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Ammonia excretion at different life stages of silver catfish/excrecao de amonia em diferentes estagios de vida do jundia.

Introduction

Ammonia is the dominant end product of nitrogen metabolism in most teleosts, and is toxic at low concentrations, particularly in N[H.sub.3] (unionized ammonia) form (CHEW et al., 2006; FELIPO; BUTTERWORTH, 2002; IP et al., 2004; WICKS; RANDALL, 2002). The main internal source of ammonia in fish is through the catabolism of proteins, and most of this waste product is produced in the liver of fish during the transamination of amino acids followed by the deamination of glutamate (WICKS; RANDALL, 2002). Ammonia is mainly excreted through the gills (WILKIE, 2002), and teleosts usually increase the excretion of ammonia after feeding (ALTINOK; GRIZZLE, 2004).

Compared to the number of studies conducted on adult stages of teleosts, only a small number of studies have examined nitrogen metabolism during the early development of teleosts. Ammonia appears to be the dominant end product during the embryonic and yolk sac stage of freshwater teleosts (DABROWSKI et al., 1984; OLIVA-TELES; KAUSHIK, 1990; WRIGHT et al., 1995). Ammonia excretion in Caregonus lavaretus increased during the pre-hatching period, from 52.1 to 163.2 gg [h.sub.-1] [10.sup.3] [eggs.sup.-1] (DABROWSKI et al., 1984), and high rates of ammonia excretion were observed (> 100 and > 50 gg N [h.sup.-1] [10.sup.3] [eggs.sup.-1]) in common carp, Cyprinus carpio, at hatching and at the onset of free-swimming stages, respectively (KAUSHIK et al., 1982).

Altinok and Grizzle (2004) reported that dietary protein intake is the most important factor affecting ammonia excretion. In fish fed until satiation, ammonia production may be 10 times higher than in starved fish (WOOD, 1993).

The silver catfish, Rhamdia quelen (Quoy and Gaimard, 1824; Heptapteridae), is found from southern Mexico to central Argentina; the species is bred more intensively in Brazil, Uruguay and Argentina. Moreover, the species shows two spawning peaks year-1 (GOMES et al., 2000); embryological development is fast, and larval development occurs in 3-5 days (AMORIM et al., 2009; PEREIRA et al., 2006). Therefore, the aim of this study was to examine ammonia excretion at different life stages (eggs, larvae and juveniles) and determining the influence of fasting time on ammonia excretion in silver catfish.

Material and methods

Silver catfish eggs (mean weight = 5.0 mg) were obtained after induced spawning. The brood fish received one dose of carp pituitary extract (female = 5 mg kg-1; male = 3 mg kg-1, according to LEGENDRE et al., 1996) and were then extruded after nine hours. The oocyte mass was placed in a plastic container, and milt was then added to provide fertilization. Half a liter of water at the same temperature as the water in which the brood fish were maintained was added to the container to allow egg hydration (10 min.). Twelve minutes later, the dead eggs were manually separated on Petri dishes, and the viable fertilized eggs (determined by the observation of the initial cell division on a microscope) were placed in incubators (4 L polyethylene bottles--600 eggs per bottle) at a temperature of 24 [+ or -] 1.0[degrees]C and a pH of 7.2 [+ or -] 0.2 units. Each bottle received continuous aeration with a 20 W air pump (3.2 L min.-1 air flow) that also promoted water movement. The incubators were cleaned daily by suction, and, consequently, at least 30% of the water in the bottles was replaced with water previously adjusted to the same conditions of temperature and pH.

Eggs and larvae were collected from the incubators at 0, 12, 24, 36, and 192h after fecundation and placed in continuously aerated 25 mL chambers (ten replications in each time, n=10 for each replication) for 12h. Water samples (5 mL) were taken at the beginning and end of each 12h period and the ammonia concentration was immediately measured. Afterwards, all eggs and larvae from each replication were weighed in a scale (precision [+ or -] 0.00001 g). Larvae received commercial diet (32% crude protein) after hatching (approximately 28h after fecundation), in constant intervals (every two hours).

Silver catfish juveniles (2-50 g and 150-320 g) were bought from a commercial fish farm near the city of Santa Maria, Rio Grande do Sul State, Brazil, and transported to the Fish Physiology laboratory at the UFSM, where they were maintained for four days in continuously aerated 250 L tanks (aerated using two 20 W air pumps; pH 6.7 [+ or -] 0.5 units; temperature 23 [+ or -] 1.0[degrees]C; and hardness 32.0 [+ or -] 1.0 mg CaC[O.sub.3] [L.sup.-1]). After this acclimation period, the silver catfish were fed and placed in individual chambers (ten fish for each size range) with approximately 20 times their volume in water. Water was collected from each chamber at 0, 6, 12, 24, 36, and 48h after the transfer and the ammonia concentration was immediately measured. Fish were weighed at the end of water collection and were not fed when inside the chambers.

Dissolved oxygen (6.17 [+ or -] 0.8 mg [L.sup.-1]) and temperature (21.5 [+ or -] 1.5[degrees]C) were monitored with an oxygen meter (model Y5512). The pH levels (7.2 [+ or -] 0.2 units) were verified with a DMPH-2 pH meter, while nitrite values (0.3 [+ or -] 0.1 mg [L.sup.-1]) were assessed using a colorimetric method (commercial kit), and water alkalinity (40 [+ or -] 1.3 mg CaC[O.sub.3] [L.sup.-1]) and hardness values (36 [+ or -] 1.5 mg CaC[O.sub.3] [L.sup.-1]) were determined according to Boyd and Tucker (1992). Ammonia concentrations in the water samples were measured according to Verdouw et al. (1978), and ammonia excretion (efflux) was calculated according to Gonzalez et al. (1998). These parameters were observed in all experiments (eggs, larvae and juveniles groups).

Data are reported as means [+ or -] S.E.M. Homogeneity of variances between groups was tested by Levene's test. Comparisons of ammonia excretion at different times of embryonic development and larviculture and after fasting in juveniles were conducted using one-way ANOVA and Tukey's test (Statistica software v.5.1). The relationship between weight and ammonia excretion in silver catfish juveniles was assessed using Sigma Plot 11.0 software.

Results and discussion

All physicochemical parameters of the water were kept within the range recommended for this species throughout the experiment (BALDISSEROTTO, 2004).

Ammonia excretion by eggs was low, but when hatching started approximately 28h after fecundation, excretion increased until 48h after fecundation (Figure 1). Larger larvae (192h after fecundation) presented lower values of ammonia excretion. Therefore, the increase observed during the embryonic stage probably reflects the small but growing amount of respiring tissues and also the elimination of metabolites. However, although the egg capsule or chorion is permeable to ammonia (RAHAMAN-NORONHA et al., 1996), elimination of ammonia is slow in the absence of respiratory convection (ROMBOUGH; MOROZ, 1990, 1997) and direct contact with bulk water. The present results regarding silver catfish are in agreement with studies of ammonia excretion of embryos and larvae of other freshwater teleost species (BUCKING; WOOD, 2008; DABROWSKI et al., 1984; KAUSHIK et al., 1982; OLIVA-TELES; KAUSHIK, 1987, 1990; TERJESEN et al., 1997; WRIGHT et al., 1995). Ammonia excretion increased markedly for up to 48h after hatching, but the trend did not continue at the next sampling point. Interestingly, a similar pattern with an apparent lag phase was observed in studies of other freshwater teleost larvae (DABROWSKI et al., 1984; KAUSHIK et al., 1982; OLIVA-TELES; KAUSHIK, 1987; TERJESEN et al., 1997), and it could result from a high amino acid catabolism associated with the process of hatching.

[FIGURE 1 OMITTED]

In fasting silver catfish, there was a significant negative relationship between ammonia excretion and weight after 48h (Figure 2). This is in agreement with higher ammonia urinary excretion associated with lower body mass observed in silver catfish (BOLNER; BALDISSEROTTO, 2007), as well as in walleye, Sander vitreus (YAGER; SUMMERFELT, 1993) and tambaqui, Colossoma macropomum (ISMINO-ORBE et al., 2003). This can be attributed at least partially to ontogenetic changes in the "metabolic intensities" of the different tissues, which tend to decline as fish increase in size (WOOD, 1993).

[FIGURE 2 OMITTED]

Ammonia excretion decreased significantly after 12 and 48h of fasting (compared to 6h of fasting) in the smallest and largest specimens, respectively (Figure 3). Ammonia excretion is associated with feeding changes during the postprandial period. Several studies (Dosdat et al. (1996), with five teleost fish species divided into two weight classes, 10 and 100 g; Gelineau et al. (1998), with 70 g rainbow trout; Leung et al. (1999), with 83 g Epinephelus areolatus; Bucking and Wood (2008), with 300-400 g rainbow trout) have documented that elevated ammonia excretion rates occurred between 2 and 12h after feeding. As reported above, ammonia excretion increases during the postprandial period in fish, suggesting that internal ammonia levels have risen after feeding (WICKS; RANDALL, 2002). Interestingly, ammonia excretion increased again in small silver catfish after 24--48h of fasting. As explained earlier, small fish have a higher metabolic rate than larger fish, and it is possible that after 24h fasting they use protein rather than lipid and carbohydrate resources to generate energy. This protein catabolism would lead to an increase in ammonia excretion. In agreement with this hypothesis, rainbow trout fasted for one week presented ammonia excretion levels as high as those observed in trout 6 12h after feeding (BUCKING; WOOD, 2008).

Postprandial nitrogenous excretion is known to be influenced by the type of feed (ENGIN; CARTER, 2001; LAM et al., 2008; WEBB JR.; GATLIN III, 2003) and fish size (JOBLING, 1981; LEUNG et al., 1999), and thus it is essential that future studies examine the intricate relationships between feed types qualities-1 and the induction of N retention mechanisms in silver catfish at different stages of development.

[FIGURE 3 OMITTED]

Conclusion

In conclusion, during the incubation of silver catfish eggs, water renovation must be increased at hatching time to avoid a build-up of ammonia. Additionally, since ammonia excretion in this species increases after feeding, feeding must be discontinued when ammonia levels in the tanks are high, to avoid a further increase of this metabolite and consequent fish mortality.

Acknowledgements

N. Braun received CAPES (Coordenacao de Aperfeicoamento de Pessoal de Nivel Superior, Brazil) fellowships, and A. G. Becker, V. L. Loro and B. Baldisserotto received CNPq (Conselho Nacional de Desenvolvimento Cientifico e Tecnologico) fellowships. This study was supported by CNPq (process number 475017/03-0).

Doi: 10.4025/actascianimsci.v34i1.11898

References

ALTINOK, I.; GRIZZLE, J. M. Excretion of ammonia and urea by phylogenetically diverse fish species in low salinities. Aquaculture, v. 238, n. 1-4, p. 499-507, 2004.

AMORIM, M. P.; GOMES, B. V. C.; MARTINS, Y. S.; SATO, Y.; RIZZO, E.; BAZZOLI, N. Early development of the silver catfish Rhamdia quelen (Quoy & Gaimard, 1824) (Pisces: Heptapteridae) from the Sao Francisco River basin,

Brazil. Aquaculture Research, v. 40, n. 2, p. 172-180, 2009. BALDISSEROTTO, B. Silver catfish culture. World Aquaculture, v. 35, n. 4, p. 65-67, 2004.

BOLNER, K. C. S.; BALDISSEROTTO, B. Water pH and urinary excretion in silver catfish Rhamdia quelen. Journal of Fish Biology, v. 70, n. 1, p. 50-64, 2007.

BOYD, C. E.; TUCKER, C. S. Water quality and pond soil analysis for aquaculture. Alabama Agricultural Experiment Station. Alabama: Auburn University, 1992.

BUCKING, C.; WOOD, C. M. The alkaline tide and ammonia excretion after voluntary feeding in freshwater rainbow trout. The Journal of Experimental Biology, v. 211, n. 15, p. 2533-2541, 2008.

CHEW, S. F.; WILSON, J. M.; IP, Y. K.; RANDALL, D. J. Nitrogenous excretion and defense against ammonia toxicity. In: VAL, A.; ALMEIDA-VAL, V.; RANDALL, D. J. (Ed.). Fish physiology. The physiology of tropical fishes. New York: Academic Press, 2006. p. 307-395.

DABROWSKI, K.; KAUSHIK, S. J.; LUQUET, P. Metabolic utilization of body stores during the early life of whitefish Coregonus lavaretus L. Journal of Fish Biology, v. 24, n. 6, p. 721-729, 1984.

DOS DAT, A.; SERVAIS, F.; METAILLER, R.; HUELVAN, C.; DESBRUYERES, E. Comparison of nitrogenous losses in five teleost fish species. Aquaculture, v. 141, n. 1-2, p. 107-127, 1996.

ENGIN, K.; CARTER, C. G. Ammonia and urea excretion rates of juvenile Australian short-finned eel (Anguilla australis australis) as influence by dietary protein level. Aquaculture, v. 194, n. 1-2, p. 123-136, 2001.

FELIPO, V.; BUTTERWORTH, R. F. Neurobiology of ammonia. Progress in Neurobiology, v. 67, n. 4, p. 259-279, 2002.

GELINEAU, A.; MEDALE, F.; BOUJARD, T. Effect of feeding time on postprandial nitrogen excretion and energy expediture in rainbow trout. Journal of Fish Biology, v. 52, n. 4, p. 655-664, 1998.

GOMES, L. C.; GOLOMBIESKI, J. I.; CHIPPARIGOMES, A. R.; BALDISSEROTTO, B. Biologia do jundia (Rhamdia quelen; Teleostei, Pimelodidae). Ciencia Rural, v. 30, n. 1, p. 179-185, 2000.

GONZALEZ, R. J.; WOOD, C. M.; WILSON, R. W.; PATRICK, M. L.; BERGMAN, H. L.; NARAHARA, A.; VAL, A. L. Effects of water pH and calcium concentration on ion balance in fish of the Rio Negro, Amazon. Physiological Zoology, v. 71, n. 1, p. 15-22, 1998.

IP, Y. K.; CHEW, S. F.; WILSON, J. M.; RANDALL, D. J. Defenses against ammonia toxicity in tropical air-breathing fishes exposed to high concentrations of environmental ammonia: a review. Journal of Comparative Physiology--Part A, v. 174, n. 7, p. 565-575, 2004.

ISMINO-ORBE, R. A.; ARAUJO-LIMA, C. A. R. M.; GOMES, L. C. Excrecao de amonia por tambaqui (Colossoma macropomum) de acordo com variacoes na temperatura da agua e massa do peixe. Pesquisa Agropecuaria Brasileira, v. 38, n. 10, p. 1243-1247, 2003.

JOBLING, M. Some effects of temperature, feeding and body weight on nitrogenous excretion in young plaice Pleuronectes platessa L. Journal of Fish Biology, v. 18, n. 1, p. 87-96, 1981.

KAUSHIK, S. J.; DABROWSKI, K.; LUQUET, P. Patterns of nitrogen excretion and oxygen consumption during ontogenesis of common carp (Cyprinus carpio). Canadian Journal of Fisheries and Aquatic Sciences, v. 39, n. 8, p. 1095-1105, 1982.

LAM, S. S.; AMBAK, M. A.; JUSOH, A.; LAW, A. T. Waste excretion of marble goby (Oxyeleotris marmorata Bleeker) fed with different diet. Aquaculture, v. 274, n. 1, p. 49-56, 2008.

LEGENDRE, M.; LINHART, R.; BILLARD, R. Spawning and management of gametes fertilized eggs and embryos in Siluroidei. Aquatic Living Resources, v. 9, n. 1, p. 59-80, 1996.

LEUNG, K. M. Y.; CHU, J. C. W.; WU, R. S. S. Effects of body weight, water temperature and ration size on ammonia excretion by aerolated grouper (Epinephelus areolatus) and mangrove snapper (Lutjanus argentimaculatus). Aquaculture, v. 170, n. 3-4, p. 215-227, 1999.

OLIVA-TELES, A.; KAUSHIK, S. J. Nitrogen and energy metabolism during the early ontogeny of diploid and triploid rainbow trout (Salmo gairdneri R.). Comparative Biochemistry and Physiology--Part A, v. 87, n. 1, p. 157-160, 1987.

OLIVA-TELES, A.; KAUSHIK, S. J. Effect of temperature on utilization of endogenous energy reserves during embryonic development of diploid and triploid rainbow trout (Salmo gairdneri R.). Aquaculture, v. 84, n. 3-4, p. 373-382, 1990.

PEREIRA, C. R.; BARCELLOS, L. J. G.; KREUTZ, L. C.; QUEVEDO, R. M.; RITTER, F.; SILVA, L. B. Embryonic and larval development of jundia (Rhamdia quelen, Quoy & Gaimard, 1824, Pisces, Teleostei) a South American catfish. Brazilian Journal of Biology, v. 66, n. 4, p. 1057-1063, 2006.

RAHAMAN-NORONHA, E.; O'DONNELL, M. J.; PILLEY, C. M.; WRIGHT, P. A. Excretion and distribution of ammonia and the influence of boundary layer acidification in embryonic rainbow trout (Oncorhynchus mykiss). Journal of Experimental Biology, v. 199, n. 12, p. 2713-2723, 1996.

ROMBOUGH, P. J.; MOROZ, B. M. The scaling and potential importance of cutaneous and branchial surfaces in respiratory gas exchange in young chinook salmon (Oncorhynchus tshawytscha). Journal of Experimental Biology, v. 154, n. 1, p. 1-12, 1990.

ROMBOUGH, P. J.; MOROZ, B. M. The scaling and potential importance of cutaneous and branchial surfaces in respiratory gas exchange in larval and juvenile walleye Stizostedion vitreum. Journal of Experimental Biology, v. 200, n. 18, p. 2459-2468, 1997.

TERJESEN, B. F.; VERRETH, J.; FYHN, H. J. Urea and ammonia excretion by embryos and larvae of the African catfish, Clarias gariepinus (Burchell 1822). Fish Physiology and Biochemistry, v. 16, n. 4, p. 311-321, 1997.

VERDOUW, H.; Van ECHTELD, C. J. A.; DEKKERS, E. M. J. Ammonia determination based on indophenol formation with sodium salicylate. Water Research, v. 12, n. 6, p. 399-402, 1978.

WEBB JR., K. A.; GATLIN III, D. M. Effects of dietary protein level and form on production characteristics and ammonia excretion of red drum Sciaenops ocellatus. Aquaculture, v. 225, n. 1-4, p. 17-26, 2003.

WICKS, B. J.; RANDALL, D. J. The effect of sub-lethal ammonia exposure on fed and unfed rainbow trout: the role of glutamine in regulation of ammonia. Comparative Biochemistry and Physiology--Part A, v. 132, n. 2, p. 275-285, 2002.

WILKIE, M. P. Ammonia excretion and urea handling by the fish gills: present understanding and future research challenges. Journal of Experimental Zoology, v. 293, n. 3, p. 284-301, 2002.

WOOD, C. M. Ammonia and urea metabolism and excretion. In: EVANS, D. (Ed.). The Physiology of Fishes. Boca Raton: CRC Press, 1993. p. 379-425.

WRIGHT, P. A.; FELSKIE, A.; ANDERSON, P. M. Induction of ornithine-urea cycle enzymes and nitrogen metabolism and excretion in rainbow trout (Oncorhynchus mykiss) during early life stages. Journal of Experimental Biology, v. 198, n. 1, p. 127-135, 1995.

YAGER, T. K.; SUMMERFELT, R. C. Effects of fish size and feeding frequency on metabolism of juvenile walleye. Aquacultural Engineering, v. 12, n. 1, p. 19-36, 1993.

Received on December 16, 2010.

Accepted on April 29, 2011.

Luciano de Oliveira Garcia (1), Neiva Braun (2), Alexssandro Geferson Becker (1), Vania Lucia Loro (3) and Bernardo Baldisserotto (1) *

(1) Laboratorio de Fisiologia de Peixes, Departamento de Fisiologia e Farmacologia, Universidade Federal de Santa Maria, Av. Roraima, 1000, 97105-900, Santa Maria, Rio Grande do Sul, Brazil. (2) Departamento de Aquicultura, Universidade Federal de Santa Catarina, Florianopolis, Santa Catarina, Brazil. (3) Laboratorio de Bioquimica Adaptativa, Departamento de Quimica, Universidade Federal de Santa Maria, Santa Maria, Rio Grande do Sul, Brazil. * Author for correspondence. E-mail: bbaldisserotto@hotmail.com
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Author:Garcia, Luciano de Oliveira; Braun, Neiva; Becker, Alexssandro Geferson; Loro, Vania Lucia; Baldisse
Publication:Acta Scientiarum. Animal Sciences (UEM)
Date:Jan 1, 2012
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