Abstract
NaCl-rich rock salt dissolved in natural water source leads to salinity fluctuation that profoundly affects freshwater ecosystem and aquatic fauna. The snakehead (Channa striata) can live in saline water, but the osmoregulatory mechanisms underlying this ability remain unclear. Herein, we found that exposure to salinities ≥10 ‰ NaCl markedly elevated plasma cortisol and glucose levels, and caused muscle dehydration. In a study of time-dependent response after being transferred from fresh water (0 ‰ NaCl, FW) to salt-dissolved brackish water (10 ‰ NaCl, SW), FW–SW, cortisol increased rapidly along with elevations of plasma glucose and lactate. Interestingly, plasma cortisol returned to baseline after prolonged exposure, followed by a second peak that probably enhanced the branchial Na+/K+-ATPase activity. Under SW–FW condition, Na+/K+-ATPase activity was not altered as compared to SW-adapted fish. In conclusion, salinity change, especially FW–SW, induced a stress response and hence cortisol release in C. striata, which might increase plasma glucose and lactate to energize the branchial Na+/K+-ATPase.
Similar content being viewed by others
Explore related subjects
Discover the latest articles, news and stories from top researchers in related subjects.Avoid common mistakes on your manuscript.
Introduction
Salinity is an important environmental factor, which influences the distribution of fish. Salinity effects have been studied in several freshwater fish (Altinok and Grizzle 2001; Luz et al. 2008), but while most studies have focused on the effects of seawater, little is known about the consequence of rock salt contamination (Bringolf et al. 2005). Approximately, 85 and 96 % of mineral contents is NaCl in seawater and rock salt-contaminated water, respectively. Seawater also contains sulfate, magnesium, potassium, and calcium (Bringolf et al. 2005); therefore, the effects of two water sources on aquatic fauna are different. The natural water sources in northeastern Thailand are contaminated by NaCl-rich rock salt (also known as halite) from extensive outcrop of Mesozoic rock as well as the underground NaCl-rich rock salt (El Tabakh et al. 1999). In the dry season, the salinity can be as high as 32 ‰ and is similar to seawater (Suwannatrai et al. 2011). This condition thus inevitably has a widespread ecological impact on the local water dwelling flora and fauna.
Environmental salinity fluctuations induce stress response in freshwater fish (Mommsen et al. 1999; Barton 2002; Kammerer et al. 2010), as indicated by the elevated plasma cortisol level (Wendelaar Bonga 1997). The rise of cortisol is important for survival as it increases blood glucose via glycogenolysis (rapid response) and gluconeogenesis (long-term response) to provide energy and enhance the ability of teleosts to adapt to environmental osmotic changes (Morgan and Iwama 1996; Vijayan et al. 1996; Mommsen et al. 1999). In euryhaline teleosts, cortisol has a role in seawater adaptation by stimulating differentiation of the gill chloride cells (mitochondria-rich cells) and branchial Na+/K+-ATPase activity, thus enhancing seawater tolerance in euryhaline fish (Madsen and Bern 1993; Madsen et al. 1995; McCormick 1996). However, the exact role of cortisol and branchial Na+/K+-ATPase activity in stenohaline freshwater teleosts in their osmoregulatory response to saltwater is not known.
Previous reports revealed that air-breathing fish, namely Monopterus albus (Pedersen et al. 2014), Anabas testudineus (Chang et al. 2007), and Clarias batrachus (Sarma et al. 2013), could survive in brackish water. Specifically, M. albus thrived in 10 ‰ salinity, while A. tesudineus tolerated up to 30 ‰. For C. batrachus, although they could endure in as high as 8 ‰ salinity, growth and survival rates were low when compared to fish living in fresh water. However, little is known regarding the salinity tolerance of air-breathing fish in the Channidae family. The snakehead (Channa striata), a freshwater teleost of Family Channidae and Order Perciformes, is economically important and is distributed throughout southern and southeastern Asia (Vidthayanon 2002). This species normally inhabits ponds, rice field and rivers, preferring stagnant and muddy water of plains. They can survive in dry season by burrowing in bottom mud as long as skin and breathing apparatus remain moist (Musikasinthorn 2003). The natural habitat of snakehead ranges from fresh water to brackish water. Although they live in brackish environments especially in the summer, the snakehead is normally cultured in freshwater in Asia, except in northeastern Thailand where they are cultured in brackish water (De Silva 2008). Since snakehead is a freshwater fish species that live in areas with NaCl-rich rock salt contamination, it is important to understand their salinity tolerance and osmoregulatory response, especially how an increase in salinity affects the physiochemical blood parameters and branchial Na+/K+-ATPase activity.
In the present study, we aimed to investigate (1) the acute effect (1 h) of different level of salinity on blood chemistry (glucose, lactate, Na+, Cl−, and K+) of C. striata, and (2) the long-term effects (15 days) of osmotic changes caused by transferring fish from fresh water to 10 ‰ NaCl, and vice versa. We also determined time-dependent changes in plasma cortisol levels, and the correlation between the increased cortisol levels and plasma osmolality or branchial Na+/K+-ATPase activity.
Materials and methods
Animals
Snakehead (C. striata) weighing 120 ± 1.24 g were obtained from natural water sources in Khon Kaen Province in the northeast of Thailand, and maintained in four aerated fiberglass tanks (160 × 110 × 55 cm3). Each tank held 150 L of dechlorinated tap water equipped with charcoal filters and air stones. Water temperature was 22–26 °C. Fifty percent of water was changed daily. They were fed brine shrimp (Artemia salina) twice a day (~2 % of body weight per day) and acclimated for more than a week. Since A. salina was cultured in seawater, they were washed several times with fresh water before use. Once fish looked healthy and ate well, they were divided into two groups. The first group was transferred to salt water, which was prepared by dissolving NaCl (Anivar, Australia) in dechlorinated tap water, and salinity was determined by a light refractometer. Salinity in the tank was increased at a rate of 2 ‰ NaCl per day and fish were allowed to acclimate to new salinity for 24 h until the endpoint salinity of 10 ‰ NaCl. A half of water in each tank was replaced with 10 ‰ NaCl every 4 days. The second group was acclimated in dechlorinated tap water (fresh water). Both groups were kept under these conditions for at least 4 weeks prior to the experiment. Fish were maintained under natural photoperiod. Stressors (e.g., noise, crowding, and vibration) were kept to minimum to avoid variation of cortisol levels. This study has been approved by the Animal Ethics Committee of Khon Kaen University, Thailand (no. 0514.1.12.2/26). All animals were cared for in accordance with the Ethics of Animal Experimentation of National Council of Thailand.
Experimental design
Experiment 1: acute effect of the various salinities on blood chemistry of C. striata
Chemical and ion compositions of fresh water and salt water are shown in Table 1. Animals were fasted for 24 h prior to the experiment. The freshwater-acclimated fish were randomly placed into each concentration of salt water for 1 h. The control group [0 ‰ NaCl, fresh water] was exposed to dechlorinated tap water. Finally, all fish were subjected to determinations of plasma osmolality, muscle water content, and plasma concentrations of cortisol, glucose, Na+, Cl−, and K+. The muscle water content after an acute salinity exposure reflected the ability of fish to restrict water loss.
Experiment 2: time-dependent adaptation to salt-dissolved brackish water (SW)
The experimental group (FW–SW) was fish exposed to abrupt salinity change from fresh water, FW, (0 ‰ NaCl) to salt-dissolved brackish water (10 ‰ NaCl), whereas the control group (FW–FW) was fish transferred from fresh water to fresh water. To avoid handling stress, the old water in the tanks was rapidly pumped out and concurrently replaced with the experimental medium. Plasma osmolality, blood chemistry (plasma concentrations of cortisol, glucose, lactate, Na+, and Cl−) and branchial Na+/K+-ATPase activity were measured at 0 h (fresh water), and then at 1, 3, 4, 6, 12, 24, 72, 168, 240, and 360 h after exposure (n = 8 animals per each time point).
Experiment 3: response of SW-acclimated fish to fresh water
In the experimental group (SW–FW), fish acclimated in SW (10 ‰ NaCl) for 4 weeks were transferred to fresh water (0 ‰ NaCl), whereas the control group (SW–SW) was transferred from brackish to brackish water. Plasma osmolality, blood chemistry (plasma concentrations of cortisol, glucose, lactate, Na+, and Cl−) and branchial Na+/K+-ATPase activity were measured at 0 h (salt water), and then at 1, 3, 4, 6, 12, 24, 72, 168, 240, and 360 h after exposure (n = 8 animals per each time point).
Sample collections
Prior to blood collection by cardiac puncture, fish were anesthetized with 0.5 % tricaine methanesulfonate (catalog no. MS222; Sigma, St. Louis, MO, USA). The water used for anesthesia had the same temperature and electrolyte composition as that previously used in the experiment. It took about 5 min for the fish to become unconscious. Under anesthesia, the heart was exposed immediately, and blood sample was drawn from the bulbus arteriosus using a syringe coated with 200 U mL−1 ammonium heparin (Sigma). Plasma was stored at −80 °C until analysis. The muscle tissue samples (~0.5 g) were collected from epaxial side in duplicate and weighed immediately to obtain wet weight. Thereafter, they were dried at 60 °C for 48 h and then weighed (dry weight). The percent muscle water content was calculated as: (wet weight − dry weight)/wet weight × 100.
Blood and water analyses
Plasma and water osmolality was determined by a freezing point-based osmometer (Advanced Instruments, Norwood, MA, USA). Concentrations of Na+, Cl−, and K+ in plasma and water were determined by ion-selective electrode system of Cobas 6000 analyzer module c501 (Roche Diagnostics, Rotkreuz, Switzerland). Concentrations of glucose and lactate were also measured by Cobas 6000 analyzer. Plasma samples were analyzed in triplicate or duplicate, depending on available plasma volume. Hematocrit measurement was performed in duplicate using microhematocrit capillary tubes centrifuged at 11,000 rpm for 5 min in a microhematocrit centrifuge.
Measurement of cortisol level
Plasma cortisol concentrations were determined by radioimmunoassay using a commercial kit (ImmuChemCoated Tube Cortisol 125I RIA kit, MP Biomedicals, NY, USA). Plasma samples and standards were pipetted into anti-cortisol-coated tubes. Cortisol-3-carboxymethyloxime-BSA was used as an immunogen to produce anti-cortisol antibody in rabbits. The anti-serum was coated and bound to the inner surface of a polypropylene tube. Cortisol 125I was added to all tubes followed by 45-min incubation. The coated tubes were then analyzed in a gamma counter to determine the amount of antibody-bound 125I-cortisol. Levels of cortisol in the plasma samples were obtained from the standard curve. The anti-serum (primary antibody) reacted 100 % with cortisol, 12.3 % with 11-desoxycortisol, 5.5 % with corticosterone, 2.1 % with cortisone, 0.25 % with progesterone, and <0.1 % with testosterone.
Na+/K+-ATPase activity assay
The measurement of Na+/K+-ATPase activity was modified from the method of McCormick (1993). Gill tissues taken from the fish were homogenized in 200 µL of SEID buffer (150 mM sucrose, 10 mM Na2EDTA, 10 mM imidazole, 0.1 % deoxycholic acid), and then centrifuged at 5000g for 1 min. Homogenate samples (10 µL) were added into 200 µL of solution A [4 U mL−1 lactate dehydrogenase, 5 U mL−1 pyruvate kinase, 2.8 mM phosphoenolpyruvate (PEP), 0.7 mM ATP, 0.22 mM NADH, and 50 mM imidazole, pH 7.5] or solution B [solution A plus 0.5 mM ouabain (Na+/K+-ATPase inhibitor)] in 96-well microplates at 25 °C, followed by reading at 340 nm for 10 min by a microplate reader (Bio-Rad, QC, Canada) to determine a decrease in NADH level, which was used to calculate ATP hydrolysis (McCormick 1993). Each pair of wells (with and without ouabain) was determined for Na+/K+-ATPase activity (µmol ADP mg protein−1 h−1), which was calculated from the difference of ATP hydrolysis in the absence and presence of ouabain. The total protein concentrations were determined by bicinchoninic acid (BCA) assay kit (Pierce, Rockford, IL, USA).
Statistical analysis
All data were analyzed by GraphPad Prism 6.0 (San Diego, CA, USA). Results are expressed as mean ± SE. Differences between groups were analyzed by one-way analysis of variance (ANOVA) with Dunnett’s post test. Comparison between the two factors, i.e., salinity and time, were performed by two-way ANOVA. The interaction between salinity and time was also analyzed. The level of significance for all statistical analyses was P < 0.05.
Results
Experiment 1: acute effect of the various salinities on the blood chemistry of C. striata
In natural water sources, there is a periodic change in salinity, and fish might be exposed to a brief salinity fluctuation. Therefore, the present experiment was performed to demonstrate an abrupt change in blood chemistry after 1-h exposure to NaCl-contaminated water, which mimicked a sudden exposure to natural salinity fluctuation. Snakeheads could survive after 1-h exposure to 2, 5, 10, 15, and 20 ‰ NaCl, but none survived in 35 ‰ NaCl. Fish exposed to 15 and 20 ‰ NaCl showed stress behaviors, such decreased movement and increased mucus secretion, and eventually died within 6 h. Their blood chemistry and percent muscle water content are shown in Table 2. Percent muscle water content increased significantly at 2 ‰ NaCl and decreased at salinities >5 ‰ NaCl, while hematocrit was significantly increased at salinity 20 ‰ NaCl. Plasma glucose was elevated in all salinities and reached the highest level at 10 ‰ NaCl. Plasma levels of K+ were not altered after exposure to salt water.
The osmolality and ion concentrations (Na+, Cl−, and K+) of FW and SW (2, 5, 10, 15, 20, and 35 ‰ NaCl) were determined (Table 1). The osmolality values of media with 0, 2, 5, 10, 15, 20, and 35 ‰ NaCl were 9, 70, 166, 310, 460, 640, and 1126 mOsm kg−1 H2O, respectively. Since plasma osmolality of the fish exposed to fresh water (9 mOsm kg−1 H2O) was about 281.8 ± 16.0 mOsm kg−1 H2O, plasma cortisol levels remained unchanged after 1-h exposure to hypoosmotic media (70 and 166 mOsm kg−1 H2O), but were significantly increased in hyperosmotic solution (310, 460, and 640 mOsm kg−1 H2O) (Fig. 1a). Plasma concentrations of Na+ and Cl− as well as the plasma osmolality were elevated significantly with increasing salinities, starting from 310 mOsm kg−1 H2O (Fig. 1b, c).
Experiment 2: time-dependent adaptation to SW
No evidence of mortality in FW–SW and FW–FW groups was found, but there were conspicuous changes in blood ion levels, plasma osmolality, and cortisol levels in the FW–SW group as compared to FW–FW group. Changes in the plasma cortisol levels were complex. Specifically, they were transiently increased during the first hour after being transferred from FW to SW, but returned to the control level at 4 h, increased again at 72–240 h, and then returned to the baseline value at 360 h (day 15). There was no change in cortisol level in the FW–FW group (Fig. 2a).
Plasma osmolality of FW-adapted fish was elevated at 1 h after being transferred to SW as compared to the value at 0 h (Fig. 2b). After exposure to water salinity 10 ‰ (310 mOsm kg−1 H2O) for 168 h, the plasma osmolality could increase from ~280 mOsm kg−1 H2O (at 0 h) to 390 mOsm kg−1 H2O, which was greater than that of the plasma baseline and medium by ~40 and ~25 %, respectively. The plasma levels of Na+ and Cl− significantly increased at 3 and 1 h, respectively, after being transferred to SW (Fig. 2c). Ion concentrations remained higher than that of the control levels even after 360 h.
Figure 3a and b show the plasma glucose and lactate levels, respectively. The control and treatment fish were obtained from FW–FW and FW–SW groups, respectively. In the FW–SW group, marked increases in both plasma glucose and lactate levels were observed within the first hour post-transfer as compared to the corresponding FW–FW group, before returning to the control levels at 4 h. The control group exhibited a relatively constant value throughout the experimental period. Moreover, FW–SW group showed a two-fold increase in the branchial Na+/K+-ATPase activity on day 7 (168 h) compared to the baseline level (0 h), which remained at this high level until the end of the experiment (Fig. 4). The branchial Na+/K+-ATPase activity of FW–FW group was not altered.
Experiment 3: response of SW-acclimated fish to fresh water
In this series of experiments, the SW-acclimated fish were transferred to either FW (experimental group; SW–FW) or 10 ‰ NaCl (control group; SW–SW). Plasma cortisol levels in both control and experimental groups appeared higher at the first hour post-transfer as compared to the baseline level at 0 h (Fig. 5a), before returning to the baseline level thereafter. Plasma osmolality and concentrations of Na+ and Cl− rapidly decreased during the first hour post-transfer, and remained relatively constant until the end of experiment (Fig. 5b, c). Plasma glucose peaked at 3 h and then decreased to the baseline level, while that of the control fish (SW–SW) remained unaltered throughout the experiment (Fig. 6a). Both SW–FW and SW–SW groups had similar levels of plasma lactate (Fig. 6b) and branchial Na+/K+-ATPase activities (Fig. 7).
Discussion
The snakehead fish occasionally encounter fluctuations in environmental salinity. The present study revealed that the abrupt transfer of the snakehead fish to media of various salinities could induce increases in plasma cortisol, plasma osmolality and ions (Na+ and Cl−). Abrupt changes in cortisol and glucose levels that occurred shortly after salinity change likely provided extra energy for coping with unfavorable conditions. The fish endured salt-dissolved brackish water (10 ‰) for a long duration, and interestingly exhibited a second peak of plasma cortisol. This response may in fact account for the enhancement of branchial Na+/K+-ATPase activity that allowed the fish to maintain ionic homeostasis. Under SW–FW condition, rapid loss of Na+ and Cl− and a brief stress were observed, and the considerably higher activity of Na+/K+-ATPase of SW–SW and SW–FW fish, as compared to FW-adapted fish, remained unchanged. Hence, the snakehead was capable of adapting to salt-dissolved brackish water, similar to other freshwater teleosts, e.g., climbing perch (A. testudineus) (Chang et al. 2007), Asian swamp eel (M. albus) (Pedersen et al. 2014), white sucker (Catostomus commersoni) (Wilkes and McMahon 1986), common carp (Cyprinus carpio) (Wang et al. 1997), flathead catfish (Pylodictis olivaris) (Bringolf et al. 2005), and goldfish (Carassius auratus) (Luz et al. 2008).
The common responses of stenohaline freshwater fish to salinity changes are the increased plasma osmolality and ion concentrations (Eckert et al. 2001; Tam et al. 2003; Luz et al. 2008), both of which were observed in snakehead. Since Na+ and Cl− are the major electrolytes in body fluid, regulation of both Na+ and Cl− is critical for osmoregulation (Evans 2008; Kaneko et al. 2008). When fish are exposed to hyperosmotic medium relative to plasma osmolality, water tended to be lost from the body with salt influx across the gill epithelium. The plasma hyperosmolality-induced tissue water loss—as indicated by muscle dehydration—was not only found in snakehead but also reported in common carp (Van der Linden et al. 1999) and goldfish (Luz et al. 2008). In addition, a decrease in plasma free water also raised the hematocrit in snakehead, similar to that observed in white sucker (C. commersonii) (Wilkes and McMahon 1986). In Asian swamp eel, hematocrit decreased after a long exposure to saline water (Pedersen et al. 2014). However, hematocrit was not altered in some other species, such as goldfish (C. auratus), tilapia (O. mossambicus), and gray snapper (Lutjanus griseus) after a direct salinity exposure (Luz et al. 2008; Kammerer et al. 2010; Serrano et al. 2011). The upper limit of salinity tolerance in stenohaline freshwater fish appeared to be determined by their ability to deal with soft tissue dehydration and to restrict an increase in plasma osmolality. If freshwater fish are exposed to a relatively high salinity, they may eventually die of continuous water loss and blood electrolyte imbalance (Maceina and Shireman 1979; Wang et al. 1997; Luz et al. 2008). As shown here, exposure of the snakehead to >10 ‰ salinity levels resulted in 100 % mortality within 24 h, indicating that salinities around 10 ‰ were the upper limit of tolerance for this species.
Plasma cortisol was increased as early as 1 h following exposure to 10 ‰ NaCl (Fig. 2a), and subsequently decreased after 3 h of exposure. The increases in plasma osmolality, Na+, and Cl− at 1, 3, and 1 h, respectively (Fig. 2b, c) together with the initial rise in cortisol level after SW exposure indicate a state of stress. Increased plasma cortisol following seawater transfer has previously been observed in killifish (F. heteroclitus) (Jacob and Taylor 1983; Marshall et al. 1999) and tilapia (O. mossambicus) (Kammerer et al. 2010). Since acute stress is an energy-consuming process as evidenced by the stress-induced increases in metabolic rate and oxygen uptake in fish (Barton 2002), the first peak of cortisol in response to acute stress from salinity change might play an important role in a rapid production of glucose, which could be used as an energy source for cell metabolism (Soivio et al. 1981; Mommsen 1984). The rapid elevation of plasma glucose level after hyperosmotic exposure, suggests that glycogenolysis—known to be enhanced by cortisol (Vijayan et al. 1997; Mommsen et al. 1999)—contributed to the rapid provision of glucose. Such cortisol action appeared to be non-genomic, and probably involved alteration in the phosphorylation-dephosphorylation status of glycogen phosphorylase (Gomez-Munoz et al. 1989). However, since this hyperglycemia was transient, gluconeogenesis that took longer time was not involved in providing glucose during saltwater exposure (van der Boon et al. 1991; Wendelaar Bonga 1997). Meanwhile, during exposure to environmental salinities, an increase in oxygen consumption for branchial ATP production often occurred to stimulate pumps and ion transporters (Chang et al. 2007; Tseng et al. 2007), consistent with the present finding that Na+/K+-ATPase was activated. The enhanced ATP production through glycolysis might eventually lead to excessive lactate production.
The second phase of cortisol release after being exposed to SW could be directly associated with the long-lasting osmoregulatory mechanism. We observed that after the snakehead were exposed to SW, the plasma osmolality continued to increase during the initial phase (1–72 h) and then remained high (~380 mOsm kg−1 H2O) thereafter until the end of the experiment (Fig. 2b) coincidently with the second cortisol surge (Fig. 2a). In addition, the plasma osmolality of the 4-week SW-acclimated fish was ~380 mOsm kg−1 H2O (Fig. 5b, at 0 h). These results indicated that fish could adjust the osmoregulatory variables (i.e., plasma osmolality and ion concentrations) to a new homeostatic level. Since increase in plasma osmolality paralleled increases in the plasma Na+ and Cl− levels, the hyperosmotic plasma was likely to result from influx of Na+ and Cl−. An increase in plasma osmolality was also evident in other stenohaline species (De Boeck et al. 2000; Eckert et al. 2001; Tam et al. 2003). For example, in goldfish exposed to 10 ‰ salinity (~284 mOsm kg−1 H2O), plasma osmolality can reach up to ~350 mOsm kg−1 H2O (Luz et al. 2008).
Cortisol has been reported to directly activate Na+/K+-ATPase in several teleost species, such as Oncorhynchus kisutch (Björnsson et al. 1987), Anguilla rostrata (Butler and Carmichael 1972), O. mossambicus (Dange 1986), and F. heteroclitus (Pickford et al. 1970). In addition, a decrease in the gill Na+/K+-ATPase activity in hypophysectomized killifish (F. heteroclitus) could be restored by cortisol supplementation (Pickford et al. 1970). In vitro treatment of primary gill tissue culture of coho salmon with cortisol (O. kisutch) was also found to increase Na+/K+-ATPase activity in a dose-dependent manner (McCormick and Bern 1989). Taken together, the osmoregulatory adaptation in SW-acclimated snakehead, which occurred about ~3 days after high salinity exposure, triggered the release of cortisol and activated Na+/K+-ATPase activity for body adjustment to the new homeostasis.
When SW-acclimated snakehead fish were transferred to fresh water, they exhibited a rapid ion loss, leading to acute stress, as indicated by elevated plasma cortisol and glucose. The rapid loss of ions was a necessary osmoregulatory mechanism to maintain plasma ion concentrations. The energy required to drive Na+ uptake in fresh water can be generated by both V-type H+-ATPase and Na+/K+-ATPase. If external Na+ concentration is in the 1 mmol L−1 range, the energy requirement can be solely generated by Na+/K+-ATPase (Kirschner 2004). However, the contributions of these pumps to generate electrochemical gradient vary with tissues, cell types, and expression patterns of the two transporters. For example, in frog skin, Na+/K+-ATPase in the granular cells is the main transporters to generate the gradient for Na+ uptake, while V-type H+-ATPase in the chloride cells works in concert with Na+/K+-ATPase (Ehrenfeld and Klein 1997). In the present study, the snakehead fish showed high Na+/K+-ATPase activity throughout the 15 days (360 h) post-transfer. Glucose could be used to energize the branchial Na+/K+-ATPase in snakehead.
Several investigations suggested that cortisol played a role in ion uptake in freshwater- and brackish-water adapted fish by increasing Na+/K+-ATPase density in the gill chloride cells (Laurent and Perry 1990; Dang et al. 2000; Eckert et al. 2001). A number of studies have also shown upregulation of Na+/K+-ATPase activity in freshwater-acclimated fish (Ciccotti et al. 1994; Woo and Chung 1995; Kelly et al. 1999; Lin et al. 2003). Therefore, it was not surprising to observe high Na+/K+-ATPase activity in both FW–SW and SW–FW adaptations in the snakeheads. However, the transient elevation of cortisol observed in the SW–SW group (1 h after exposure) could have resulted from handling stress during water exchange, and the elevated level was much smaller than that in the SW–FW group. Similar findings regarding handling stress were also reported in killifish (Scott et al. 2004), tilapia and jundiá (Barcellos et al. 2011). Indeed, stressors of various causes, such as sudden water temperature change, pollutants, and handling, have been reported to increase cortisol release, passive ion influx, and water loss in many fish species (Wendelaar Bonga and Lock 1992).
Meanwhile, consistent with findings in O. mossambicus (Morgan et al. 1997), plasma K+ level did not change significantly after exposure to different salinity levels. This was probably due to the lower gradient of K+ concentration between the blood (8.42 ± 1.14 mmol L−1) in freshwater-acclimated fish and salt water (ranging 0–0.3 mmol L−1) compared to those of Na+ and Cl−. Exchange of K+ between plasma and the intracellular compartment could also prevent fluctuation in the plasma K+ level (Eddy 1985).
In conclusion, we have provided evidence to explain how snakehead survives in natural water sources with salinity fluctuation. Specifically, the snakehead was capable of living in brackish water (<10 ‰ NaCl) for an extended period of time (i.e., up to 4 weeks, duration for acclimated fish in SW). This stressful condition induced cortisol secretion from the interrenal cells, which, in turn, enhanced the production of glucose, presumably through glycogenolysis and glycolysis, respectively. Glucose further energized Na+/K+-ATPase, that was the important transporter for adaptation to the new condition during FW–SW acclimation. In addition, glucose could generate a driving force for sodium uptake during SW–FW acclimation. Cortisol itself also has a direct stimulatory effect on the Na+/K+-ATPase activity, which, in turn, maintained osmoregulation and ionoregulation in the new level of homeostasis (Björnsson et al. 1987). When SW-acclimated snakehead was placed in fresh water, the plasma osmolality and ion concentrations were restored to normal level, but acute stress was still observed as indicated by transient increases in the plasma cortisol and glucose levels. Thus, the present findings underline the reason why salinity must be monitored and tightly controlled in commercial fish farming even when using natural water sources.
References
Altinok I, Grizzle JM (2001) Effects of low salinities on Flavobacterium columnare infection of euryhaline and freshwater stenohaline fishes. J Fish Dis 24:361–367
Barcellos LJG, Volpato GL, Barreto RE, Coldebella I, Ferreira D (2011) Chemical communication of handling stress in fish. Physiol Behav 103:372–375
Barton BA (2002) Stress in fishes: a diversity of responses with particular reference to changes in circulating corticosteroids. Integr Comp Biol 42:517–525
Björnsson BT, Yamauchi K, Nishioka RS, Deftos LJ, Bern HA (1987) Effects of hypophysectomy and subsequent hormonal replacement therapy on hormonal and osmoregulatory status of coho salmon, Oncorhynchus kisutch. Gen Comp Endocrinol 68:421–430
Bringolf RB, Kwak TJ, Cope WG, Larimore MS (2005) Salinity tolerance of the Flathead Catfish: implications for dispersal of introduced populations. T Am Fish Soc 134:927–936
Butler DG, Carmichael J (1972) (Na+, K+)-ATPase activity in eel (Anguilla rostrata) gills in relation to change in environmental salinity: role of adrenocortical steroids. Gen Comp Endocrinol 19:421–427
Chang EWY, Loong AM, Wong WP, Chew SF, Wilson JM, Ip YK (2007) Changes in tissue free amino acid contents, branchial Na+/K+-ATPase activity and bimodal breathing pattern in the freshwater climbing perch, Anabas testudineus (Bloch), during seawater acclimation. J Exp Zool 307A:708–723
Ciccotti E, Marino G, Pucci P, Cataldi E, Cataudella S (1994) Acclimation trial of Mugil cephalus juveniles to freshwater: morphological and biochemical aspects. Environ Biol Fish 43:163–170
Dang Z, Balm PHM, Flik G, Wendelaar Bonga SE, Lock RAC (2000) Cortisol increases Na+/K+-ATPase density in plasma membranes of gill chloride cells in the freshwater tilapia Oreochromis mossambicus. J Exp Biol 203:2349–2355
Dange AD (1986) Brachial Na+, K+-ATPase activity in freshwater or saltwater acclimated tilapia Oreochromis (Sarotherodon) mossambicus: effects of cortisol and thyroxine. Gen Comp Endocrinol 62:341–343
De Boeck G, Vlaeminck A, Van der Linden A, Blust R (2000) The energy metabolism of common carp (Cyprinus carpio) when exposed to salt stress: an increase in energy expenditure or effects of starvation? Physiol Biochem Zool 73:102–111
De Silva SS (2008) Market chains of non-high value cultured aquatic commodities: case studies from Asia. FAO fisheries and aquaculture circular, no 1032, Rome, FAO, p 46
Eckert SM, Yada T, Shepherd BS, Stetson MH, Hirano T, Grau EG (2001) Hormonal control of osmoregulation in the channel catfish Ictalurus punctatus. Gen Comp Endocrinol 122:270–286
Eddy FB (1985) Uptake and loss of potassium by rainbow trout (Salmo gairdneri) in fresh water and dilute sea water. J Exp Biol 118:277–286
Ehrenfeld J, Klein U (1997) The key role of the H+ V-ATPase in acid-base balance and Na+ transport processes in frog skin. J Exp Biol 200:247–256
El Tabakh M, Utha-Aroon C, Schreiber C (1999) Sedimentology of the Cretaceous Maha Sarakham evaporites in the Khorat Plateau of northeastern Thailand. Sediment Geol 123:31–62
Evans DH (2008) Teleost fish osmoregulation: what have we learned since August Krogh, Homer Smith, and Ancel Keys. Am J Physiol 295:R704–R713
Gomez-Munoz A, Hales P, Brindley DN, Sancho MJ (1989) Rapid activation of glycogen phosphorylase by steroid hormones in cultured rat hepatocytes. Biochem J 262:417–423
Jacob WF, Taylor MH (1983) The time course of seawater acclimation in Fundulus heteroclitus L. J Exp Zool 228:33–39
Kammerer BD, Cech JJ Jr, Kültz D (2010) Rapid changes in plasma cortisol, osmolality, and respiration in response to salinity stress in tilapia (Oreochromis mossambicus). Comp Biochem Physiol 157A:260–265
Kaneko T, Watanabe S, Lee KM (2008) Functional morphology of mitochondrion-rich cells in euryhaline and stenohaline teleosts. Aqua-BioSci Monogr 1:1–62
Kelly SP, Chow INK, Woo NYS (1999) Haloplasticity of black seabream (Mylio macrocephalus): hypersaline to freshwater acclimation. J Exp Zool 282:226–241
Kirschner LB (2004) The mechanism of sodium chloride uptake in hyperregulating aquatic animals. J Exp Biol 207:1439–1452
Laurent P, Perry SF (1990) Effects of cortisol on gill chloride cell morphology and ionic uptake in the freshwater trout, Salmo gairdneri. Cell Tissue Res 259:429–442
Lin YM, Chen CN, Lee TH (2003) The expression of gill Na, K-ATPase in milkfish, Chanos chanos, acclimated to seawater, brackish water and freshwater. Comp Biochem Physiol A 135:489–497
Luz RK, Martínez-Álvarez RM, De Pedro N, Delgado MJ (2008) Growth, food intake regulation and metabolic adaptation in goldfish (Carassius auratus) exposed to different salinities. Aquaculture 276:171–178
Maceina MJ, Shireman JV (1979) Grass carp: effects of salinity on survival, weight loss, and muscle tissue water content. Prog Fish Cult 41:69–73
Madsen SS, Bern HA (1993) In vitro effects of insulin-like growth factor-I on gill Na+/K+-ATPase in coho salmon, Oncorhynchus kisutch. J Endocrinol 138:23–30
Madsen SS, Jensen MK, Nhr J, Kristiansen K (1995) Expression of Na+/K+-ATPase in the brown trout, Salmo trutta: in vivo modulation by hormones and seawater. Am J Physiol 269:R1339–R1345
Marshall WS, Emberley TR, Singer TD, Bryson SE, McCormick SD (1999) Time course of salinity adaptation in a strongly euryhaline estuarine teleost, Fundulus heteroclitus: a multivariable approach. J Exp Biol 202:1535–1544
McCormick SD (1993) Methods for non-lethal gill biopsy and measurement of Na+, K+-ATPase activity. Can J Fish Aquat Sci 50:656–658
McCormick SD (1996) Effects of growth hormone and insulin-like growth factor I on salinity tolerance and gill Na+/K+-ATPase in Atlantic salmon (Salmo salar): interaction with cortisol. Gen Comp Endocrinol 101:3–11
McCormick SD, Bern HA (1989) In vitro stimulation of Na+-K+-ATPase activity and ouabain binding by cortisol in coho salmon gill. Am J Physiol 256:707–715
Mommsen TP (1984) Biochemical characterization of the rainbow trout gill. J Comp Physiol B 154:191–198
Mommsen TP, Vijayan MM, Moon TW (1999) Cortisol in teleosts: dynamics, mechanisms of action, and metabolic regulation. Rev Fish Biol Fish 9:211–268
Morgan JD, Iwama GK (1996) Cortisol-induced changes in oxygen consumption and ionic regulation in coastal cutthroat trout (Oncorhynchus clarki clarki) parr. Fish Physiol Biochem 15:385–394
Morgan JD, Sakamoto T, Grau EG, Iwama GK (1997) Physiological and respiratory responses of the Mozambique tilapia (Oreochromis mossambicus) to salinity acclimation. Comp Biochem Physiol 117A:391–398
Musikasinthorn P (2003) Channoidei (snakeheads). In: Hutchins M, Thoney A, Loiselle PV, Schlager N (eds) Grzimek’s animal life encyclopedia, 2nd edn, vols 4, 5. Fishes I–II. Gale Group, Farmington Hills, pp 437–447
Pedersen PBM, Hansen K, Huong DTT, Bayley M, Wang T (2014) Effects of salinity on osmoregulation, growth and survival in Asian swamp eel (Monopterus albus) (Zuiew 1793). Aquacul Res 45:427–438
Pickford GE, Pang PK, Weinstein E, Torretti J, Hendler E, Epstein FH (1970) The response of the hypophysectomized Cyprinodont, Fundulus heteroclitus, to replacement therapy with cortisol: effects on blood serum and sodium–potassium activated adenosine triphosphatase in the gills, kidney, and intestinal mucosa. Gen Comp Endocrinol 14:524–534
Sarma K, Prabakaran K, Kishnan P, Grinson G, Kumar AA (2013) Response of a freshwater air-breathing fish, Clarias batrachus to salinity stress: an experimental case for their farming in brackishwater area in Andaman, India. Aquacul Int 21:183–196
Scott GR, Richards JG, Forbush B, Isenring P, Schulte PM (2004) Changes in gene expression in gills of the euryhaline killifish Fundulus heteroclitus after abrupt salinity transfer. Am J Physiol Cell Physiol 287:C300–C309
Serrano X, Serafy J, Grosell M (2011) Osmoregulatory capabilities of the gray snapper, Lutjanus griseus: salinity challenges and field observations. Mar Freshw Behav Physiol 44:185–196
Soivio A, Nikinmaa M, Nyholm K, Westman K (1981) The role of gills in the responses of Salmo gairdneri to moderate hypoxia. Comp Biochem Physiol 70A:133–139
Suwannatrai A, Suwannatrai K, Haruay S, Piratae S, Thammasiri C, Khampoosa P, Kulsantiwong J, Prasopdee S, Tarbsripair P, Suwanwerakamtorn R, Sukchan S, Boonmars T, Malone JB, Kearney MT, Tesana S (2011) Effect of soil surface salt on the density and distribution of the snail Bithynia siamensis goniomphalos in northeast Thailand. Geospatial Health 5:183–190
Tam WL, Wong WP, Loong AM, Hiong KC, Chew SF, Ballantyne JS (2003) The osmotic response of the Asian freshwater stingray (Himantura signifer) to increased salinity: a comparison with marine (Taeniura lymma) and amazonian freshwater (Potamotrygon motoro) stingrays. J Exp Biol 206:2931–2940
Tseng YC, Huang CJ, Chang JCH, Teng WY, Baba O, Fann MJ, Hwang PP (2007) Glycogen phosphorylase in glycogen rich cells is involved in the energy supply for ion regulation in fish gill epithelia. Am J Physiol 293:R482–R491
van der Boon J, van den Thillart GEEJM, Addink ADF (1991) The effects of cortisol administration on intermediary metabolism in teleost fish. Comp Biochem Physiol 100A:47–53
Van der Linden A, Vanaudenhove M, Verhoye M, De Boeck G, Blust R (1999) Osmoregulation of the common carp (Cyprinus carpio) when exposed to an osmotic challenge assessed in vivo and non-invasively by diffusion- and T2-weighted magnetic resonance imaging. Comp Biochem Physiol 124A:343–352
Vidthayanon C (2002) Peat swamp fishes of Thailand. Office of Environmental Policy and Planning, Bangkok
Vijayan MM, Morgan JD, Sakamoto T, Grau EG, Iwama GK (1996) Food-deprivation affects seawater acclimation in tilapia: hormonal and metabolic changes. J Exp Biol 199:2467–2475
Vijayan MM, Pereira C, Forsyth RB, Kennedy CJ, Iwama GK (1997) Handling stress does not affect the expression of hepatic heat shock protein 70 and conjugation enzymes in rainbow trout treated with β-naphtoflvone. Life Sci 61:117–127
Wang JQ, Lui H, Po H, Fan L (1997) Influence of salinity on food consumption, growth and energy conversion efficiency of common carp (Cyprinus carpio) fingerlings. Aquaculture 148:115–124
Wendelaar Bonga SE (1997) The stress response in fish. Physiol Rev 7:591–625
Wendelaar Bonga SE, Lock RAC (1992) Toxicants and osmoregulations in fish. Neth J Zool 42:478–493
Wilkes PRH, McMahon BR (1986) Responses of a stenohaline freshwater teleost (Catostomus commersoni) to hypersaline exposure. J Exp Biol 121:77–94
Woo NYS, Chung KC (1995) Tolerance of Pomacanthus imperator to hypoosmotic salinities: changes in body composition and hepatic enzyme activities. J Fish Biol 47:70–81
Acknowledgments
The authors thank Prof. Nateetip Krishnamra for proofreading of the manuscript, and Dr. Panan Suntornsaratoon for the excellent technical assistance. This work was supported by a grant from the Thailand Research Fund (TRF), the Office of the Higher Education Commission, and Khon Kaen University (MRG5580008 to L. Nakkrasae). N. Charoenphandhu is the TRF Senior Research Scholar (RTA5780001) awarded by Thailand Research Fund and Mahidol University.
Conflict of interest
The authors declare no conflicts of interest.
Author information
Authors and Affiliations
Corresponding author
Additional information
Communicated by G. Heldmaier.
Rights and permissions
About this article
Cite this article
Nakkrasae, Li., Wisetdee, K. & Charoenphandhu, N. Osmoregulatory adaptations of freshwater air-breathing snakehead fish (Channa striata) after exposure to brackish water. J Comp Physiol B 185, 527–537 (2015). https://doi.org/10.1007/s00360-015-0902-z
Received:
Revised:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s00360-015-0902-z