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First published online February 1, 2008
Journal of Experimental Biology 211, 539-547 (2008)
Published by The Company of Biologists 2008
doi: 10.1242/jeb.009175

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Sodium uptake in different life stages of crustaceans: the water flea Daphnia magna Strauss

Adalto Bianchini^1,* and Chris M. Wood²

¹ Fundação Universidade Federal do Rio Grande, Departamento de Ciências Fisiológicas, Campus Carreiros, Av. Itália s/n, 96.201-900 Rio Grande, RS, Brazil
² McMaster University, Department of Biology, 1280 Main Street West, Hamilton, ON, L8S 4K1, Canada

^* Author for correspondence (e-mail: adalto{at}octopus.furg.br)

Accepted 3 December 2007

	Summary

TOP Summary INTRODUCTION MATERIALS AND METHODS RESULTS DISCUSSION References

 
The concentration-dependent kinetics and main mechanisms of whole-body Na⁺ uptake were assessed in neonate and adult water flea Daphnia magna Strauss acclimated to moderately hard water (0.6 mmol l^–1 NaCl, 1.0 mmol l^–1 CaCO₃ and 0.15 mmol l^–1 MgSO₄·7H₂O; pH 8.2). Whole-body Na⁺ uptake is independent of the presence of Cl^– in the external medium and kinetic parameters are dependent on the life stage. Adults have a lower maximum capacity of Na⁺ transport on a mass-specific basis but a higher affinity for Na⁺ when compared to neonates. Based on pharmacological analyses, mechanisms involved in whole-body Na⁺ uptake differ according to the life stage considered. In neonates, a proton pump-coupled Na⁺ channel appears to play an important role in the whole-body Na⁺ uptake at the apical membrane. However, they do not appear to contribute to whole-body Na⁺ uptake in adults, where only the Na⁺ channel seems to be present, associated with the Na⁺/H⁺ exchanger. In both cases, carbonic anhydrase contributes by providing H⁺ for the transporters. At the basolateral membrane of the salt-transporting epithelia of neonates, Na⁺ is pumped from the cells to the extracellular fluid by a Na⁺,K⁺-ATPase and a Na⁺/Cl^– exchanger whereas K⁺ and Cl^– move through specific channels. In adults, a Na⁺/K⁺/2Cl^– cotransporter replaces the Na⁺/Cl^– exchanger. Differential sensitivity of neonates and adults to iono- and osmoregulatory toxicants, such as metals, are discussed with respect to differences in whole-body Na⁺ uptake kinetics, as well as in the mechanisms of Na⁺ transport involved in the whole-body Na⁺ uptake in the two life stages.

Key words: crustacean, Daphnia magna, ion transport, life stage, Na⁺ uptake

	INTRODUCTION

TOP Summary INTRODUCTION MATERIALS AND METHODS RESULTS DISCUSSION References

 
Most aquatic crustaceans are marine species and only a few of them are able to hyper-osmoregulate their haemolymph in diluted seawater, i.e. to maintain a haemolymph osmotic concentration higher than that of the surrounding medium in diluted seawater. Furthermore, among those capable of performing haemolymph hyper-ionoregulation several of them are only weak regulators, being able to live for only a short time in freshwater. Most crab and shrimp species are in this group. Among the strong regulators, we can find some stenohaline freshwater crab and crayfish species.

In contrast to other invertebrates and fish (Kirschner, 2004), crustaceans living in freshwater present a somewhat different ionoregulatory picture (Péqueux, 1995; Kirschner, 2004; Freire et al., 2007). For freshwater fish, data available in the literature are sufficient to allow researchers to model the main routes of Na⁺ and Cl^– transport and the mechanisms involved in such processes (Kirschner, 2004; Evans et al., 2005). However, much less is known about the ion transport mechanisms in invertebrates. For example, ion-transporting epithelia (midgut and Malpighian tubules) in insects appears to be energized through a proton-motive force generated by a vacuolar-type proton ATPase (V-H⁺-ATPase proton pump). However, secondary transport mechanisms that are coupled to the V-H⁺-ATPase activity are not fully elucidated (Pullikuth et al., 2003). In crustaceans, models of ion transport in salt-transporting epithelia, especially gills, have also been generated over the last decade (Péqueux, 1995; Kirschner, 2004; Freire et al., 2007). However, ionoregulatory studies in freshwater crustaceans have been mainly limited to a few crayfish, crab and shrimp species, which because of their large size are convenient for in vivo experiments. In this regard, crayfish species are by far the most studied (Kirschner, 2004). However, very small cladocerans have proved suitable for radiotracer studies.

Daphnia magna Strauss is a small hyper-regulating freshwater cladoceran showing a vigorous, active NaCl uptake (Holm-Jensen, 1948; Stobbart et al., 1977; Potts and Fryer, 1979; Bianchini and Wood, 2002; Bianchini and Wood, 2003; Glover and Wood, 2005; Glover et al., 2005). This NaCl uptake is essential to counteract the continuous ion loss to the hypo-osmotic medium. This situation is aggravated in daphnids because they show a high surface to volume ratio. In fact, we have previously demonstrated that the sodium uptake rate is dependent on the body size and clearly determines the sensitivity of freshwater animals to ionoregulatory toxicants such as metals (Bianchini et al., 2002a; Grosell et al., 2002). Daphnids have been shown to be the most sensitive aquatic organisms to both waterborne copper and silver after either acute or chronic exposure (Ratte, 1999; Bianchini et al., 2002b; Grosell et al., 2002). Furthermore, the mechanisms of acute and chronic toxicity of these metals are associated with an alteration of the whole-body Na⁺ concentration as a consequence of a metal-induced inhibition of the whole-body Na⁺,K⁺-ATPase activity (Bianchini and Wood, 2002; Grosell et al., 2002; Bianchini and Wood, 2003). The inhibition of the Na⁺ uptake by Ag⁺ is clearly competitive and Ag⁺ does not affect whole-body Cl^– levels (Bianchini and Wood, 2003), which suggests that different ionoregulatory effects occur in freshwater crustaceans than in freshwater fish (Hogstrand and Wood, 1998; Wood, 2001; Evans et al., 2005). Taken together, these findings clearly indicate that the knowledge of the mechanisms of ion transport involved in the NaCl uptake in D. magna, the most metal-sensitive aquatic species, is essential to better interpret toxicity data and to have a good understanding of the mode of action of contaminant metals in the aquatic environment.

Toxicological data have also shown that the early-life stages of aquatic animals are the most sensitive to ionoregulatory toxicants such as metals (Ratte, 1999; Bianchini et al., 2002b; Grosell et al., 2002). In turn, physiological studies have clearly demonstrated that significant changes in the ability to cope with hypo-osmotic environments occur during the ontogenesis of the osmoregulatory organs in various crustacean groups, including cladocerans (daphnids), isopods, amphipods and decapods (crabs, lobsters, shrimps and crayfish) (Charmantier, 1998; Charmantier and Charmantier-Daures, 2001; Charmantier et al., 2002; Cieluch et al., 2004; Khodabandeh et al., 2005a; Khodabandeh et al., 2005b). The ontogenesis of the osmoregulation can occur at either the embryonic or the postembryonic phase (Charmantier and Charmantier-Daures, 2001).

According to Charmantier (Charmantier, 1998), crustaceans show three different patterns of ontogeny of osmoregulation. The first pattern is shown by weak osmoregulators, in which only small changes in the ability to osmoregulate during the course of development are seen. The true marine osmoconformers belong to this category. The second pattern is shown by crustaceans, in which the first postembryonic stage possesses the same osmoregulatory pattern as the adults. This category is represented by the freshwater-invading species. The third pattern is shown by species in which changes in the osmoregulatory pattern occur during their development, usually at or after metamorphosis. In this case, they shift from an osmoconforming to an osmoregulating response. This category is composed of the transitional species between the true marine osmoconformers and the very strongly regulating species (Charmantier, 1998).

Osmoregulation in daphnids has been extensively reviewed (Aladin and Potts, 1995). Briefly, eggs are incubated in brood chambers, which are closed in several species such as D. magna. Some species, such as D. magna, inhabit fresh or slightly saline waters. However, most of them live in marine and coastal waters. In both cases, osmolality of the embryonic fluid is isosmotic to the osmolality of the brood chamber fluid, which in turn is close to the osmolality of the haemolymph. This feature protects embryos until late in their development. Shortly before hatching, the brood chamber opens, and the emerging larvae are able to osmoregulate, since they have their osmoregulatory organs already developed. The osmoregulatory organs in daphnids include the neck organ, which in some cases is later replaced by epipodites, which have developed during the embryonic stages (Aladin and Potts, 1995).

It is clear from the toxicological and physiological findings described above that structural, biochemical and physiological changes could occur at the different life stages of crustaceans to cope with the challenges imposed by environmental salinity variations. Therefore, it is important to understand the possible ontogenetic changes in the mechanisms involved in ion-transporting mechanisms in daphnids, especially those associated with the Na⁺ uptake, and link them to the differential sensitivity of the life stages to ionoregulatory toxicants, such as copper and silver.

Although it has long been known that whole-body Na⁺ uptake is both active and occurs in a concentration-dependent, saturable manner in daphnids (Holm-Jensen, 1948; Stobbart et al., 1977; Potts and Fryer, 1979), there has been only one recent investigation on the actual mechanism(s) involved (Glover and Wood, 2005). This study used 7–8-day-old specimens of D. magna and provided evidence that the electrogenic 2Na⁺/1H⁺ exchanger played an important role (Glover and Wood, 2005). In light of the above, the objectives of the present study were to use radiotracer and pharmacological techniques to characterize the mechanism(s) of transport involved in whole-body Na⁺ uptake in D. magna of two size and age classes. Neonate animals (<24 h old) were compared with adults (7–8 days old), which were approximately sevenfold greater in body mass. Our results indicate that significant ontogenetic differences occur between the two age classes, and provide new information on the mechanisms of Na⁺ transport in freshwater cladocerans.

	MATERIALS AND METHODS

TOP Summary INTRODUCTION MATERIALS AND METHODS RESULTS DISCUSSION References

 
Daphnid maintenance
The water fleas Daphnia magna Strauss (ARO strain, Aquatic Research Organisms, Hampton, NH, USA) employed in the present study were obtained from an established laboratory culture. They were reared as previously described (Bianchini and Wood, 2002; Bowles et al., 2002; Bianchini and Wood, 2003; Bianchini et al., 2002a; Bianchini et al., 2002b; Bianchini et al., 2005). Briefly, the Daphnia colony was maintained in moderately hard synthetic freshwater, of which the ionic composition (0.6 mmol l^–1 NaCl, 1.0 mmol l^–1 CaCO₃ and 0.15 mmol l^–1 MgSO₄·7H₂O; pH 8.2) was similar to the water from the Lake Ontario (Canada). Synthetic water used for all tests was prepared as a single batch employing 1000 l of reverse-osmosis-purified water in a food-grade polyethylene tank.

During the maintenance period, as well as during experiments, D. magna were fed algae (Ankistrodesmus convolutus; 1.82x10⁸ cells l^–1, which is equal to 33 mg dry mass l^–1) and a mixture of a yeast–Cerophyll–trout chow slurry (YCT; 18.5 mg dry mass l^–1) on a daily basis.

Water was not aerated, but the experimental medium, including food, was renewed each day. Temperature and photoperiod were fixed at 20°C and 16 h:8 h L:D, respectively.

Sodium uptake
To assess the possible influence of body mass on Na⁺ uptake, neonate (<24 h) and adult (1 week) daphnids (N=48) were collected from the culture using plastic pipettes. They were randomly divided in three groups (16 daphnids per chamber) and tested in 50 ml glass beakers, as described below. Wet mass of all tested daphnids ranged from 0.050 to 3.700 mg. For the remaining experiments, daphnid size was selected in order to avoid the effect of body mass on sodium fluxes. Mean wet mass (± s.e.m.) of neonate (<24 h; N=48) and adult (1 week; N=48) daphnids used to determine the kinetic parameters of the whole-body Na⁺ uptake was 0.181±0.014 and 3.279±0.197 mg, respectively. Mean wet mass (± s.e.m.) of neonate (<24 h; N=78) and adult (1 week; N=78) daphnids used to characterize the different mechanisms involved in the Na⁺ uptake was 0.056±0.008 and 3.087±0.206 mg, respectively. In all cases, whole-body Na⁺ uptake was measured using ²²Na (0.37 mBq l^–1, Amersham, specific activity 11.2 TBq g^–1 Na⁺) as a radiotracer and measurements were done at 20°C.

Whole-body Na⁺ uptake was determined as previously described (Bianchini and Wood, 2002; Bianchini and Wood, 2003; Glover and Wood, 2005). Briefly, neonate and adult daphnids were collected from the culture medium, quickly rinsed in deionized water and transferred to a new glass beaker containing 50 ml of a simplified synthetic freshwater (0.6 mmol l^–1 NaCl and 0.5 mmol l^–1 CaCl₂; pH adjusted to 8.2 with KOH), which served as the basic test solution in all trials. Potassium concentration after adjusting pH was within the range found in the Lake Ontario [0.049–0.069 mmol l^–1 (NRCC, 1977)] and the tap water in Ontario province [0.001–0.512 mmol l^–1 (Health Canada, 2007)]. ²²Na was then added to this new experimental medium at a final specific activity of 1.85 kBq/µEq Na⁺. Water samples for measurement of ²²Na radioactivity and total sodium were taken at 0 and 1 h, after which the test was ended. These samples were used for ²²Na radioactivity measurement using a Canberra-Packard MINAXI gamma counter, and for total sodium measurement using a Varian AA-1275 atomic absorption unit operated in flame emission mode. After the 1 h flux period, daphnids were collected using plastic pipettes, washed for 15 s in a concentrated (600 mmol l^–1) NaCl solution to displace loosely bound ²²Na, blotted dry on filter paper, weighed on an electronic microscale (Mettler UMT2; 0.001 mg accuracy; Mettler-Toledo, Columbus, OH, USA), and transferred to plastic vials. The ²²Na radioactivity in the whole body was then measured as described for the water samples. Na⁺ uptake rate was calculated based on the incorporation of ²²Na in the whole body during the 1 h flux period, the mean measured specific activity of the ²²Na in the water, the body mass of the animal, and the elapsed time, as previously described (Bianchini and Wood, 2002; Bianchini et al., 2002a; Bianchini and Wood, 2003; Grosell et al., 2002).

To determine the kinetic parameters of the whole-body Na⁺ uptake, groups of daphnids (N=6 in each group) were exposed (1 h) to different NaCl levels (0.05 to 4.80 mmol l^–1) in the test water. Media were prepared adding NaCl to a 0.5 mmol l^–1 CaCl₂ solution to reach the desired Na⁺ concentration and the pH of the solution was adjusted to 8.2 with KOH. The Na⁺ uptake rates at the different Na⁺ concentrations were calculated as described above. Kinetic parameters [Michaelis constant (K_m) and maximal velocity (V_max)] for sodium uptake in neonate and adult daphnids under control conditions were determined by means of nonlinear regression analyses (one-site binding), as previously described (Bianchini and Wood, 2003).

Several pharmacological tools were used to characterize the different mechanisms involved in the Na⁺ uptake in daphnids. Considering that D. magna can tolerate and live in freshwater and brackish waters (Schuytema, 1997), the drugs tested were selected based on the mechanisms described to operate in salt-transporting epithelia of weak and strong hyperosmoregulator crustaceans. These mechanisms have been recently reviewed and modelled (Kirschner, 2004; Freire et al., 2007). In turn, concentrations of drugs tested in the present study were selected to fall within the range of concentrations showed to significantly inhibit the desired target mechanisms in weak and strong hyperosmoregulator crustaceans. Original studies reporting these concentrations have been extensively reviewed (Péqueux, 1995; Onken and Riestenpatt, 1998; Kirschner, 2004; Freire et al., 2007). Based on these considerations, the following enzyme inhibitors and ion channel and transporter blockers were added to the external water in separate tests: acetazolamide (10^–3 mol l^–1; carbonic anhydrase inhibitor); bafilomycin A₁ (5x10^–7 mol l^–1; V-H⁺-ATPase inhibitor); phenamil (10^–4 mol l^–1; Na⁺ channel blocker); diphenylamine-2-carboxylate (DPC; 10^–3 mol l^–1; Cl^– channel blocker); amiloride (10^–3 mol l^–1; Na⁺/H⁺ exchanger); bumetanide (10^–3 mol l^–1; Na⁺/Cl^– and Na⁺/K⁺/2Cl^– cotransporters blocker); furosemide (10^–3 mol l^–1; Na⁺/K⁺/2Cl^– cotransporter blocker); thiazide (10^–3 mol l^–1; Na⁺/Cl^– cotransporter blocker); di-isothiocyanostilbene-2,2' disulfonic acid (DIDS; 10^–3 mol l^–1; Cl^–/HCO₃^– exchanger blocker); and 2,4,6-triaminopyrimidine (TAP; 10^–3 mol l^–1; paracellular pathway blocker).

All drugs used were purchased from Sigma (St Louis, MI, USA), except the bafilomycin A₁, which was purchased from Biomol Research Laboratories (Plymouth Meeting, PA, USA). They were previously dissolved in dimethylsulfoxide (DMSO) such that the final DMSO concentration in the test solution was 1%. All drugs were added to the external water in separate tests. For each test, daphnids were pre-exposed for 15 min to the specific blocker or inhibitor, prior to the addition of ²²Na to start the flux measurement. Pre-exposure was carried out in the same test solution and the drug remained present during the 1 h flux measurement. In control treatments, whole-body Na⁺ uptake was similarly measured in the presence of 1% DMSO to rule out a possible effect of this chemical on the whole-body Na⁺ influx. Also, some tests were carried out in the absence of Cl^– (replaced by gluconate) in the test solution to check for possible Cl^– dependence of the whole-body Na⁺ uptake.

Data from pharmacological studies were expressed as mean ± s.e.m. (N=6). Significant differences between treatments were assessed by analysis of variance (ANOVA) followed by the a posteriori Tukey's test. The significance level adopted was 95%.

	RESULTS

TOP Summary INTRODUCTION MATERIALS AND METHODS RESULTS DISCUSSION References

 
Kinetics of whole-body Na⁺ uptake
The whole-body Na⁺ uptake rate was inversely related to the body mass over a wide range of body mass (0.050–3.700 mg). The slope of this relationship on a log–log plot was –0.305 (Fig. 1).

View larger version (6K): [in this window] [in a new window]   Fig. 1. Influence of wet body mass (ww) on mass-specific Na+ uptake rate (influx) in the water flea Daphnia magna. Note that both axes are logarithmic.

View larger version (8K): [in this window] [in a new window]   Fig. 2. Kinetics of mass-specific Na+ uptake rate in neonate and adult water flea Daphnia magna as a function of sodium concentration. Data are expressed as mean ± 1 s.e.m. (N=6). Kinetic parameters (Michaelis constant [Km] and maximal velocity [Vmax]) for sodium uptake in neonate and adult daphnids were determined by means of nonlinear regression analyses (one-site binding), as previously described (Bianchini and Wood, 2003).

View larger version (10K): [in this window] [in a new window]   Fig. 3. Whole-body Na+ uptake rate in neonate and adult water flea Daphnia magna after pre-exposure to 1% dimethylsulfoxide (DMSO), in the absence of Cl– (replaced with equimolar gluconate) in the external medium (Gluco) or after pre-exposure to 2,4,6-triaminopyrimidine (TAP, 10–3 mol l–1). Data are expressed as mean ± 1 s.e.m. (N=6). Note the different axis scale for neonate (left) and adult (right) daphnids.

In weak hyperosmoregulators, both transcellular and paracellular transepithelial transport of Na⁺ have been reported. It has been shown that Na⁺ absorption occurs via the paracellular pathway, and that an apical Na⁺/H⁺ exchanger and a Na⁺/K⁺/2Cl^– cotransporter are implicated in transcellular Na⁺ uptake from the external medium by the salt-transporting epithelia. On the basolateral side of these epithelia, a Na⁺/K⁺ pump uses the energy resulting from the Na⁺/K⁺-ATPase activity and pumps the intracellular Na⁺ into the haemolymph. In the present study, we did not test the effect of ouabain, a well-known inhibitor of the Na⁺/K⁺-ATPase activity, since high specific whole-body Na⁺/K⁺-ATPase activities have been already reported in both neonate and adult D. magna (Bianchini and Wood, 2002; Bianchini and Wood, 2003). However, TAP (10^–3 mol l^–1) was employed to block a possible paracellular entry of Na⁺, whereas amiloride (10^–3 mol l^–1) was used to target the Na⁺/H⁺ exchanger. In the presence of TAP, no significant change in whole-body Na⁺ uptake was observed in either neonate or adult daphnids (Fig. 3). By contrast, a significant decrease (34%) in whole-body Na⁺ uptake was observed after exposure to amiloride in adult daphnids, but not neonates (Fig. 4).

View larger version (9K): [in this window] [in a new window]   Fig. 4. Whole-body Na+ uptake rate in neonate and adult water flea Daphnia magna after pre-exposure to amiloride (Amilo, 10–3 mol l–1), phenamil (Phena, 10–4 mol l–1) or bafilomycin A1 (Bafilo, 5x10–7 mol l–1). Data are expressed as mean ± 1 s.e.m. (N=6). Note the different axis scale for neonate (left) and adult (right) daphnids.

Regarding the Na⁺/K⁺/2Cl^– cotransporter, both furosemide (10^–3 mol l^–1) and bumetanide (10^–3 mol l^–1) were used in the present study to target this mechanism. The use of furosemide is more common in pharmacological studies, but bumetanide was also employed because of its higher effectiveness, at least in mammalian tissues (O'Grady et al., 1987). However, bumetanide at the concentration used can also block the Na⁺/Cl^– cotransporter. Therefore, thiazide (10^–3 mol l^–1) was tested to identify a possible inhibition of both Na⁺/K⁺/2Cl^– and Na⁺/Cl^– cotransporters by bumetanide. It is important to note that thiazide has been shown to block the Na⁺/Cl^– cotransporter, but not the Na⁺/K⁺/2Cl^– exchanger. In the present study, furosemide was without significant effect on whole-body Na⁺ uptake in either neonate or adult daphnids (Fig. 5). However, whole-body Na⁺ uptake significantly decreased after exposure of neonates (61%) or adults (53%) to bumetanide. Furthermore, a significant decrease (53%) in whole-body Na⁺ uptake was observed in neonates exposed to thiazide but no significant effect of this drug was observed in adult daphnids (Fig. 5).

View larger version (9K): [in this window] [in a new window]   Fig. 5. Whole-body Na+ uptake rate in neonate and adult water flea Daphnia magna after pre-exposure to furosemide (furo, 10–3 mol l–1), bumetanide (bume, 10–3 mol l–1) or thiazide (thiaz, 10–3 mol l–1). Data are expressed as mean ± 1 s.e.m. (N=6). Note the different axis scale for neonate (left) and adult (right) daphnids.

Regarding Cl^– transepithelial transport, the Cl^–/HCO₃^– exchanger and Cl^– channels seem to be involved in this process at the apical and basolateral membrane, respectively. This picture is similar in both weak and strong hyperosmoregulators (Kirschner, 2004; Freire et al., 2007). In the present study, DIDS (10^–3 mol l^–1) and DPC (10^–3 mol l^–1) were employed to target the Cl^–/HCO₃^– exchanger and Cl^– channels, respectively. DIDS was used instead of SITS (stilbene isothiosulphonic acid) because the whole-body Na⁺ uptake in D. magna was previously reported to be independent of the Cl^– concentration in the external medium (Glover and Wood, 2005). DPC exposure induced significant decreases in whole-body Na⁺ uptake in both neonate (59%) and adult (74%) daphnids. However, DIDS was without significant effect in both life stages (Fig. 6).

View larger version (9K): [in this window] [in a new window]   Fig. 6. Whole-body Na+ uptake rate in neonate and adult water flea Daphnia magna after pre-exposure to 4,4' diisothiocyanostilbene-2,2' disulfonic acid (DIDS, 10–3 mol l–1), diphenylamine-2-carboxylate (DPC, 10–3 mol l–1) or acetazolamide (Aceta, 10–3 mol l–1). Data are expressed as mean ± 1 s.e.m. (N=6). Note the different axis scale for neonate (left) and adult (right) daphnids.

	DISCUSSION

TOP Summary INTRODUCTION MATERIALS AND METHODS RESULTS DISCUSSION References

 
In the present study, we used radiolabelling techniques combined with pharmacological tools to assess the kinetic characteristics and mechanisms of transport involved in the Na⁺ uptake in free-swimming Daphnia magna. We considered only measurements of whole-body Na⁺ uptake due to the very small size of daphnids, and therefore cannot partition transport to the various structures that might be involved.

Na⁺ uptake rate, and therefore probably Na⁺ turnover, is inversely related to the body mass in D. magna over a wide range (0.050–3.700 mg; Fig. 1). This relationship can be explained by the fact that, in freshwater fish and crustaceans, the body mass-specific area of the salt-transporting organs, especially the gills, is also inversely related to body mass (Hughes and Morgan, 1973; Santos et al., 1987). Note that the slope (–0.305) obtained for the log–log relationship between the whole-body Na⁺ uptake and body mass is very close to that (–0.328) observed when several aquatic species were considered (Grosell et al., 2002). Furthermore, this slope is similar to that expected for other surface-dependent physiological processes in aquatic invertebrates, such as respiration (Barnes et al., 1993). Thus, these findings clearly indicate that small daphnids would be more sensitive than larger ones to environmental toxicants with ionoregulatory actions. In fact, a significant and highly negative correlation was observed between the body mass and metal (Cu and Ag) sensitivity in several aquatic species (Grosell et al., 2002), including D. magna at different life stages (Bianchini et al., 2002a). In addition to the dependence on size, sensitivity to metals within daphnids could be also associated with structural, biochemical, and/or physiological ontogenetic differences, as discussed below.

Transport kinetics data indicate that in both neonate and adult daphnids whole-body Na⁺ uptake follows a typical Michaelis–Menten saturation curve (Fig. 2). This feature is similar to that described for other freshwater crustaceans, such as the crayfish Astacus pallipes (Shaw, 1959). However, a marked difference was observed between the two life stages. Both the maximum capacity for sodium transport (J_max) and the affinity constant for sodium transport (K_m) were much higher in neonates than in adults. Based on the mean sizes of the two groups of daphnids used to determine the kinetic parameters of the whole-body Na⁺ uptake and the relationship shown in Fig. 1, the whole-body Na⁺ uptake rates are 11.44 and 4.73 µEq g^–1 h^–1 for the neonates (0.181 mg) and adults (3.279 mg) used, respectively. These data show that the lower affinity (higher K_m) for Na⁺ in neonates is compensated by a higher maximum capacity of Na⁺ uptake. It is possible that these differences occur because the same mechanisms of Na⁺ uptake are present in neonates and adults, but with biochemically mediated (e.g. intracellular modulators) or structurally mediated differences (e.g. diffusion access distances), or that the mechanism(s) of Na⁺ uptake is (are) fundamentally different in neonates and adults. Notably, ontogenetic changes seen in hyper-regulating crustaceans are generally associated with anatomical and/or structural changes in the ion-transporting cells and organs (Charmantier and Charmantier-Daures, 2001; Charmantier et al., 2002; Cieluch et al., 2004; Khodabandeh et al., 2005a; Khodabandeh et al., 2005b).

View larger version (13K): [in this window] [in a new window]   Fig. 7. Functional models of ion transport mechanisms involved in whole-body Na+ uptake in neonate (A) and adult (B) water flea Daphnia magna. CA, carbonic anhydrase. Solid and broken lines indicate transport and diffusion, respectively. ? indicates the need for more data to confirm or not the presence of the mechanism of transport.

Data from kinetic experiments performed in the present study show that Na⁺ uptake is saturable in both neonate and adult D. magna (Fig. 2). A similar saturable Na⁺ uptake has been previously reported in D. magna, but only for adults (Stobbart et al., 1977; Potts and Fryer, 1979; Glover and Wood, 2005). This finding indicates that a specific transport mechanism or mechanisms is/are involved in Na⁺ uptake in both life stages. In this context, it is important to note that Na⁺ uptake in D. magna is dependent on pH, reducing as pH decreases (Potts and Fryer, 1979; Glover and Wood, 2005). Therefore, it seems that sodium uptake may be linked to proton excretion in D. magna. Furthermore, in agreement with a previous report for adult daphnids (Glover and Wood, 2005), no significant effect on whole-body Na⁺ uptake was observed in both neonate and adult daphnids when Cl^– was completely replaced by gluconate in the external medium (Fig. 3). This finding indicates that the whole-body Na⁺ uptake in both neonate and adult daphnids is not dependent on Cl^– concentration in the external medium, at least at Na⁺ levels typical of those occurring in natural freshwater. This finding is similar to that reported for other crustaceans adapted to freshwater, such as the Chinese mitten crab Eriocheir sinensis (Péqueux, 1995; Kirschner, 2004; Freire et al., 2007). Furthermore, the Na⁺ uptake characteristics shown by daphnids are quite similar to those reported for the freshwater crayfish Astacus pallipes, i.e. whole-body Na⁺ influx in this species is also independent of the ambient Cl^– concentrations, but dependent on the external Na⁺ concentration, following typical Michaelis–Menten kinetics (Shaw, 1959).

The fact that TAP, a well-known blocker of paracellular permeability in salt-transporting epithelia, did not affect the whole-body Na⁺ influx (Fig. 3) clearly indicates that the Na⁺ uptake in both neonate and adult daphnids is mainly occurring through the transcellular pathway. In fact, transcellular Na⁺ influx has been widely reported to occur in gills, i.e. the main organ involved in ionic and osmotic regulation in freshwater and euryhaline crustaceans such as shrimp, crab and crayfish (Péqueux, 1995; Kirschner, 2004; Freire et al., 2007).

Regarding a possible involvement of a Na⁺/H⁺ exchanger in the whole-body Na⁺ uptake in D. magna, a significant amiloride-sensitive whole-body Na⁺ uptake was observed in adult daphnids (Fig. 4). This result is in complete agreement with those previously reported for adult daphnids (Glover and Wood, 2005). Regarding the putative elements of a Na⁺/H⁺ (or NH₄⁺) exchanger in crustaceans, they have been reported for freshwater and euryhaline crabs, as well as for freshwater crayfish (Péqueux, 1995; Kirschner, 2004; Freire et al., 2007). As performed here, most studies have employed pharmacological tools to demonstrate the presence of this mechanism in aquatic crustaceans. For example, amiloride, at the same concentration tested in daphnids in the present study (10^–3 mol l^–1), also inhibited the whole-body influxes of both Na⁺ and H⁺ without significant effects on the whole-body Na⁺ efflux in salt-depleted crayfish (Kirschner et al., 1973; Ehrenfeld, 1974). Furthermore, several lines of evidence from studies on whole-body Na⁺ and H⁺ fluxes, as well as the effect of external NH₄⁺ concentration on these fluxes, also suggested that a Na⁺/H⁺ exchanger may play an important role in whole-body Na⁺ uptake in freshwater crayfish (Shaw, 1960a; Shaw, 1960b; Kirschner, 2002).

Based on their findings, Glover and Wood (Glover and Wood, 2005) suggested that a putative electrogenic 2Na⁺/1H⁺ exchanger would be involved in the whole-body Na⁺ uptake in adult D. magna. In fact, invertebrate epithelial cells from different tissues, including crustacean gills, posses an electrogenic brush-border 2Na⁺/1H⁺ antiporter protein that is analogous to the vertebrate electroneutral 1Na⁺/1H⁺ exchanger. This electrogenic antiporter is also sensitive to amiloride, but performs an extensive array of transport functions because of its electrogenic nature and wide substrate range, involving both monovalent and divalent cations (Ahearn and Franco, 1990; Ahearn et al., 1994; Zhuang et al., 1995; Ahearn, 1996; Ahearn et al., 1999; Ahearn et al., 2001; Mandal et al., 2003; Pullikuth et al., 2003). In this case, a 2Na⁺/1H⁺ system would be expected to yield a sigmoidal relationship of Na⁺ uptake rate with water Na⁺ concentration because of co-operativity effects. However, a typical hyperbolic Michaelis–Menten kinetic relationship was observed in both neonates and adults in the present study, as well as for adults in the study by Glover and Wood (Glover and Wood, 2005). This finding suggests that at low Na⁺ concentrations, as observed in most freshwaters, a 1Na⁺/1H⁺ exchanger would be operating at the apical surface of the salt-transporting epithelia in daphnids. This electroneutral exchange is also reported to operate in different invertebrate salt-transporting epithelia, such as the Malpighian tubules of mosquitoes (Weng et al., 2003) and gills of freshwater and euryhaline crabs (Péqueux, 1995; Kirschner, 2004; Freire et al., 2007). In turn, the electrogenic exchange has been implicated in maintaining the alkaline lepidopteran or mosquito midgut lumen or the acidic lumen of crustaceans (Pullikuth et al., 2003). In fact, the prevalence of electrogenic cation–proton exchange in invertebrates has been viewed as an ancestral mechanism, whereas the electroneutral exchange occurring in mammals is considered an evolutionary adaptation (Grinstein and Wieczoreck, 1994; Ahearn et al., 2001).

Despite the clear inhibitory effect of amiloride on the Na⁺ uptake in adult daphnids, no significant effect was observed in neonates (Fig. 4). This differential response of neonate and adult daphnids to amiloride could be associated with different cuticle properties, which hinder the drug from approaching the apical membrane of ion-transporting epithelia. It has been demonstrated that the crustacean cuticle has ion-selective properties (Avenet and Lignon, 1985; Lignon and Lenoir, 1985), which would certainly affect the local water chemistry next to the salt-transporting epithelia, thereby also affecting the kinetics (e.g. K_m) of whole-body ion uptake. Otherwise, we need to consider that fundamentally different mechanisms of ion transport are operating in the different life stages. This second hypothesis is clearly supported by the data from our pharmacological studies. Whole-body Na⁺ uptake was inhibited by bafilomycin A₁ (Fig. 4) and thiazide (Fig. 5) only in neonates, whereas amiloride had a significant inhibitory effect only in adults (Fig. 4).

If we assume that a Na⁺/H⁺ exchanger is not operating in the whole-body Na⁺ uptake in neonate daphnids, based on the lack of effect of amiloride, another possibility is that the Na⁺ influx could be driven across the apical membrane by the activity of a V-H⁺-ATPase proton pump. Arguing in favour of this hypothesis, a clear inhibition (50%) of the whole-body Na⁺ uptake was observed in the present study in neonate daphnids (Fig. 4) after pre-exposure to either phenamil, a well-known inhibitor of epithelial Na⁺ channels, or bafilomycin A₁, a potent and specific inhibitor of the V-H⁺-ATPase. Taken together, these findings indicate that a V-H⁺-ATPase associated with an epithelial Na⁺ channel is involved in the whole-body Na⁺ uptake in neonate daphnids. This enzyme has been shown to be also present in gills of both freshwater and euryhaline crabs (Onken and Putzenlechner, 1995; Tresguerres et al., 2003; Weihrauch et al., 2004), as well as in freshwater crayfish (Putzenlechner, 1994; Zare and Greenaway, 1998; Zetino et al., 2001). In insects, the V-H⁺-ATPase proton pump also plays a pivotal role in generating a proton-motive force that energizes the ion-transporting epithelia (midgut and Malpighian tubules) (Pullikuth et al., 2003).

The fact that a similar effect of phenamil, but not of bafilomycin A₁, was seen in adult daphnids (Fig. 4) suggests that they are probably not expressing V-H⁺-ATPase or else are expressing this enzyme only at low levels, but the epithelial Na⁺ channel is still present and operating. In this context, an ATP-driven Na⁺ influx in neonates would be in agreement with the higher transport capacity (higher J_max) for Na⁺ showed by neonate daphnids. Furthermore, as observed in other aquatic species, neonate daphnids exhibit higher Na⁺ turnover rates than adults because of their higher mass-specific area for exchange with the environmental medium (Bianchini et al., 2002a), thus requiring a better efficiency for Na⁺ uptake. In addition, a consequently higher metabolism would be occurring (Baillieul et al., 2005), requiring a higher capacity of H⁺ extrusion across the apical membrane of salt-transporting epithelia in neonates.

In summary, the Na⁺ influx across the salt-transporting epithelia of neonate daphnids seems to occur through an epithelial Na⁺ channel, powered by an active proton extrusion via a V-type H⁺-ATPase, which would provide the required electrical gradient for Na⁺ uptake across the apical membrane against a concentration gradient, as observed in the ion-transporting epithelia of insects (Pullikuth et al., 2003) and gills of freshwater-adapted crabs (Kirschner, 2004; Freire et al., 2007). By contrast, the Na⁺ influx across the salt-transporting epithelia of adult daphnids seems to involve the Na⁺/H⁺ exchanger, as observed in freshwater crayfish and brackish water-acclimated crabs (Péqueux, 1995; Kirschner, 2004; Freire et al., 2007). In both cases, carbonic anhydrase would be providing the H⁺ needed for the ion transport operation, as observed in freshwater crayfish (Ehrenfeld, 1974; Kirschner, 2004; Freire et al., 2007). This statement is based on the fact that acetazolamide, a well-known inhibitor of carbonic anhydrase (CA), induced a significant decrease in the Na⁺ influx in both neonate and adult daphnids (Fig. 6). In fact, CA is the enzyme responsible for H₂CO₃ formation from CO₂ hydration, generating both H⁺ and HCO₃^– in gills of aquatic invertebrates (Péqueux, 1995; Kirschner, 2004; Freire et al., 2007).

Regarding the ion movements across the basolateral membrane of the salt-transporting epithelia in daphnids, Na⁺ would be driven by an ATP-dependent sodium–potassium pump (Na⁺/K⁺-ATPase), as observed in salt-transporting epithelia of insects (Pullikuth et al., 2003) and several freshwater and brackish crustaceans (Péqueux, 1995; Kirschner, 2004; Freire et al., 2007). This statement is based on the fact that high specific whole-body Na⁺/K⁺-ATPase activities have been reported in both neonate and adult D. magna (Bianchini and Wood, 2002; Bianchini and Wood, 2003). Thus, a putative pump-and-leaky system would transport Na⁺ from the intracellular to the extracellular fluid across the basolateral membrane with K⁺ being transported in the opposite direction at the expense of ATP. In turn, intracellular K⁺ would diffuse from the intracellular to the extracellular fluid through specific K⁺ channels, following an electrochemical gradient generated by the Na⁺/K⁺-ATPase pump. The diffusive movement of K⁺ would generate a local electric gradient enough to drive the Cl^– from the intracellular to the extracellular fluid through specific Cl^– channels across the basolateral membrane of the salt-transporting epithelia. This hypothesis is supported by the fact that a marked and significant inhibition of the whole Na⁺ uptake was observed after exposure of both neonate and adult daphnids to DPC (Fig. 6), a known specific inhibitor of Cl^– channels. Furthermore, evidence for the existence of epithelial Cl^– channels in intact crustaceans has already been reported in the literature (Zetino and Kirschner, 1993). Notably, the absence of an effect of DIDS in either life stage suggests that a basolateral Na⁺/HCO₃^– cotransport system is not involved in Na⁺ uptake, in contrast to recent models in insects (Pullikuth et al., 2003) and freshwater fish (Perry et al., 2003; Scott et al., 2005). However, further studies should be performed to better elucidate this point, since a DIDS-insensitive Na⁺/HCO₃^– cotransport system has been reported to occur in the basolateral membrane of different mammalian tissues (Aickin, 1994; Odgaard et al., 2003). Despite the absence of and effect of DIDS on whole-body Na⁺ uptake in neonate and adult daphnids, it is also possible that the HCO₃^– generated by the carbonic anhydrase would diffuse from the intracellular fluid to the surrounding medium through a Cl^–/HCO₃^– exchanger. This idea is based on two facts: an apical Cl^–/HCO₃^– exchanger has been widely reported in ion-transporting epithelia of both freshwater and euryhaline crustaceans (Péqueux, 1995; Kirschner, 2004; Freire et al., 2007); and a Na⁺-independent Cl^–/HCO₃^– exchanger resistant to inhibition by DIDS has been identified and cloned in the apical membranes of mammalian ion-transporting epithelia (Alper, 1991; Godinich and Jennings, 1995; Romero and Boron, 1999; Soleimani and Burnham, 2000; Royaux et al., 2001; Tsuganezawa et al., 2001; Barmeyer et al., 2007). Therefore, future studies should be performed to verify the possible expression and localization of this kind of Cl^–/HCO₃^– exchanger in daphnids.

In addition to the ATP-dependent Na⁺ transport driven by the Na⁺/K⁺ pump (Na⁺/K⁺-ATPase) at the basolateral membrane, other mechanisms of Na⁺ transport seem to be involved as well. The significant inhibition of the whole-body Na⁺ uptake induced by bumetanide in both neonate and adult daphnids (Fig. 5) strongly suggest that, at least part of the Na⁺ influx could be associated with the action of a Na⁺/K⁺/2Cl^– cotransporter in both life stages. However, a significant inhibition of the whole-body Na⁺ uptake after exposure to thiazide was only observed in neonate daphnids (Fig. 5). The combination of these results indicate that in neonates a Na⁺/Cl^– cotransporter would play an important role in the whole-body Na⁺ uptake whereas in adults the mechanism probably involves the Na⁺/K⁺/2Cl^– cotransporter. The clear lack of effect of the absence of Cl^– in the external medium on the whole-body Na⁺ uptake in both neonate and adult daphnids (Fig. 3) strongly suggests that these mechanisms are in fact located at the basolateral membrane and are involved in extrusion of Na⁺ from the intracellular fluid to the extracellular fluid. In turn, the lack of effect of furosemide on Na⁺ uptake in both life stages of daphnids (Fig. 5) could be explained by a possible lower sensitivity of the salt transporting epithelia to furosemide than to bumetanide, as observed in some salt-transporting epithelia in mammals (O'Grady et al., 1987). A bumetanide-sensitive Na⁺/K⁺/2Cl^– cotransporter has been also suggested to operate in the basolateral membrane of Malpighian tubules of insects (Pullikuth et al., 2003).

Functional models of the schemes outlined above for neonate and adult daphnids are depicted in Fig. 7, based on the findings described in the present study. These models do not necessarily mean that all Na⁺ transport is occurring at only one kind of salt-transporting epithelial cell. In fact, it has been reported that the epithelial cells of the epipodites are those involved in the osmoregulation in D. magna (Goldmann et al., 1999), and that two kinds of epithelial cells, dark and light types, are alternately arranged in this `gill' of D. magna (Kikuchi, 1983). Thus, it could be possible that the different mechanisms of ion transport involved in the whole-body Na⁺ uptake in D. magna, identified in the present study, are partitioned into the two different kinds of cells (dark and light cells). This picture would be very similar to that described for the amphibian skin, where MR cells are associated with principal cells (Kirschner, 2004).

Taken together, the findings reported here clearly suggest that differences in whole-body Na⁺ uptake kinetics, as well as in the mechanisms of Na⁺ transport involved in the whole-body Na⁺ uptake in neonate and adult D. magna could be the physiological basis for the differential sensitivity of these two life stages to iono- and osmoregulatory toxicants, such as metals (Bianchini et al., 2002a; Grosell et al., 2002).

The higher sensitivity of neonates could be explained by the lower affinity of the Na⁺ uptake mechanisms in this life stage. This lower affinity for Na⁺ would favour the ionoregulatory toxicants, such as Cu⁺ and Ag⁺, in the competition for the binding sites for Na⁺ at the ion-transporting epithelia of daphnids. In fact, we found that the inhibition of whole-body Na⁺ uptake by Ag⁺ is clearly competitive in D. magna (Bianchini and Wood, 2003). This higher competition associated with the higher maximum capacity for sodium transport (J_max) observed in neonates would lead to a higher whole-body accumulation of the toxicant in individuals of this life stage. In fact, we have reported a highly significant negative correlation (slope around 0.4) between body mass of D. magna and whole-body silver accumulation, which was directly related to the whole-body Na⁺/K⁺-ATPase inhibition induced by Ag⁺ (Bianchini and Wood, 2003). At this point, its important to stress that inhibition of the whole-body Na⁺ uptake induced by Ag⁺ is directly associated with the metal-induced inhibition of the whole-body Na⁺/K⁺-ATPase activity, constituting the physiological basis of both Cu⁺ and Ag⁺ toxicity in D. magna (Bianchini and Wood, 2002; Grosell et al., 2002; Bianchini and Wood, 2003).

In addition to the increased metal accumulation associated with the features described above, the major mechanism controlling Na⁺ uptake in neonate daphnids, i.e. the epithelial Na⁺ channel associated with the V-type H⁺-ATPase, could be also favouring the metal accumulation in this life stage. This statement is based on the fact that silver, probably as Ag⁺, has been demonstrated to enter the branchial epithelial cells via the Na⁺ channel coupled to the proton ATPase in the apical membrane of freshwater fish (Bury and Wood, 1999). On the other hand, the absence of a V-type H⁺-ATPase and the expression of a Na⁺/H⁺ exchanger in the apical membrane of adult daphnids seem to be at the basis of a lower metal accumulation rate and a consequently lower sensitivity of adult daphnids to metal exposure.

	Acknowledgments

 
A. Bianchini is a fellow of the Brazilian CNPq (Proc. # 300906/2006-4) and C.M.W. is supported by the Canada Research Chair Program. Supported by an NSERC Discovery grant and an NSERC CRD grant in association with co-funding from Kodak Canada Inc. to C.M.W.

	References

TOP Summary INTRODUCTION MATERIALS AND METHODS RESULTS DISCUSSION References

 

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