with an increase in maximal O2 consumption rate at Ucrit (; 35% and 39%, respectively). While hypoxia acclimation resulted in an increase in Ucrit in normoxia, acclimation to sustained exercise did not improve subsequent swimming performance in normoxia. This lack of improvement was possibly due to depleted oxidizable substrates during exercise acclimation.

In situ cardiac function in Atlantic cod (Gadus morhua): effects of acute and chronic hypoxia

Recent in vivo experiments on Atlantic cod (Gadus morhua) acclimated to chronic hypoxia (6-12 weeks at 10°C; PwO2 ~8-9 kPa) revealed a considerable decrease in the pumping capacity of the heart. To examine whether this diminished cardiac performance was due to the direct effects of chronic moderate hypoxia on the myocardium (as opposed to alterations in neural and/or hormonal control), we measured the resting and maximum in situ function of hearts from normoxia- and hypoxia-acclimated cod: (1) when initially perfused with oxygenated saline; (2) at the end of a 15 min exposure to severe hypoxia (PO2 ~0.6 kPa); and (3) 30 min after the hearts had been reperfused with oxygenated saline. Acclimation to hypoxia did not influence resting (basal) in situ cardiac performance during oxygenated or hypoxic conditions. However, it caused a decrease in maximum cardiac output () under oxygenated conditions (from 49.5 to 40.3 ml min−1 kg−1; by 19%), that was due to diminished values for maximum stroke volume (VS) and scope for VS. Severe hypoxia reduced in both groups to ~20 ml min−1 kg−1, yet, the hearts of hypoxia-acclimated fish were better able to sustain this level of under hypoxia, and the recovery of (as compared with initial values under oxygenated conditions) was significantly improved (94% vs 83%). These data show that acclimation to hypoxia has a direct effect on cod myocardial function and/or physiology, and suggest that the cod heart shows some adaptations to prolonged hypoxia.

Analysis of highly phosphorylated inositols in avian and crocodilian erythrocytes

Both morphological and paleontological characteristics support the hypothesis of a monophyletic origin of crocodilian and avian groups. However, while the erythrocytes of all birds studied to date are reported to contain high levels of inositol pentakisphosphate (InsP(5)), which acts as an allosteric effector of hemoglobin, this molecule has not been reported in crocodilian erythrocytes. In this study we compare the highly phosphorylated inositols in crocodilian and avian erythrocytes using a particularly sensitive analytical procedure. Our aim was to obtain new data which might provide further evidence for the monophyletic origin, or otherwise, of crocodiles and birds. We studied three avian and three crocodilian species. The erythrocytes of the three bird species contained low levels of inositol-3,4,5,6-tetrakisphosphate and inositol-1,3,4,6-tetrakisphosphate, thought to be precursors of Ins(1,3,4,5,6)P(5). The crocodilian erythrocytes studied contained Ins(1,3,4,5,6)P(5) and InsP(6) in higher concentrations than those found in mammal erythrocytes and in other more active cells such as macrophages. Our data provide further evidence of the similarity between crocodilian and avian groups and agree with the hypothesis that both groups evolved from a common ancestor. The process by which the function of inositol phosphates changed from that of intracellular signaling to hemoglobin allosteric effector is discussed.

Hypoxia: from molecular responses to ecosystem responses

Hypoxia affects thousands of km2 of marine waters all over the world, and has caused mass mortality of marine animals, benthic defaunation and decline in fisheries production in many places. The severity, frequency occurrence and spatial scale of hypoxia have increased in the last few decades. Due to rapid human population growth and global warming, the problem of hypoxia is likely to become worse in the coming years. Molecular responses of marine animals to hypoxia are poorly known. In many animals, a haem protein probably serves as the cellular sensor for oxygen, and reactive oxygen species are generated as signaling molecules. In mammal and fish, a heterodimeric transcription factor, hypoxia-inducible factor 1 (HIF-1) has been identified. HIF-1 receives signals from the molecular oxygen senor through redox reactions and/or phosphorylation, and in turn, regulates the transcription of a number of hypoxia-inducible genes, including genes involved in erythropoiesis, angiogenesis and glycolysis. These molecular responses then cascade into a series of biochemical and physiological adjustments, enabling the animal to survive better under hypoxic conditions. Marine animals respond to hypoxia by first attempting to maintain oxygen delivery (e.g. increases in respiration rate, number of red blood cells, or oxygen binding capacity of hemoglobin), then by conserving energy (e.g. metabolic depression, down regulation of protein synthesis and down regulation/modification of certain regulatory enzymes). Upon exposure to prolonged hypoxia, animals must eventually resort to anaerobic respiration. Hypoxia reduces growth and feeding, which may eventually affect individual fitness. Effects of hypoxia on reproduction and development of marine animals, albeit important in affecting species survival, remain almost unknown. Many fish and marine organisms can detect, and actively avoid hypoxia. Some benthos may leave their burrows and move to sediment surface during hypoxia. These behaviorial changes may render the animals more vulnerable to predation. Hypoxia may eliminate sensitive species, thereby causing major changes in species composition of benthic, fish and phytoplankton communities. Decreases in species diversity and species richness are well documented, and changes in trophodynamics and functional groups have also been reported. Under hypoxic conditions, there is a general tendency for suspended feeders to be replaced by deposit feeders; demersal fish by pelagic fish; and macrobenthos by meiobenthos. Microflagellates and nanoplankton also tend to dominate in the phytoplankton community in hypoxic environments. Existing evidence suggest that recovery of benthic communities in temperate region take two to several years. Recovery however, appears to be much quicker in subtropical environments. In natural conditions, hypoxia is often associated with increases in ammonia, hydrogen sulphide and particulate organic materials. The inability to isolate effects of hypoxia from interactions of these compounding factors makes it difficult to attribute many of the observed ecological effects to hypoxia.