AJP - Regu AJP: Advances in Physiology Education
HOME HELP FEEDBACK SUBSCRIPTIONS ARCHIVE SEARCH TABLE OF CONTENTS
 QUICK SEARCH:   [advanced]


     


Am J Physiol Regul Integr Comp Physiol 292: R2048-R2058, 2007. First published February 1, 2007; doi:10.1152/ajpregu.00640.2006
0363-6119/07 $8.00
This Article
Right arrow Abstract Freely available
Right arrow Full Text (PDF)
Right arrow All Versions of this Article:
292/5/R2048    most recent
00640.2006v1
Right arrow Alert me when this article is cited
Right arrow Alert me if a correction is posted
Right arrow Citation Map
Services
Right arrow Email this article to a friend
Right arrow Similar articles in this journal
Right arrow Similar articles in ISI Web of Science
Right arrow Similar articles in PubMed
Right arrow Alert me to new issues of the journal
Right arrow Download to citation manager
Citing Articles
Right arrow Citing Articles via ISI Web of Science (1)
Right arrow Citing Articles via Google Scholar
Google Scholar
Right arrow Articles by Wood, C. M.
Right arrow Articles by Val, A. L.
Right arrow Search for Related Content
PubMed
Right arrow PubMed Citation
Right arrow Articles by Wood, C. M.
Right arrow Articles by Val, A. L.

COMPARATIVE AND EVOLUTIONARY PHYSIOLOGY

Rapid regulation of Na+ fluxes and ammonia excretion in response to acute environmental hypoxia in the Amazonian oscar, Astronotus ocellatus

Chris M. Wood,1,2 Makiko Kajimura,1 Katherine A. Sloman,3 Graham R. Scott,4 Patrick J. Walsh,2,5 Vera M. F. Almeida-Val,6 and Adalberto L. Val6

1Department of Biology, McMaster University, Hamilton, Ontario, Canada; 2Division of Marine Biology and Fisheries, Rosenstiel School of Marine and Atmospheric Science, University of Miami, Miami, Florida; 3School of Biological Sciences, University of Plymouth, Devon, United Kingdom; 4Department of Zoology, University of British Columbia, Vancouver, Canada; 5Department of Biology, University of Ottawa, Ottawa, Ontario, Canada; and 6Laboratory of Ecophysiology and Molecular Evolution, Instituto Nacional de Pesquisas da Amazônia, Manaus, Brazil

Submitted 12 September 2006 ; accepted in final form 28 January 2007


    ABSTRACT
 TOP
 ABSTRACT
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 GRANTS
 REFERENCES
 
The Amazonian oscar is extremely resistant to hypoxia, and tolerance scales with size. Overall, ionoregulatory responses of small (~15 g) and large oscars (~200 g) to hypoxia were qualitatively similar, but the latter were more effective. Large oscars exhibited a rapid reduction in unidirectional Na+ uptake rate at the gills during acute hypoxia (PO2 ~10 mmHg), which intensified with time (7 or 8 h); Na+ efflux rates were also reduced, so net balance was little affected. The inhibitions were virtually immediate (1st h) and preceded a later 60% reduction (at 3 h) in gill Na+-K+-ATPase activity, reflected in a 60% reduction in maximum Na+ uptake capacity without change in affinity (Km) for Na+. Upon acute restoration of normoxia, recovery of Na+ uptake was delayed for 1 h. These data suggest that dual mechanisms may be involved (e.g., immediate effects of O2 availability on transporters, channels, or permeability, slower effects of Na+-K+-ATPase regulation). Ammonia excretion appeared to be linked indirectly to Na+ uptake, exhibiting a Michaelis-Menten relationship with external [Na+], but the Km was less than for Na+ uptake. During hypoxia, ammonia excretion fell in a similar manner to Na+ fluxes, with a delayed recovery upon normoxia restoration, but the relationship with [Na+] was blocked. Reductions in ammonia excretion were greater than in urea excretion. Plasma ammonia rose moderately over 3 h hypoxia, suggesting that inhibition of excretion was greater than inhibition of ammonia production. Overall, the oscar maintains excellent homeostasis of ionoregulation and N-balance during severe hypoxia.

teleost fish; ionoregulation; nitrogen metabolism; sodium-potassium-ATPase; ion channels


THE PRESENT STUDY USES the hypoxia-tolerant oscar (acará-açu; Astronotus ocellatus), an entirely water-breathing Amazonian cichlid, to examine the effects of low environmental O2 on two key aspects of gill function, ionoregulation and nitrogenous waste excretion. The oscar commonly encounters hypoxia in its natural environment when it enters the seasonally flooded jungle to feed and reproduce; adults are reported to survive up to 6 h of complete anoxia and can tolerate levels of 5–20% air saturation for 20–50 h (1, 2, 32). There are several reasons for believing that ionic balance and ammonia excretion may be particularly sensitive to hypoxia in freshwater fish, but to date, these areas have received little experimental attention.

First, the respiratory-osmoregulatory compromise at the gills has been well documented in exercise studies on several teleost species: the effective gill area and diffusion distance are adjusted as a trade-off between providing the permeability required for gas exchange, while minimizing diffusive ion losses and osmotic water gain (12, 13, 57, 58). During environmental hypoxia, it is probable that similar lamellar recruitment and decreased diffusion distance occurs to help sustain O2 uptake (17, 18) because gill O2 transfer factor, an index of effective O2 permeability, increases markedly in both hypoxia and exercise (36). We therefore hypothesized that increases in diffusive Na+ loss rates to the water and a possible reduction of plasma ion levels would also occur.

Secondly, ionoregulation is a costly process in freshwater fish, with estimates generally falling in the range of 2–20% of resting metabolism at the whole animal level (reviewed in Ref. 11). The very dilute nature of many Amazonian waters ("slightly contaminated distilled water;" 41) may exacerbate these costs, and a general tendency for reduced ion levels in the plasma of Amazonian teleosts has been noted (28). In other fish, the rate of O2 utilization by artificially perfused and ventilated gill tissue amounts to about 4–12% of resting O2 uptake by the whole animal (26, 31, 59), that is, in the same range as estimates of the costs of ionoregulation. About half of this O2 used by gill cells comes directly from the water, and the other half comes from the perfusate or blood, which itself has just been oxygenated in the arterial-arterial pathway of the gill lamellae before reaching the ionocytes (33, 52). Thus gill ionocytes will be on the front line of hypoxia exposure and the very first cells to experience an O2 deficit during environmental hypoxia. By way of analogy, in neural cells, the cost of ion pumping appears to be second only to that of protein synthesis, and both processes are markedly turned down during hypoxia in model species, such as the turtle and crucian carp, which are capable of severe hypometabolism (reviewed in Refs. 6, 7, and 19). Therefore, we hypothesized that active Na+ influx rates from the water could fall during hypoxia for two reasons: 1) as a direct response to O2 starvation of the working ionocytes and 2) as a result of downregulation of uptake channels and/or Na+-K+-ATPase activity to save metabolic costs.

Third, if ion transport processes are affected by hypoxia, ammonia excretion might be affected as well. The gills excrete more than 80% of the metabolic ammonia production in fish, and the mechanism is thought to be linked in some way to the active uptake of Na+ (see Refs. 50, 51, 53, 56 for a review). Original ideas about direct Na+/NH4+ exchange coupling in the gill cells (e.g., 21, 27, 60), while not entirely disproven, have given way in recent years to the concept that the coupling is indirect (3, 25, 34). Thus an H+ pump on the apical membrane provides the electrical gradient needed to drive Na+ uptake from the water through coupled Na+ channels, and the associated acidification of the gill boundary layer enhances the "diffusion-trapping" of NH3 as NH4+, thus sustaining the PNH3 gradient for diffusive NH3 efflux (9, 54). We, therefore, hypothesized that if hypoxia interferes with the Na+ uptake-H+ pumping mechanism (or Na+/NH4+ exchange), ammonia excretion would be inhibited, and/or uncoupled from Na+ uptake. However, the situation is complicated by the fact that the rate of metabolic ammonia (and urea) production may also be reduced by down-regulation of aerobic metabolism (i.e., less deamination of amino acids for fuel; Refs. 47 and 48), though at least one study has shown an increase in ammonia production during hypoxia (22). Regardless, metabolic rate depression per se is another reason to suspect that ammonia excretion could be sensitive to hypoxia. Therefore, we also measured plasma ammonia levels as an indicator of whether the excretion processes or the production processes were altered to the greater extent, as well as changes in urea excretion as a general indicator of N-metabolism during hypoxia.

In addition to the effects of hypoxia on ion balance and ammonia excretion in general, we explored the influence of body size. Large oscars are more tolerant of hypoxia than small oscars, in contrast to the pattern in many other teleost species (e.g., 8, 38, 43). Large oscars possess lower mass-specific MO2s and a greater aerobic ability to sustain MO2 during hypoxia (i.e., lower PO2crit; Ref. 42), a much greater anaerobic capacity (2), and different behavioral responses (42). We therefore looked for possible qualitative or quantitative differences between large and small fish in Na+ and ammonia flux responses to hypoxia.


    MATERIALS AND METHODS
 TOP
 ABSTRACT
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 GRANTS
 REFERENCES
 
Experimental animals. Oscars (Astronotus ocellatus) in two weight ranges ("small": 10–25 g and "large": 130–260 g) were obtained from Sítio dos Rodrigues (Km 35, Rod. AM-010, Manaus, Brazil) in August 2004. The fish were transferred to the Ecophysiology and Molecular Evolution Laboratory at the Instituto Nacional de Pesquisas da Amazônia (INPA), Manaus, Amazonas, Brazil and held in 500-liter outdoor tanks at 28 ± 3°C with a natural photoperiod; 50% of the water was exchanged every 2 days. The holding and experimental water was typical Amazonian soft water taken from a well on the INPA campus (Na+ = 19, Cl = 21, K+= 16, Ca2+ = 11, Mg2+ = 2 µmol/l, pH = 6.5, dissolved organic carbon = 0.6 mg C/l). The fish were fed daily with commercial pellets, but feeding was suspended 2 days before experimentation. All experimental procedures complied with Brazilian and INPA animal care regulations.

Experimental protocols. Experimental temperature was 28 ± 1.5°C, and the same soft water was used in all trials. Most experimental protocols consisted of exposing the fish (n = 5–9 per experiment) to various O2 regimes, while simultaneously measuring unidirectional Na+ fluxes with 22Na (manufactured by New England Nuclear-Dupont, Boston, MA, and supplied by REM, Sâo Paulo, Brazil) and net ammonia and urea fluxes. Experimental chambers for large fish were 2.5-liter sealable Nalgene kitchen cutlery containers mounted on their sides; the horizontally flattened shape fitted the morphology of the fish. For small fish, 700-ml Nalgene beakers with sealable lids were employed. The chambers were shielded with black plastic to minimize visual disturbance and fitted with individual water lines for flushing, and air-stones for air or N2 gassing. The chambers were 80% submerged in a flowing water bath to maintain the experimental temperature of 28 ± 1.5°C. Fish were placed in these individual containers the evening before an experiment and left overnight to settle with flow-through flushing and continuous aeration.

At the start of a standard experiment, the water flow was stopped but aeration continued, and an aliquot of 22Na (typically 2 µCi/l) was added to each container and allowed to equilibrate for 1 h. Water samples (4 x 5 ml for 22Na, total Na+, ammonia, and urea measurements) were taken at the start of the experiment (0 h) and at subsequent 1-h intervals up to 7 h, when the experiment was terminated and the animal was weighed. During this period, the O2 regime was experimentally manipulated by vigorous gassing with either air or N2, followed by more gentle gassing for maintenance. Tests demonstrated that PO2 changes were complete within 10 min, so water PO2 was routinely monitored (1-ml samples) at the midpoint of each 1-h flux. The overall 7-h measurement period was chosen so as to avoid the need to perform correction for back flux of the radioisotope, with its attendant uncertainties (cf. 20, 55). Theoretical calculations, confirmed by blood samples in preliminary trials, indicated that internal specific activity reached only 2–6% of external specific activity by this time, below the threshold (10%), in which back-flux correction would become necessary.

One exception to this basic protocol occurred in an experiment with large oscars, where fluxes were measured over a 3-h period, which included 1 h of normoxia and the first 2 h of hypoxia, and then again at 7–9 h of hypoxic exposure. The external radioisotope concentration was tripled at 6 h of hypoxia so as to avoid a back-flux problem. A second exception occurred in kinetic flux experiments with large oscars, in which the concentration dependence of Na+ uptake was measured at successively higher external Na+ concentrations in five steps over an 11-h period (cf. 55). In these experiments, 22Na and "cold" Na+ were raised in direct proportion to one another by adding aliquots of a 22Na-labeled 180 mmol/l NaCl solution in a geometrically increasing series. At each concentration, a 0.5-h mixing period was followed by a 1-h to 2-h period of flux measurement. Similar experiments were attempted with small oscars, but the higher volume-to-mass ratio used precluded accurate Na+ uptake measurements at higher Na+ concentrations, so only ammonia flux data from the latter experiments have been reported.

One experimental series focused on terminal blood and tissue sampling. Large oscars were set up in their individual containers exactly as during flux tests, but 22Na was not added. A typical O2 regime of normoxia, followed by 3 h of severe hypoxia and 3 h of normoxia restoration was implemented. Fish (n = 7 per sampling point) were rapidly killed with a lethal dose of benzocaine (0.5 g/l; Sigma, St. Louis, MO) during normoxia, after 1 and 3 h of severe hypoxia, and after 1 and 3 h of normoxia restoration. In this series, water PO2 was measured at each sampling time and also at 10 min after the changes from normoxia-to-hypoxia and from hypoxia-to-normoxia. Blood samples (1 ml) were taken by caudal venipuncture, and then samples of gill filaments and epaxial white muscle were excised. Plasma and tissue samples were snap-frozen in liquid N2 and stored at –80°C for later analysis.

Finally, a separate experimental series using an identical normoxia-hypoxia-normoxia regime and duplicating the exact conditions used during the flux and tissue sampling experiments was carried out with five large oscars. Water pH was monitored at 30-min intervals throughout to ensure that it was not a confounding factor in interpretation of results.

Analytical techniques and calculations. Water PO2 was monitored by injecting 1-ml samples into an O2 electrode (Radiometer-Copenhagen, Denmark) thermostatted to the experimental temperature and connected to a Cameron OM-200 oxygen meter (Cameron Instruments, Port Aransas, TX). Water pH was monitored with a Radiometer GK24O1C combination electrode suitable for use in ion-poor water. Water total ammonia (salicylate hypochlorite assay; Ref. 49) and urea concentrations (diacetyl monoxime assay; Ref. 35) were determined colorimetrically. 22Na activities in water samples were measured via liquid scintillation counting (LS6500, Beckman Coulter, Fullerton, CA) on 5-ml water samples added to 5-ml of Packard Ultima Gold AB fluor (Perkin Elmer, Wellesley, MA). Tests demonstrated that quenching was constant, so no correction was necessary. Water total Na+ concentrations were measured using flame atomic absorption spectrophotometry (AAnalyst 800, Perkin Elmer). Na+ influx rates (JNain, by convention positive) were calculated from the mean external specific activity, and the disappearance of counts from the external water (factored by time, volume, and fish mass); Na+ net flux rates (JNanet) were calculated from the change in total Na+ concentration in the water (similarly factored); and Na+ unidirectional efflux rates (JNaout, by convention negative) were calculated by difference, as outlined in detail by Wood (55). This approach makes no assumptions about steady state and allows for comparisons of different treatments over time. Net flux rates of ammonia (JAmm) and urea (JUrea) were calculated as for JNanet. In kinetic analyses, the coordinates of the Michaelis-Menten equation (Km, Jmax) and their SE estimates were fitted by nonlinear regression using Sigmaplot 8.

Plasma samples were analyzed for Na+, Ca2+, Mg2+ (all by atomic absorption spectrophotometry using a Varian SpectrAA-220FS; Varian, Mulgrave, Australia), Cl by coulometric titration (CMT10, Radiometer-Copenhagen, Denmark), total ammonia by the glutamate dehydrogenase method (Raichem, Ammonia Reagent, Product No. 85446, Columbia, MD), cortisol by radioimmunoassay (ICN Pharmaceuticals, Costa Mesa, CA), and glucose and lactate by standard enzymatic assays (10, 37). Muscle samples were similarly analyzed for lactate, but some samples were lost due to accidental thawing. Gill Na+-K+-ATPase activity was determined by the microplate method of McCormick (29) and normalized to total protein content (measured using the bicinchoninic acid method; Sigma).

All data are reported as means ± SE (n = number of fish). Relationships were assessed by 1-way ANOVA followed by the Bonferroni multiple comparison test for independent data or Dunnett's multiple comparison test for paired data, as appropriate, to determine when values became significantly different from reference means. A significance level of P ≤ 0.05 was used throughout.


    RESULTS
 TOP
 ABSTRACT
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 GRANTS
 REFERENCES
 
Large vs. small oscars. The Na+ and ammonia flux responses of large vs. small oscars to hypoxia were qualitatively similar and differed only in quantitative detail. Therefore, responses of large oscars have been generally presented. Interestingly, under normoxia, unidirectional Na+ flux rates (JNain and JNaout) were of similar magnitude on a mass-specific basis in small vs. large fish (e.g., Fig. 1, B and E), whereas mass-specific JAmm and JUrea were several-fold higher in small oscars (e.g., Fig. 1, C and F). Large oscars were also generally closer to achieving Na+ balance (i.e., JNanet close to zero, Fig. 1F), whereas small oscars usually exhibited negative JNanet (Fig. 1B). Negative balance is typical of Amazonian fish in ion-poor native waters, and it is probable that the deficit is normally supplied by dietary Na+ (15, 16). The oscars had been fasted 2 days before test. Our initial intention was to expose both small fish and large fish to the same severity of hypoxia (~10 mmHg; e.g., Fig. 1D), but in preliminary experiments, it was found that some small oscars succumbed at this level, so a less severe hypoxia (~20 mmHg) was used for the latter (e.g., Fig. 1A).


Figure 1
View larger version (28K):
[in this window]
[in a new window]

 
Fig. 1. The responses of small oscars (A, B, C; n = 5) and large oscars (D, E, F; n = 7) to an acute induction of severe hypoxia for 3 h followed by an acute restoration of normoxia. (A, D) Water O2 tension; (B, E) Na+ unidirectional influx (JNain, upward bars), Na+ efflux (JNaout, downward bars), and Na+ net flux rates (JNanet hatched bars); and (C, F) net excretion rate of ammonia (JAmm). Values are expressed as means ± SE. *P ≤ 0.05 relative to the mean value of the first 3 h (normoxia).

 
Na+ flux responses to hypoxia and normoxic recovery. In the first hour of severe hypoxia exposure, large oscars exhibited significant declines of about 50% in both JNain and JNaout, such that JNanet was little affected, and the responses persisted through 3 h of hypoxia (Fig. 1E). Similar responses were seen in small oscars, but developed more slowly (Fig. 1B). Upon return to normoxia, the inhibition of both JNain and JNaout persisted over the first hour in both size groups, despite the restoration of normal water PO2 (Fig. 1, B and E). In view of the 7-h limitation dictated by radioisotopic back-flux considerations, only the first hour of normoxic recovery was examined in the experiments of Fig. 1. Therefore, separate experiments were performed in which flux measurements started during severe hypoxia and continued for 4 h of normoxic recovery. These trials confirmed that JNa in remained depressed during the first hour of normoxic recovery but was fully restored throughout the subsequent 3 h of normoxia (Fig. 2B). In the large fish experiment shown in Fig. 2B, JNaout was not significantly depressed during the first hour of normoxic restoration, in contrast to both the large fish and small fish experiments in Fig. 1, E and B, respectively. However, in a comparable small fish experiment (not shown), both JNaout and JNain remained low during the first hour of return to high PO2 (as in Fig. 1B) and then increased to stable, typical normoxic values thereafter. Thus there was some variability in the rate of JNaout recovery.


Figure 2
View larger version (17K):
[in this window]
[in a new window]

 
Fig. 2. The responses of large oscars (n = 8) to acute restoration of normoxia after 3 h of acute exposure to severe hypoxia. A: water O2 tension. B: JNain, upward bars, JNaout (downward bars), and JNanet (hatched bars) of Na+. C: JAmm. Values are expressed as means ± SE. +P ≤ 0.05 relative to the mean value of the first 3 h (severe hypoxia).

 
The experiment performed with large oscars and water pH measurements at 30-min intervals demonstrated that water pH did not change appreciably during the hypoxic regime. Representative data (n = 5) are normoxia, 6.75 ± 0.06; hypoxia, –1 h, 6.97 ± 0.13; hypoxia –3 h, 7.14 ± 0.10; normoxia restoration –1 h, 6.75 ± 0.07; normoxia restoration –3 h, 6.91 ± 0.08.

An experiment was carried out with large fish to determine whether the inhibition of JNain and JNaout would persist during prolonged hypoxia. Indeed, the responses appeared to intensify over time, such that the reduction of JNain was greater at 7 and 8 h of severe hypoxia than it had been at 1 h and 2 h (Fig. 3B). Similarly, the reduction of JNaout was also greater, at least at 8 h.


Figure 3
View larger version (17K):
[in this window]
[in a new window]

 
Fig. 3. The responses of large oscars (n = 5) to prolonged exposure to severe hypoxia. Flux measurements were made during the first 2 h of acute exposure, and then again at 7 and 8 h of prolonged exposure. A: water O2 tension. B: JNain (upward bars), JNaout (downward bars), and JNanet (hatched bars) of Na+. C: JAmm. Values are expressed as means ± SE. *P ≤ 0.05 relative to the normoxia value of the first hour. +P ≤ 0.05 relative to the mean value of the first 2 h of severe hypoxia.

 
As a step change to severe hypoxia may not be environmentally realistic, experiments were performed in which the water PO2 was allowed to fall more gradually. The same reductions in JNain and JNaout were seen, with the first significant decreases occurring at a threshold PO2 of about 40 mmHg in large fish (Fig. 4B). Small fish exhibited very similar responses, although the first significant reductions in JNain and JNaout did not occur until a threshold of about 20 mmHg (not shown). Notably, in all of these responses (Figs. 14), reductions in JNain and JNaout were of similar magnitude, so JNanet was little affected.


Figure 4
View larger version (17K):
[in this window]
[in a new window]

 
Fig. 4. The responses of large oscars (n = 7) to a gradual induction of severe hypoxia. Aeration was stopped after the first 2 h (normoxia control period), and the O2 tension was allowed to fall gradually over the following 4 h. A: water O2 tension. B: JNain (upward bars), JNaout (downward bars), and JNanet (hatched bars) of Na+. C: JAmm. Values are expressed as means ± SE. *P ≤ 0.05 relative to the mean value of the first 2 h (normoxia).

 
Kinetic analysis of the concentration dependence of Na+ uptake was performed only for large oscars. Under normoxia (PO2 = 144 ± 3 mmHg), the relationship exhibited typical Michaelis-Menten saturation kinetics (Fig. 5A). Under hypoxia (PO2 = 17.0 ± 0.9 mmHg), the Michaelis-Menten relationship persisted, but the position of the curve exhibited a marked downward shift. Jmax was significantly reduced by about 60% during hypoxia (from 502 ± 128 to 218 ± 26 µmol·kg–1·h–1), but Km was not significantly altered (780 ± 252 vs. 470 ± 118 µmol/l). This response suggests that hypoxia acts like a noncompetitive inhibitor, reducing the number (Jmax) of functioning Na+ transport sites.


Figure 5
View larger version (13K):
[in this window]
[in a new window]

 
Fig. 5. A: Michaelis-Menten kinetics of Na+ influx rate (JNain) as a function of external Na+ concentration in large oscars (n = 8) during normoxia and during severe hypoxia. Note the decrease in Jmax without significant change in Km during hypoxia. B: Michaelis-Menten kinetics of JAmm as a function of external Na+ concentration in the same large oscars during normoxia. Note the lack of a Michaelis-Menten relationship during severe hypoxia. Note also the difference in Km, with no difference in Jmax between the JNain relationship (A) and the JAmm relationship (B) in normoxia. Values are expressed as means ± SE.

 
Ammonia flux responses to hypoxia and normoxic recovery. Simultaneous measurement of the ammonia fluxes (Fig. 5B) during the Na+ kinetic analysis (Fig. 5A) demonstrated a strong Michaelis-Menten dependence of JAmm on environmental [Na+] in large oscars during normoxia. The apparent Km (in terms of [Na+]) was 103 ± 20 µmol/l, while Jmax was 434 ± 23 µmol·kg–1·h–1. Notably, this Km value was significantly lower (i.e., higher apparent affinity for environmental [Na+]) than for the JNain relationship in these same fish (780 ± 252 µmol/l), but the Jmax was very similar (502 ± 128 µmol·kg–1·h–1). The difference in Km suggests that any coupling of JNain with JAmm must be indirect.

The kinetic experiment was repeated on the same large oscars 2 days later during hypoxia (PO2 = 17.0 ± 0.9 mmHg). The coupling of JAmm to environmental [Na+] was entirely blocked by hypoxia (Fig. 5B).

Kinetic experiments with small oscars (not shown) demonstrated a very similar relationship between JAmm and environmental [Na+] during normoxia (PO2 = 125 ± 6 mmHg), with an identical Km (122 ± 49 µmol/l) to that in large oscars, but a much larger mass-specific Jmax (1,319 ± 156 µmol·kg–1·h–1), as would be anticipated from allometric considerations. However, JNain values could not be determined in these small fish experiments (see MATERIALS AND METHODS). Notably, the coupling of JAmm to environmental [Na+] was again eliminated by hypoxia (PO2 = 29 ± 4 mmHg).

JAmm was measured in all time-course experiments (e.g., Figs. 14) and invariably declined during hypoxia and increased again after restoration of normoxia. Responses were generally more pronounced in large fish (e.g., Fig. 1, C and F). The trends were therefore qualitatively similar to those in JNain and JNaout, but the relative changes in JAmm were often larger than in the Na+ fluxes, and the time courses of the responses were not always matched, again suggesting that any coupling must be indirect. Thus in the acute and gradual hypoxia exposures of Figs. 3C and 4C, respectively, the initial declines in JAmm lagged behind the initial declines in JNain (Figs. 3B and 4B), but the reductions in JAmm did become more intense over time during prolonged severe hypoxia (Fig. 3C). During the first hour of normoxia restoration, JAmm exhibited either no recovery (e.g., Fig. 1C and an additional small fish experiment not shown) or only partial recovery (e.g., Figs. 1F and 2C), but thereafter was always fully restored to the original normoxia level.

JUrea was also measured in all time course experiments (not shown). As with JAmm, JUrea was several-fold larger on a mass-specific basis in small fish relative to large fish, as expected from allometry. Under normoxia, JUrea was only 10.9 ± 2.5% (n = 34) of JAmm on a per unit N basis, and during hypoxia, declines in JUrea almost always occurred in parallel to declines in JAmm. Thus, as with JAmm, decreases in JUrea were relatively larger in large oscars than in small oscars. However, the relationship between JUrea and JAmm was not one of direct proportionality (Fig. 6). The slope of the regression relating percentage change in urea-N excretion to that in ammonia-N excretion was only 0.57, and the intercept was significantly greater than zero. Therefore, at greater than about 50% inhibition, the relative declines in JAmm were greater than the relative declines in JUrea. Under severe hypoxia, when JAmm was greatly depressed, JUrea was 27.2 ± 5.9% (n = 34) of JAmm on a per unit-N basis.


Figure 6
View larger version (16K):
[in this window]
[in a new window]

 
Fig. 6. The relationship between the mean relative urea-N excretion rate (JUrea, y, as a percentage of the normoxic control value) and the mean relative ammonia-N excretion rate (JAmm, x, as a percentage of the normoxic control value) in individual periods of various hypoxic exposure experiments with large and small oscars. Values are presented as means ± SE (n = 5–9 at each point). The equation of the regression line is y = 0.57 x + 23 (r = 0.75, P ≤ 0.0001).

 
Plasma and tissue responses to hypoxia and normoxic recovery. Large oscars were terminally sampled at various times during a regime consisting of normoxia, 3 h acute severe hypoxia, and 3 h of normoxia restoration (Fig. 7A). There were no declines in plasma electrolytes, and indeed plasma [Na+] and [Cl] increased significantly at 1 h (Fig. 7B), while [Mg2+] increased significantly at both 1 h and 3 h of acute hypoxia (Table 1). The rise in plasma [Ca2+] was not significant (Table 1). All of these changes were reversed during normoxia restoration. Gill Na+-K+-ATPase activity remained unchanged at 1 h but declined by 60% at 3 h of severe hypoxia (Fig. 7C). This depression was completely reversed by 1 h of normoxic recovery. Plasma total ammonia level rose significantly by 45% after 3 h of hypoxia but was similarly corrected by 1 h of normoxic recovery (Fig. 7D).


Figure 7
View larger version (8K):
[in this window]
[in a new window]

 
Fig. 7. Plasma and tissue responses of large oscars (n = 7 at each point) to an acute induction of severe hypoxia for 3 h followed by an acute restoration of normoxia for 3 h. A: water O2 tension. B: plasma Na+ and Cl concentrations. C: gill Na+, K+-ATPase activity. D: plasma total ammonia concentration. Values are presented as means ± SE. *P ≤ 0.05 relative to the normoxic control value (C).

 

View this table:
[in this window]
[in a new window]

 
Table 1. Changes in plasma chemistry of large oscars (Astronotus ocellatus) during 3 h of acute exposure to severe hypoxia, followed by 3 h of acute normoxia restoration

 
Plasma glucose fell by about 40% after 3 h of hypoxia but was no longer significantly depressed at both sampling times after return to normoxia (Table 1). Plasma lactate concentration rose rapidly during severe hypoxia, with 11-fold and 16-fold increases, respectively, after 1 and 3 h of acute exposure (Table 1). Lactate was rapidly cleared from the plasma and was no longer significantly elevated at 1 h after restoration of normoxia. These plasma lactate changes coincided with significant increases in muscle lactate concentration from 7.6 ± 0.8 mmol/kg (n = 7) under normoxia to 17.3 ± 1.9 (n = 7) and 17.4 ± 1.6 mmol/kg (n = 7) at 1 and 3 h of hypoxia, respectively; the normoxic recovery samples were lost. Plasma cortisol exhibited a biphasic pattern, doubling at 1 h of hypoxia and later falling to 50% of the original control level at 1 h of normoxia restoration, before returning to normal after 3 h of recovery (Table 1).


    DISCUSSION
 TOP
 ABSTRACT
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 GRANTS
 REFERENCES
 
Overview. Some of our original hypotheses were supported, but others were not. Active Na+ influx rates from the water (JNain) and ammonia excretion rate (JAmm) were both greatly depressed during hypoxia, and JAmm became uncoupled from JNain. JUrea also fell, indicating a general decrease in N metabolism, although the fall was not as large as in JAmm. In accord, plasma total ammonia concentration rose modestly, suggesting that the ammonia excretion rate was inhibited to a greater extent than the ammonia production rate. However, contrary to our original predictions based on the respiratory-osmoregulatory compromise, JNaout actually decreased rather than increased during hypoxia. As a consequence, JNanet remained largely unchanged, and plasma ion levels did not fall. Factors other than the respiratory-osmoregulatory compromise, such as regulated channel arrest, may instead come into play. In summary, under severe hypoxia, oscars suffer no obvious ionoregulatory imbalance, and only a moderate disturbance of ammonia regulation. In addition to exhibiting impressive adaptations in its behavior, anaerobic potential, and aerobic regulation capacity (1, 2, 32, 42), Astronotus ocellatus is clearly well adapted to maintain ionoregulatory homeostasis and N balance in the severe O2 regimes that are part of its normal lifestyle in the Amazon floodplain.

Small vs. large oscars. Although Na+ influx kinetics were measured only for large oscars, they fit the pattern of relatively high Km (i.e., low Na+ affinity) and low influx and efflux rates (i.e., low permeability) reported for other Amazonian cichlids (reviewed in Ref. 16), very different from the characids, which are abundant in the same environment and which exhibit low Km (i.e., high Na+ affinity) and much higher Na+ turnover rates (14, 15). The cichlid strategy is presumably more economical because it necessitates less active ion pumping. The fact that mass-specific Na+ turnover rates are not greater in small oscars than large oscars in the expected allometric fashion (e.g., Ref. 4) may in itself represent a cost-saving adaptive strategy for these small fish in ion-poor water. However, mass-specific ammonia excretion rates (JAmm) were higher in small fish than in large fish (Fig. 1, C and F), and the differences were relatively larger than in MO2 (42), suggesting that small oscars rely on protein oxidation to a greater extent (23, 47).

The responses to hypoxia, including reductions in JNain, JNaout, JAmm, and JUrea, were qualitatively similar between large and small oscars and differed only in quantitative detail. The reductions in JNain and JNaout during hypoxia became significant more rapidly in large fish (first hour vs. second or third hour), and the inhibitions of JAmm and JUrea were more pronounced than in small fish (Fig. 1). Note, however, that a less severe level of acute hypoxia was used for small fish (~20 vs. ~10 mmHg in large fish) because of their lower hypoxic tolerance. These responses should be interpreted with respect to the metabolic responses of large and small oscars to hypoxia, as determined through respirometry in a parallel study under very similar conditions (42). Sloman et al. (42) reported that MO2 was around 2,200 µmol·kg–1·h–1 under normoxic conditions in large fish and remained stable down to a PO2 of 50 mmHg, where it was significantly depressed (by 26%). In contrast, MO2 was around 4,900 µmol·kg–1·h–1 under normoxia in small oscars and tended to fall progressively as PO2 declined, with the first significant decrease (by 27%) occurring at 70 mmHg. In both large and small fish, MO2 fell steadily with PO2 below these thresholds. On the basis of model equations fitted to these data (42), a 200-g fish would have exhibited a 75% decline in MO2 at 10 mmHg, whereas a 15-g fish would have exhibited a 68% decline at the higher PO2 of 20 mmHg and a 79% decline had 10 mmHg been used.

During the gradual hypoxia trials, in large fish, reductions in both JNain and JNaout first became significant at a threshold PO2 of about 40 mmHg (Fig. 4, A and B; corresponding to a decline in MO2 of only 37%), slightly below the threshold PO2 (PO2crit = 50 mmHg), at which aerobic metabolic rate depression started. This suggests that reduced ion turnover at the gills is part of the strategy for metabolic rate depression in large oscars and is likely regulated in some fashion. However, in small fish, the PO2 threshold for significant reduction in unidirectional Na+ fluxes was about 20 mmHg, corresponding to a 68% decline in MO2, whereas PO2crit was 70 mmHg. In small oscars, physiological regulation may be less developed, so that direct effects of O2 starvation on the gills (with later onset) may be the dominant mechanism. In summary, it appears that large oscars are better able to implement these cost-saving responses more quickly, at a higher PO2, without compromising net Na+ balance, another indicator of their better hypoxia tolerance relative to small oscars (cf. Refs. 2 and 42). Interestingly, Lewis et al. (24) recently reported that protein synthesis rates in the gills of large oscars were reduced by 50% during a comparable hypoxic exposure but recovered without overshoot within 1 h after restoration of normoxia.

Influence of hypoxia on ionoregulation. Contrary to predictions based on the respiratory-osmoregulatory compromise, JNaout and JNanet did not increase, and plasma ions did not fall during severe hypoxia. The situation is very different than during exercise, where increases in MO2 are associated with increases in ion losses in a number of species (12, 13, 57, 58). However, unlike exercise, where MO2 clearly increases, there is a marked decrease in MO2 during hypoxia (32, 42). Gill blood flow changes may be rather different during hypoxia, because in contrast to the overall branchial vasodilation that accompanies exercise, there is a branchial vasoconstriction and an increase in the arterio-venous flow, which returns O2 to the heart (17, 44, 45). At present, we have no evidence that increased lamellar blood flow actually occurs during hypoxia in Astronotus ocellatus. This is an important area for future investigation, as are possible changes in the perfusion of the secondary circulation to the skin, and alterations in the relative surface areas and diffusion distances from water to blood of the gills vs. other parts of the body during the hypoxic exposure.

The only study with a comparable focus is that of Thomas et al. (46), in which rainbow trout, a hypoxia-intolerant species, were acutely exposed to a PO2 of 40 mmHg. Thomas et al. (46) were able to measure net flux rates of Na+ and Cl with the water in only a few trout due to fecal contamination problems but concluded that these remained approximately stable during hypoxia, in accord with the present study. Furthermore, plasma [Na+] and [Cl] actually increased, again in agreement with the present results (Fig. 7B), attributed to a fluid shift into the intracellular compartment (i.e., hemoconcentration), as well as a preferential movement of Na+ into the extracellular fluid to balance the lactate anion. Comparable explanations likely apply for the oscar, as all plasma ions tended to increase, there was a rapid appearance of lactate in the extracellular fluid (Table 1) and a marked rise in muscle lactate occurred (the measured concentration of 17.4 mmol/kg at 1–3 h of hypoxia would have amounted to about 24 mmol/l on an intracellular fluid basis). This rapid response of lactate production, as well as the moderate fall in plasma glucose (Table 1), are in accord with previous reports on the well-developed anaerobic potential of white muscle in large oscars (2, 32). Lactate production from glycogen stores would have driven a shift of fluid out of the extracellular compartment into muscle by osmosis. The rapid appearance of lactate and its equally rapid clearance after return to normoxia may have been associated with the sharp increases and decreases in cortisol at these times (Table 1; see Refs. 10 and 30). Very recently, Richards et al. (37) have reported a detailed biochemical study on Astronotus ocellatus exposed to a similar hypoxic regime and have confirmed many of the trends seen in the present study, including lactate accumulation, glycogen depletion, hemoconcentration, and apparent fluid shift to the intracellular compartment.

Three possible explanations, which are by no means mutually exclusive, come to mind for the observed decreases in JNaout during hypoxia (Figs. 1, B and E, 2B, 3B, and 4B). The first is channel arrest, a well-documented phenomenon at the cellular level in hypoxia-tolerant species (6, 7, 19). If this occurred at the gills, it could reduce both JNain and JNaout, and perhaps also JAmm. The second possibility, a different interpretation of the respiratory-osmoregulatory compromise, is that a hypoxia-tolerant species such as the oscar actually reduces gill area and permeability during severe hypoxia by reducing lamellar perfusion so as to reduce ionoregulatory costs in a situation in which the potential for MO2 uptake from the water has become very slight. This might occur in association with depressed protein synthesis in the gills (24), with a change in the pattern of cardiac output (the well-documented bradycardia without fall in stroke volume) and/or a possible change in circulatory pattern in the gills during hypoxia (17, 18, 44, 45), as discussed earlier. Measurements of water flux across the gills would illuminate whether effective branchial water permeability is turned down in parallel to apparent branchial Na+ permeability, which would support this explanation. The third possibility is that an exchange diffusion transport system occurs at the gills and is turned down during hypoxia, so that the reduced JNaout is directly coupled to the reduced JNain. Exchange diffusion has been seen during normoxia in many freshwater teleosts and crustaceans (e.g., 40, 58), including about half of the Amazonian teleosts surveyed by Gonzalez et al. (15), but to our knowledge, it has never been studied during hypoxia.

In both large and small oscars, JNain declined substantially during hypoxia (Figs. 14), in accord with our original hypothesis that this expensive process would be limited by O2 availability. However, several lines of evidence point to, at least, a partial temporal disconnection between the O2 regime and the simultaneously measured ion fluxes, suggesting that two (or more) mechanisms may be causing the reduction in Na+ turnover during hypoxia.

The first is that in the large fish experiment of Fig. 7C, branchial Na+-K+-ATPase activity was fully maintained at the end of 1 h of hypoxia, despite the fact that Na+ influx and efflux rates had already declined over the first hour in a comparable series (Fig. 1E). Na+-K+-ATPase activity did fall greatly (by about 60%) by 3 h of hypoxia but had fully recovered by 1 h of normoxia reestablishment (Fig. 7C), yet unidirectional flux rates remained depressed during this first hour (Fig. 1E). An important caveat here is the recent demonstration that in trout hepatocytes, low PO2 can reduce the transport activity of Na+-K+-ATPase before its ATP hydrolytic capacity (the parameter measured in the assay) is affected (5). It must be remembered, that Na+-K+-ATPase activity is assayed under optimal conditions in vitro, whereas in vivo, the intracellular milieu of the enzyme may change during hypoxia. This is an important area for future investigation. Second, during prolonged exposure to severe hypoxia, both JNain and JNaout were further reduced at later times (Fig. 3B), again pointing to the involvement of a second mechanism that intensified the effect of the initial inhibition. Third, in the kinetic analysis of JNain, Jmax was significantly depressed by about 60% during prolonged hypoxia (Fig. 5A), as might be expected from the observed 60% reduction in branchial Na+-K+-ATPase activity (Fig. 7C), that is, a reduction in the number of transport sites without a change in their affinity for Na+.

In summary, the data are consistent with downregulation of Na+ influx (and efflux) rates by at least two mechanisms during hypoxia. One is clearly by a delayed reduction in Na+-K+-ATPase hydrolytic activity. Notably, this appears to occur by posttranslational modification of enzyme activity, because specific Na+-K+-ATPase mRNA and protein abundance did not fall in a comparable experiment on Astronotus ocellatus, in which branchial Na+-K+-ATPase hydrolytic activity was depressed by about 50% after 4 h of hypoxia (37). There is also clearly another mechanism(s), which is (are) more rapid and more persistent, but additional work will be required to determine the relative contributions of O2 starvation on Na+-K+-ATPase transport activity, on channel closing, on changes in lamellar perfusion, and on alterations in the activity of other proteins (e.g., H+-ATPase, Na+/H+, and Na+/Na+ exchangers) in the observed responses. Regardless, the bottom line is that Astronotus ocellatus can withstand severe hypoxia without a marked disturbance of internal ion status, by simultaneously reducing Na+ pumping and leak rates at the gills.

The finding that external water pH did not change appreciably during hypoxia, and normoxia restoration demonstrates that the observed decreases in JNain and JNaout during hypoxia, and later increases during normoxic recovery were not an artifact of changing water pH. Furthermore, recent measurements of internal pH during a comparable hypoxia regime in the same species demonstrate that this is not a confounding factor either. Richards et al. (37) reported moderate acidosis of ~0.15 units in both the blood plasma (extracellular fluid) and the white muscle (intracellular compartment) during hypoxia. By standard theory, this moderate internal acidification would be expected to "increase" Na+ influx (by stimulated Na+/H+ exchange, or stimulated H+-ATPase/Na+ channel activity; Refs. 3, 21, 25, 27, 34) so as to correct the acidosis, whereas we observed a "decrease" in Na+ influx during hypoxia.

Influence of hypoxia on ammonia excretion. Ammonia excretion rates (JAmm) were much higher on an absolute basis than Na+ influx rates (JNain) (Figs. 14), so any linkage of JAmm to JNain, if it occurs in the oscar, must be indirect. During normoxia, JAmm exhibited a Michaelis-Menten type dependence on external Na+ concentration (Fig. 5B), but the apparent Km was significantly lower (i.e., affinity for Na+ was higher) than for the simultaneously determined Michaelis-Menten dependence of JNain on external Na+ concentration, whereas the Jmax values were similar (Fig. 5A). Again, this result suggests that the coupling must be indirect rather than through a direct 1:1 Na+/NH4+ exchanger (e.g., 21, 27, 60). Regardless, the coupling is rapidly effective, such that experimental increases in water [Na+] quickly constrain an increase in JAmm. This is not seen in the rainbow trout (39), where arguments have been made for linkage either via a nonobligatory Na+/NH4+ exchanger (39) or via "diffusion-trapping" of NH3-linked to an H+-pump/Na+-channel system (3, 54).

During hypoxia, JAmm was reduced in a similar fashion to JNain and JNaout, and as with these Na+ fluxes, the inhibition became more intense during prolonged hypoxia and usually persisted during the first hour of restoration of normoxia (Figs. 14), again arguing for some sort of common mechanism. However, the responses often differed in exact time course and magnitude, and the apparent kinetic coupling of JAmm to external Na+ concentration was completely lost during prolonged hypoxia (Fig. 5B). It remains to be determined whether the declines in JAmm during hypoxia were driven primarily by a downregulation of the ammonia production rate (47, 48), or by specific hypoxia-induced blockade of the branchial ammonia excretion mechanism (e.g., by down-regulation of a Na+-linked transport system or channel arrest).

For several reasons, it appears likely that both phenomena were involved and that the latter predominated. Urea-N excretion (JUrea), although it represented only a small fraction of N-waste excretion, was reduced whenever JAmm was reduced during hypoxic exposures (Fig. 6). Urea arises from different metabolic pathways than ammonia in teleost fish (uricolysis or arginolysis rather than transdeamination or adenylate breakdown; see Refs. 51 and 56 for reviews). This suggests that a general reduction in metabolic N-waste production occurs during hypoxia, in parallel with depressed protein synthesis in many tissues (24). Likely, oxidation of N-rich fuels is reduced, while carbohydrate utilization is increased during hypoxia in accord with a general suppression of aerobic metabolic rate, reduction in protein turnover, and activation of anaerobic metabolism. However, the relative reduction in JAmm was greater than in JUrea (Fig. 7). Second, if the reduction in JAmm were simply a consequence of reduced production, it seems unlikely that it should persist during the first hour of normoxia restoration when aerobic metabolism was likely restored. And most cogently, plasma total ammonia concentration increased significantly by 3 h of hypoxic exposure (Fig. 7D), suggesting that the excretion mechanism was inhibited to a greater extent than the production mechanism. Nevertheless, the change in plasma ammonia was not large, so again the hypoxia-tolerant oscar appears to be rather good at maintaining internal homeostasis during severe O2 limitation.


    GRANTS
 TOP
 ABSTRACT
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 GRANTS
 REFERENCES
 
Financial support was provided by Natural Sciences and Engineering Research Council of Canada (NSERC) Discovery Grants to C. M. Wood and P. J. Walsh, by a National Research Council (CNPq) of Brazil/Amazon State Research Foundation (FAPEAM) Projects of the Nucleus of Excellence Grant to A. L. Val, and by a U.S. National Science Foundation Grant IOB 0455904 to P. J. Walsh. C. M. Wood and P. J. Walsh are supported by the Canada Research Chair Program and V. M. F. Almeida-Val and A. L. Val are supported by CNPq and FAPEAM and are recipients of research fellowships from CNPq. K. A. Sloman received a travel grant from the Royal Society, and M. Kajimura received travel grants from the Society of Experimental Biology and the American Fisheries Society.


    ACKNOWLEDGMENTS
 
We especially thank Sylvia Wood, Maria de Nazeré Paula da Silva, Gudrun de Boeck, Marisa Fernandes Castilho, Ana Cristina Leite Menezes, Linda Diao, and Sunita Nadella for help with experiments and analyses.


    FOOTNOTES
 

Address for reprint requests and other correspondence: C. M. Wood, Dept. of Biology, McMaster Univ., 1280 Main St. West, Hamilton, ON, Canada L8S 4K1 (e-mail: woodcm{at}mcmaster.ca)

The costs of publication of this article were defrayed in part by the payment of page charges. The article must therefore be hereby marked "advertisement" in accordance with 18 U.S.C. Section 1734 solely to indicate this fact.


    REFERENCES
 TOP
 ABSTRACT
 MATERIALS AND METHODS
 RESULTS
 DISCUSSION
 GRANTS
 REFERENCES
 

  1. Almeida-Val VMF, Hochachka PW. Air-breathing fishes: metabolic biochemistry of the first diving vertebrates. In: Environmental and Ecological Biochemistry, edited by Hochachka PW and Mommsen T. Amsterdam: Elsevier, 1995, p 45–55.
  2. Almeida-Val VMF, Val AL, Duncan WP, Souza FCA, Paula-Silva MN, Land S. Scaling effects on hypoxia tolerance in the Amazon fish Astronotus ocellatus (Perciformes: Cichlidae): contribution of tissue enzyme levels. Comp Biochem Physiol B 125: 219–226, 2000.
  3. Avella M, Bornancin M. A new analysis of ammonia and sodium transport through the gills of the freshwater rainbow trout (Salmo gairdneri). J Exp Biol 142: 155–175, 1989.[Abstract/Free Full Text]
  4. Bianchini A, Grosell M, Gregory SM, Wood CM. Acute silver toxicity in aquatic animals is a function of sodium uptake rate. Environ Sci Technol 36: 1763–1766, 2002.[Medline]
  5. Bogdanova A, Grenacher B, Nikinmaa M, Gassman M. Hypoxic responses of Na+/K+ ATPase in trout hepatocytes. J Exp Biol 208: 1793–1801, 2005.[Abstract/Free Full Text]
  6. Boutilier RG. Mechanisms of cell survival in hypoxia and hypothermia. J Exp Biol 204: 371–381, 2001.
  7. Boutilier RG, St-Pierre J. Surviving hypoxia without really dying. Comp Biochem Physiol 126A: 481–490, 2000.
  8. Burleson ML, Wilhelm DR, Smatresk NJ. The influence of fish size on the avoidance of hypoxia and oxygen selection by largemouth bass. J Fish Biol 59: 1336–1349, 2001.[ISI]
  9. Clarke AP, Potts WTW. Sodium, net acid, and ammonia fluxes in freshwater-adapted European flounder (Platichthys flesus L.). Pharmacological inhibition and effects on gill ventilation volume. J Zool Lond 246: 427–432, 1998.
  10. Eros S, Milligan CL. The effect of cortisol on recovery from exhaustive exercise in rainbow trout: potential mechanisms of action. Physiol Zool 69: 1196–1214, 1996.
  11. Febry R, Lutz P. Energy partioning in fish: the activity-related cost of osmoregulation in a euryhaline cichlid. J Exp Biol 128: 63–85, 1987.[Abstract/Free Full Text]
  12. Gonzalez RJ, McDonald DG. The relationship between oxygen consumption and ion loss in a freshwater fish. J Exp Biol 163: 317–332, 1992.[Abstract/Free Full Text]
  13. Gonzalez RJ, McDonald DG. The relationship between oxygen uptake and ion loss in fish from diverse habitats. J Exp Biol 190: 95–108, 1994.[Abstract]
  14. Gonzalez RJ, Wilson RW. Patterns of ion regulation in acidophilic fish native to the ion-poor, acidic Rio Negro. J Fish Biol 58: 1680–1690, 2001.[CrossRef][ISI]
  15. Gonzalez RJ, Wilson RW, Wood CM, Patrick ML, Val AL. Diverse strategies for ion regulation in fish collected from the ion-poor, acidic Rio Negro. Physiol Biochem Zool 75: 37–47, 2002.[CrossRef][ISI][Medline]
  16. Gonzalez RJ, Wilson RW, Wood CM. Ionoregulation in tropical fish from ion-poor, acidic blackwaters. In: The Physiology of Tropical Fish, Fish Physiology, vol. 22, edited by Val AL, Almeida-Val, VMF, and Randall, DJ. San Diego: Academic, 2005, p 397–437.
  17. Holeton GF, Randall DJ. Changes in blood pressure in the rainbow trout during hypoxia. J Exp Biol 46: 297–305, 1967.[Abstract/Free Full Text]
  18. Holeton GF, Randall DJ. The effect of hypoxia on the partial pressures of gases in the blood and water afferent and efferent to the gills of rainbow trout. J Exp Biol 46: 317–327, 1967.[Abstract/Free Full Text]
  19. Hochachka PW, Lutz PL. Mechanism, origin, and evolution of anoxia tolerance in animals. Comp Biochem Physiol B 130: 435–459, 2001.[CrossRef][Medline]
  20. Kirschner LB. The study of NaCl transport in aquatic animals. Am Zool 10: 365–376, 1970.[ISI][Medline]
  21. Krogh A. Osmotic Regulation in Aquatic Animals. Cambridge, UK: Cambridge University Press, 1939.
  22. Kutty MN. Respiratory quotient and ammonia excretion in Tilapia mossambica. Mar Biol 16: 126–133, 1972.
  23. Lauff RF, Wood CM. Respiratory gas exchange, nitrogenous waste excretion, and fuel usage during starvation in juvenile rainbow trout, Oncorhynchus mykiss. J Comp Physiol [B] 165: 542–551, 1996.[CrossRef][Medline]
  24. Lewis JM, Costa I, Val AL, Almeida-Val AF, Gamperl AK, Driedzic WR. Responses to hypoxia and recovery; Repayment of oxygen debt is not associated with compensatory protein synthesis in the Amazonian cichlid, Astronotus ocellatus. J Exp Biol. In Press.
  25. Lin H, Randall DJ. Proton pumps in fish gills. In: Cellular and Molecular Approaches to Fish Ionic Regulation, edited by Wood CM and Shuttleworth TJ. London: Academic, 1995, p. 229–255.
  26. Lyndon AR. A method for measuring oxygen consumption in isolated perfused gills. J Fish Biol 44: 707–715, 1994.[CrossRef][ISI]
  27. Maetz J, Garcia-Romeu F. The mechanism of sodium and chloride uptake by the gills of a fresh-water fish Carassius auratus. J Gen Physiol 47: 1209–1226, 1964.
  28. Mangum CP, Haswell MS, Johansen K, Towle DW. Inorganic ions and pH in the body fluids of Amazon animals. Can J Zool 56: 907–916, 1978.
  29. McCormick SD. Methods for nonlethal gill biopsy and measurement of Na+,K+ ATPase activity. Can J Fish Aquat Sci 50: 656–658, 1993.
  30. Milligan CL. A regulatory role for cortisol in muscle glycogen metabolism in rainbow trout, Oncorhynchus mykiss Walbaum. J Exp Biol 206: 3167–3173, 2003.[Abstract/Free Full Text]
  31. Morgan JD, Iwama GK. Energy cost of NaCl transport in isolated gills of cuthroat trout. Am J Physiol Regul Integr Comp Physiol 277: R631–R639, 1999.[Abstract/Free Full Text]
  32. Muusze B, Marcon J, van den Thillart G, Almeida-Val VMF. Hypoxia tolerance of Amazon fish respirometry and energy metabolism of the cichlid Astronotus ocellatus. Comp Biochem Physiol A 120: 151–156, 1998.
  33. Olson KR. Gill circulation: regulation of perfusion distribution and metabolism of regulatory molecules. J Exp Zool 293: 320–335, 2002.[CrossRef][ISI][Medline]
  34. Potts WTW. Kinetics of sodium uptake in freshwater animals: A comparison of ion exchange and proton pump hypotheses. Am J Physiol Regul Integr Comp Physiol 266: R315–R320, 1994.[Abstract/Free Full Text]
  35. Rahmatullah M, Boyde TR. Improvements in the determination of urea using diacetyl monoxime: methods with and without deproteinization. Clin Chem Acta 107: 3–9, 1980.[CrossRef][ISI][Medline]
  36. Randall DJ, Holeton GF, Stevens ED. The exchange of oxygen and carbon dioxide across the gills of rainbow trout. J Exp Biol 46: 339–348, 1967.[Abstract/Free Full Text]
  37. Richards JG, Wang YS, Brauner CJ, Gonzalez RJ, Patrick ML, Schulte PM, Chippari-Gomes Almeida-Val VM, Val AL. Metabolic and ionoregulatory responses of the Amazonian cichlid, Astronotus ocellatus, to severe hypoxia. J Comp Physiol B: In Press.
  38. Robb T, Abrahams MV. Variation in tolerance to hypoxia in a predator and prey species: an ecological advantage of being small? J Fish Biol 62: 1067–1081, 2003.[CrossRef][ISI]
  39. Salama A, Morgan IJ, Wood CM. The linkage between sodium uptake and ammonia excretion in rainbow trout—kinetic analysis, the effects of (NH4)2 SO4 and NH4 HCO3 infusion, and the influence of gill boundary layer pH. J Exp Biol 202: 697–709, 1999.[Abstract]
  40. Shaw J. The absorption of sodium ions by the crayfish, Astacus pallipes Lereboullet. I. The effect of external and internal sodium concentrations. J Exp Biol 36: 126–144, 1959.[Abstract]
  41. Sioli H. The Amazon and its main affluents: hydrography, morphology of the river courses, and river types. In: The Amazon: Limnology and Landscape Ecology of a Mighty Tropical River and Its Basin, edited by Sioli H. Dordrecht: Dr. W. Junk Publishers, 1984, p.127–166.
  42. Sloman KA, Wood CM, Scott GR, Wood S, Kajimura K, Johannsson OE, Almeida-Val VM, Val AL. Tribute to R. G. Boutilier: The effect of size on the physiological and behavioural responses of oscar, Astronotus ocellatus, to hypoxia. J Exp Biol 209: 1197–1205, 2006.[Abstract/Free Full Text]
  43. Smale MA, Rabeni CF. Hypoxia and hypothermia tolerances of headwater stream fishes. Trans Am Fish Soc 124: 698–710, 1995.[CrossRef]
  44. Sundin L. Response of the branchial circulation to hypoxia in the Atlantic cod, Gadus morhua. Am J Physiol Regul Integr Comp Physiol 268: R771–R778, 1995.[Abstract/Free Full Text]
  45. Sundin L, Nilsson G. Neurochemical mechanisms behind gill microcirculatory responses to hypoxia in trout: in vivo microscopy study. Am J Physiol Regul Integr Comp Physiol 272: R576–R585, 1997.[Abstract/Free Full Text]
  46. Thomas S, Fievet B, Motais R. Effect of deep hypoxia on acid-base balance in trout: role of ion transfer processes. Am J Physiol Regul Integr Comp Physiol 250: R319–R327, 1986.[Abstract/Free Full Text]
  47. van den Thillart G, Kesbeke F. Anaerobic production of carbon dioxide and ammonia by goldfish, Carassius auratus L. Comp Biochem Physiol 59A: 393–400, 1978.
  48. van Waarde A. Aerobic and anaerobic ammonia production by fish. Comp Biochem Physiol 74B: 675–684, 1983.[CrossRef][Medline]
  49. Verdouw H, van Echted CJA, Dekkers EMJ. Ammonia determination based on indophenol formation with sodium salicylate. Water Res 12: 399–402, 1978.
  50. Wilkie MP. Mechanisms of ammonia excretion across fish gills. Comp Biochem Physiol 118A: 39–50, 1997.
  51. Wilkie MP. Ammonia excretion and urea handling by fish gills: present understanding and future research challenges. J Exp Zool 293: 284–301, 2002.[CrossRef][ISI][Medline]
  52. Wilson JM, Laurent P. Fish gill morphology: inside out. J Exp Zool 293: 192–213, 2002.[CrossRef][ISI][Medline]
  53. Wilson RW. Ammonia excretion in fish adapted to an ion-poor environment. In: Physiology and Biochemistry of the Fishes of the Amazon, edited by Val AL, Almeida-Val VMF, and Randall, DJ. Manaus: INPA, 1996, p. 123–138.
  54. Wilson RW, Wright PM, Munger S, Wood CM. Ammonia excretion in rainbow trout Oncorhynchus mykiss: the importance of gill boundary layer acidification: lack of evidence for Na+/NH4+ exchange. J Exp Biol 191: 37–58, 1994.[Abstract]
  55. Wood CM. Flux measurements as indices of H+ and metal effects on freshwater fish. Aquat Toxicol 22: 239–264, 1992.[CrossRef][ISI]
  56. Wood CM. Ammonia and urea metabolism and excretion. In: The Physiology of Fishes edited by D. Evans, CRC, Boca Raton, pp. 379–425, 1993.
  57. Wood CM, Randall DJ. The influence of swimming activity on sodium balance in the rainbow trout (Salmo gairdneri). J Comp Physiol 82: 207–233, 1973.[CrossRef]
  58. Wood CM, Randall DJ. Sodium balance in the rainbow trout (Salmo gairdneri) during extended exercise. J Comp Physiol 82: 235–256, 1973.[CrossRef]
  59. Wood CM, McMahon BR, McDonald DG. Oxygen exchange and vascular resistance in the totally perfused rainbow trout. Am J Physiol Regul Integr Comp Physiol 234: R201–R208, 1978.[Abstract/Free Full Text]
  60. Wright PA, Wood CM. An analysis of branchial ammonia excretion in the freshwater rainbow trout: effects of environmental pH change and sodium uptake blockade. J Exp Biol 114: 329–353, 1985.[Abstract/Free Full Text]




This Article
Right arrow Abstract Freely available