Printer Friendly

Ovarian histology and fecundity in the evaluation of the reproduction of the invasive species Serrasalmus marginatus (Characidae) on a neotropical floodplain/Histologia ovariana e fecundidade na avaliacao da reproducao da especie invasora Serrasalmus marginatus (Characidae) em uma planicie de inundacao neotropical.


Invasion of species is one of the main causes of biodiversity loss leading to both environmental and economic damage (McNeely, 2001; Molnar, Gamboa, Revenga, & Spalding, 2008; Pejchar & Mooney, 2009; Keller, Geist, Jeschke, & Kuhn, 2011; Simberloff et al., 2013). Invasive species have some characteristics that facilitate or allow their establishment in a new environment (e.g. high trophic plasticity and dispersion capacity) (Lodge, 1993; Marchetti, Moyle, & Levine, 2004). As regards freshwater ecosystems, fish have received special attention due to the quantity of invasive species recorded in recent years, especially carp, tilapia and African catfish (Garcia, Loebmann, Vieira, & Bemvenuti, 2004; Vitule, Umbria, & Aranha, 2006; Russel, Thuesen, & Thomson, 2012).

The upper Parana River, possessing high species richness, according to Langeani et al. (2007), underwent a massive invasion due to the formation of the Itaipu Reservoir, which eliminated the natural geographic barrier Salto de Sete Quedas (Julio Jr, Dei Tos, Agostinho, & Pavanelli, 2009), which had separated the faunas of the middle and upper Parana River. Consequently, about 33 species became invaders, characterizing one of the largest invasions of freshwater species in South America (Skora, Abilhoa, Padial, & Vitule, 2015).

With the flooding, the piranha Serrasalmus marginatus Valenciennes, 1837 successfully colonized the upper Parana River basin. Its success increased with the construction of the Piracema Channel in the Itaipu Reservoir, where this species has been recorded (Makrakis, Gomes, & Makrakis, 2007). It is distributed in the Parana-Paraguay river basin, lives in both lentic and lotic environments, carries out short-distance migrations (Graca & Pavanelli, 2007) and has been indicated as the principal cause of the decrease in the population of its native congener (Agostinho & Julio Jr, 2002). In addition, S. marginatus is an iteroparous, gonochoristic, monomorphic, oviparous species with external fecundation. It reaches sexual maturity at 11.5 cm standard length for males and 12.2 cm standard length for females and all individuals are able to reproduce at 13.0 cm standard length (Suzuki, Vazzoler, Marques, Lizama, & Inada, 2004). Moreover, it possesses batch spawning, parental care and a long reproductive period (September to April) (Vazzoler, 1996; Suzuki et al., 2004), coinciding with the season of higher temperatures and flooding.

One way to evaluate the reasons for the success of S. marginatus is to study its reproductive activity and capacity, since reproducing and maintaining the population is one of the precepts for obtaining success in a new environment. The reproductive capacity of fish can be quantified using the following measurements: maturation length or age, type of fecundity, fecundity, duration of the reproductive season, spawning behavior, and spawning fraction. Information about reproductive potential is fundamental to spawning stock biomass evaluation (Hunter, Macewicz, Lo, & Kimbrell, 1992; Murua et al., 2003; Ganias, 2013; Ganias, Lowerre-Barbieri, & Cooper, 2015). Thus, this work aims to: i) validate the reproductive phases of the females using light microscopy; ii) estimate the fecundity and iii) evaluate the reproduction areas of the S. marginatus population from the upper Parana River floodplain.

Material and methods

Study area

The upper Parana River floodplain is located downstream from the Engenheiro Sergio Mota (Porto Primavera) Hydroelectric Power Plant and upstream from the Itaipu Reservoir. This distance (approximately 250 km) is the last dam-free stretch of the Parana River in Brazil (Agostinho & Zalewski, 1996). Although the floodplain is located between two large dams, the Parana River possesses two important tributaries, the Baia and Ivinheima rivers, which contribute to the maintenance of biodiversity and ideal conditions for the entire aquatic fauna, mainly the ichthyofauna.


The fish were collected quarterly (March, June, September and November/December 2013, 2014 and 2015) from 9 sampling sites on the upper Parana River floodplain: 1--Baia River (Rbai), 2--Ivinheima River (Rivi), 3--Parana River (Rpar), 4--Guarana Lagoon (Lgua), 5--Patos Lagoon (Lpat), 6--Parana River in the Garcas Lagoon (Lgar), 7--Ressaco do Pau Veio Lagoon (Lpve), 8--Baia River in the Fechada Lagoon (Lfec) and 9--Ivinheima River in the Ventura Lagoon (Lven) (Figure 1).

The samplings were carried out using 11 gill nets (meshes: 2.4; 3; 4; 5; 6; 7; 8; 10; 12; 14; 16 cm, between opposite knots) and two trammel nets (meshes: 6; 8 cm). The nets were exposed for 24 hours at every site and checked between 8:00 and 9:00 (night-morning), 16:00 and 17:30 (daytime) and 22:00 and 23:30 (evening-night). In addition, bottom otter trawls (20 m long; 0.5 cm mesh) were carried out during the day in the coastal areas of every lagoon. The fish were anesthetized and euthanized using 0.1% ethyl aminobenzoate (benzocaine), according to the protocols of Summerfelt and Smith (1990) and approved by CEUA (Committee for the Ethical Use of Animals) (Universidade Estadual de Maringa).

The following data were recorded for each individual: catch site, catch date, standard length (cm), total weight to the nearest 0.01 g, gonadal development phases based on the macroscopic characteristics of the ovary, total weight of the gonads (twg) to the nearest 0.01 g and weight of the ovarian fractions (wof) to the nearest 0.01 g.

Reproductive characterization

The ovarian development phases were attributed according to the macroscopic characteristics proposed by Brown-Peterson, Wyanski, Saborido-Rey, Macewicz, and Lowerre-Barbieri (2011), Wildner, Grier, and Quagio-Grassiotto (2013) and Quagio-Grassiotto, Wildner, and Ishiba (2013). A fraction of the left lobe of the ovary was fixed in Bouin solution for at least 48 hours, dehydrated in ethanol, infiltrated using Historesin and shaped into blocks, which were cross-sectioned at a thickness of 5 [micro]m and stained using 0.5% Toluidine Blue, Hematoxilin/Eosin and periodic acid Schiff/ hematoxylin/metanil yellow (Quinte ro-Hunter, Grier, & Muscato, 1991). The germ cells were identified according to Grier, Uribe-Aranzabal, and Patino (2009) and Wildner et al. (2013) and the reproductive phases attributed macroscopically (early developing subphase, developing phase, spawning capable phase, actively spawning subphase, regressing phase and regenerating phase) were validated by the microscopic characteristics of the development stages of more advanced cell types, according to Brown-Peterson et al. (2011), Quagio-Grassiotto et al. (2013) and Wildner et al. (2013).

In order to determine type of fecundity, ovaries from individuals in the developing phase, spawning capable phase and actively spawning subphase were selected. The right lobe of the ovary was fixed in 10% buffered formalin. Using the gravimetric method, the oocytes were counted and measured from three subsamples of approximately 0.3 g each from the anterior, middle and posterior region of the right lobe of the ovary (Hunter, Lo, & Leong, 1985; Murua et al., 2003).

The diameter of the oocytes from 12 specimens of S. marginatus was measured using a stereomicroscope equipped with an ocular micrometer to determine the type of oocyte development and spawning. The type of spawning was determined according to the frequency distribution of the oocytes per diameter class (Murua & Saborido-Rey, 2003).

Thus, absolute fecundity (AF), i.e. the number of oocytes that a female will spawn in the next reproductive period, was calculated according to Vazzoler (1996).

The floodplain reproduction sites were identified by number of females in different reproductive phases.


A total of 765 females with 3.9 to 24.9 cm standard length were used for macroscopic characterization of the gonads at the different sites of the floodplain. The sites having the greatest representativeness were Patos Lagoon (231 individuals), Ivinheima River (214) and Ventura Lagoon (70). In the Baia River, 145 individuals were collected, while 51 and 18 were collected in the Fechada and Guarana lagoons, respectively. The sites having the fewest number of samples were the Garcas Lagoon, Parana River, and Ressaco do Pau Veio Lagoon, with eight, twenty-three and five individuals, respectively.

Based on the microscopic diagnosis of the germ lineage, cysts with a batch of oogonia surrounded by prefollicle cells, pachytene oocytes, primary growth oocytes, early and late secondary growth oocytes, a full-grown oocyte (Figure 2 and Table 1) and oocyte maturation (Figure 3J) were recognized in S. marginatus. The postovulatory follicle complex recorded after ovulation and follicular atresia showed oocytes unable to ovulate (Figure 2H, I).

Histological sections of the ovaries showing the development phases were detailed and described (Figure 3 and Table 2).

The diameter of the vitellogenic oocytes of S. marginatus varied from 300 to 1700 [micro]m (Figure 4), and the trends reveal asynchronous development of the oocytes and batch spawning. Only a portion of the oocytes is spawned in each batch after reaching maturation and ovulation.

The diameter of the vitellogenic oocytes of S. marginatus varied from 300 to 1700 [micro]m (Figure 4), and the trends reveal asynchronous development of the oocytes and batch spawning. Only a portion of the oocytes is spawned in each batch after reaching maturation and ovulation.

The absolute fecundity estimated for six individuals whose total length varied from 16.4 to 20.2 cm, varied from 410 to 752 oocytes. As regards the different rivers of the upper Parana River floodplain, the piranha S. marginatus shows reproductive activity in every studied environment; however, it is more frequent in Patos Lagoon and the Ivinheima and Baia rivers, successfully occupying the lotic waters of the rivers and the lentic waters of the lagoon (Figure 5). Among the principal environments (Ivinheima, Baia and Parana), S. marginatus is least reproductively active in the Parana River. The main channel of the Parana River did not have any individuals in advanced stages of gonadal development (Figure 5).


A fish must allocate time and resources for reproduction to be represented genetically in the next generation (Wootton, 1998). The reproductive success of fish thus depends on their reproductive rate, the survival rate of their descendants until the age of reproduction, spawning type and number of reproductive opportunities (Wootton, 1998; Murua & Saborido-Rey, 2003; Lowerre-Barbieri, 2009). The reproductive strategy of S. marginatus may be considered opportunist, which is characteristic of species that have a short gestation period, are small in size and invest little in their offspring (Winemiller & Rose 1992; Winemiller, 2005), enabling them to rapidly populate different habitats and invade new ones. The capacity to spawn during the entire reproductive season is a species life-history trait that allows the maintenance of population levels even in situations of environmental disturbance (e.g. suppression of Sete Quedas barrier that permitted the passage of species from the middle to upper Parana River (Julio Jr et al., 2009)).

Over each reproductive cycle, the renewal of germ cells, their differentiation, development, maturation and release result in gonadal alterations that characterize different reproductive phases. The reproductive phases attributed macroscopically to S. marginatus were confirmed through light microscopy. They are developing, spawning capable, regressing and regenerating, according to Brown-Peterson et al. (2011). These phases are used because they are simpler and in Brazil have been adopted by Wildner et al. (2013) for Serrasalmus maculatus, Quagio-Grassiotto et al. (2013) for Hoplias malabaricus and Sorubim lima and Agostinho et al. (2015) for Hemiodus orthonops.

Fish species with asynchronous ovarian development exhibit strategies of determinate or indeterminate fecundity (Hunter et al., 1985; Murua et al., 2003; Murua & Saborido-Rey, 2003). These strategies relate to the pattern and time lag in which the pre-vitellogenic oocytes (primary growth) are recruited to compose the stock of vitellogenic oocytes (secondary growth). In indeterminate fecundity, vitellogenesis continues after the start of spawning (Hunter et al., 1985; Murua & Saborido-Rey, 2003; Murua et al., 2003; Ganias et al., 2015).

The fecundity of the batches, spawning frequency and duration of the reproductive season must be known to estimate indeterminate fecundity (Hunter et al., 1992; Murua & Saborido-Rey, 2003; Murua et al., 2003). The patterns of total spawning and partial spawning and the type of fecundity (determinate or indeterminate) have been recorded for marine and freshwater species (Brown-Peterson et al., 2011). Among the 41 species from the upper Parana River that were studied as regards spawning type, 73% possess batch spawning and, therefore, indeterminate fecundity (Vazzoler, 1996).

The frequency of the diameter of the oocytes and the microscopic record of the different types of oocytes that develop in the reproductive cycle show that their development is asynchronous in S. marginatus; therefore, it exhibits a reproductive strategy of batch spawning and indeterminate fecundity. Fecundity (estimated) varying from 410 to 752 has guaranteed the reproductive success of this species. This strategy of batch spawning and indeterminate fecundity has been recorded for Loricariichthys castaneus (Gomes, Araujo, Uehara, & Sales, 2011) and Serrasalmus maculatus (Wildner et al., 2013).

Adequate environmental conditions and sites for larval development and juvenile growth are fundamental to the population success of any species. Our results demonstrate that most of the reproductive stages predominate in the Baia and Ivinheima rivers, mainly spawning capable individuals, which are in great number in the lagoons associated with these two rivers. These rivers belong to the upper Parana River floodplain and are two of the main tributaries responsible for the maintenance of ichthyofaunistic diversity and serve as nursery and growth areas, mainly for migratory species (Agostinho, Thomaz, Minte-Vera, & Winemiller, 2000; Reynalte-Tataje, Agostinho, & Bialetzki, 2013). Therefore, these sites are characterized by possessing adequate conditions for the establishment of S. marginatus and, consequently, the population increase of this species results in negative impacts for the native species S. maculatus, as the two are congeners that have similar environmental and feeding requirements (Agostinho & Julio Jr, 2002; Agostinho, 2003; Alexandre, Luiz, Piana, Gomes, & Agostinho, 2004).


The reproductive success of S. marginatus on the upper Parana River floodplain is attributed to parental care and greater aggressiveness in defending its feeding and reproduction territories (Agostinho, 2003; Alexandre et al., 2004). However, it is also associated with fecundity, because the long reproductive period with the continual spawning of oocytes guarantees more descendants. Serrasalmus marginatus reproduction is intense in lotic (river) environments and moderate in channels and lagoons of the upper Parana River floodplain (Vazzoler, 1996; Agostinho, 2003; Suzuki et al., 2004). This study reveals that its reproductive success continues to be recorded in the Ivinheima River and in the lagoons of the upper Parana River floodplain.

Doi: 10.4025/actascibiolsci.v39i3.33021


We thank Dr. Liliana Rodrigues for the support received by the Programa de Pesquisa Ecologica de Longa Duracao (PELD) and the Nucleo de Pesquisas em Limnologia, Ictiologia e Aquicultura (Nupelia) for technical personnel, researchers and logistical support. Dr. Luiz C. Gomes provided financial support. We also thank the Fundacao Araucaria for granting a scientific initiation scholarship to Gabriele S. R. de Melo, the Complexo de Centrais de Apoio a Pesquisa (COMCAP) for equipment support and the anonymous reviewers for their helpful comments.


Agostinho, A. A., Suzuki, H. I., Fugi, R., Alves, D. C., Tonella, L. H., & Espindola L. A. (2015). Ecological and life history traits of Hemiodus orthonops in the invasion process: looking for clues at home. Hydrobiologia, 746(1), 415-430.

Agostinho, A. A. Thomaz, S. M., Minte-Vera, C. V., & Winemiller, K. O. (2000). Biodiversity in the high Parana River floodplain. In Gopal, B., Junk, W. J., Davis, J. A. (Eds.), Biodiversity in wetlands: assessment, function and conservation (p. 89-118). Leiden, NL: Backhuys Publishers.

Agostinho, A. A., & Zalewski, M. (1996). A planicie alagavel do alto rio Parana: importancia e preservacao. Maringa, PR: Eduem.

Agostinho, C. S. (2003). Reproductive aspects of piranhas Serrasalmus spilopleura and Serrasalmus marginatus into the upper Parana River, Brazil. Brazilian Journal of Biology, 63(1), 1-6.

Agostinho, C. S., & Julio Jr., H. F. (2002). Observation of an invasion of the piranha Serrasalmus marginatus Valenciennes, 1847 (Osteichthyes, Serrasalmidae) into the Upper Parana River, Brazil. Acta Scientiarum. Biological Sciences, 24(2), 391-395.

Alexandre, P. C., Luiz, E. A., Piana, P. A., Gomes, L. C., & Agostinho A. A. (2004). Relacao estoque recrutamento para as piranhas Serrasalmus marginatus (Valenciennes, 1847) e S. maculatus (Kner, 1860) no rio Baia, alto rio Parana. Acta Scientiarum. Biological Sciences, 26(3), 303-307.

Brown-Peterson, N. J., Wyanski, D. M., Saborido-Rey, F., Macewicz, B. J., & Lowerre-Barbieri, S. K. (2011). A standardized terminology for describing reproductive development in fishes. Marine and Coastal Fisheries: Dynamics, Management, and Ecosystem Science, 3(1), 52-70.

Ganias, K. (2013). Determining the indeterminate: Evolving concepts and methods on the assessment of the fecundity pattern of fishes. Fisheries Research, 138, 23-30. doi: 10.1016/j.fishres.2012.05.006

Ganias, K., Lowerre-Barbieri, S. K., & Cooper, W. (2015). Understanding the determinate-indeterminate fecundity dichotomy in fish populations using a temperature dependent oocyte growth model. Journal of Sea Research, 96, 1-10. doi: 10.1016/j.seares.2014.10.018

Garcia, A. M., Loebmann, D., Vieira, J. P., & Bemvenuti, M. A. (2004). First records of introduced carps (Teleostei, Cyprinidae) in the natural habitats of Mirim and Patos Lagoon estuary, Rio Grande do Sul, Brazil. Revista Brasileira de Zoologia, 21(1),157-159.

Gomes, I. D., Araujo, F. G., Uehara, W., & Sales, A. (2011). Reproductive biology of the armoured catfish Loricariichthys castaneus. (Castelnau, 1855) in Lajes reservoir, southeastern Brazil. Journal of Applied Ichthyology, 27(6), 1322-1331.

Graca, W. J., & Pavanelli, C. S. (2007). Peixes da planicie de inundacao do alto rio Parana e areas adjacentes. Maringa, PR: Eduem.

Grier, H. J., Uribe-Aranzabal M. C, & Patino, R. (2009). The ovary, folliculogenesis, and oogenesis in Teleosts. In B. G. M. Jamieson, (Ed.), Reproductive biology and phylogeny of fishes: agnathans and bony fishes (p. 25-84). Enfield: Science Publishers.

Hunter, J. R., Lo, N. C-H., & Leong, R. J. H. (1985). Batch fecundity in multiple spawning fishes. In R. Lasker, (Ed.), An egg production method for estimating spawning biomass of pelagic fish: application to the northern anchovy Engraulis mordax (p. 67-78). US Department of Commerce, National Atmospheric and Atmospheric Administration Technical Report NMFS 36. Washington, D.C.: Government Printing Office.

Hunter, J. R., Macewicz, B. J., Lo, N. C-H., & Kimbrell, C. A. (1992). Fecundity, spawning, and maturity of female Dover sole Microstomus pacificus, with an evaluation of assumptions and precision. Fishery Bulletin, 90(1), 101-128.

Julio Jr., H. F., Dei Tos, C., Agostinho, A. A., & Pavanelli, C. S. (2009). A massive invasion of fish species after eliminating a natural barrier in the upper Rio Parana basin. Neotropical Ichthyology, 7(4), 709-718.

Keller, R. P., Geist, J., Jeschke, J. M., & Kuhn, I. (2011). Invasive species in Europe: ecology, status, and policy. Environmental Sciences Europe, 23(23), 1-17.

Langeani, F., Castro, R. M. C., Oyakawa, O. T., Shibatta, O. A., Pavanelli, C. S., & Casatti, L. (2007). Diversidade da ictiofauna do Alto Rio Parana: composicao atual e perspectivas futuras. Biota Neotropica, 7(3), 181-197.

Lodge, D. M. (1993). Biological Invasions: Lessons for Ecology. Trends in Ecology & Evolution, 8(4), 133-137.

Lowerre-Barbieri, S. K. (2009). Reproduction in relation to conservation and exploitation of marine fishes. In B. G. M. Jamieson, (Ed.), Reproductive biology and phylogeny of fishes: agnathans and bony fishes (p. 371-394). Enfield: Science Publishers.

Makrakis, S., Gomes, L. C., & Makrakis, M. C. (2007). The Canal da Piracema at Itaipu Dam as a fish pass system. Neotropical Ichthyology, 5(2), 185-195.

Marchetti, M. P., Moyle, P. B., & Levine, R. (2004). Invasive species profiling? Exploring the characteristics of non-native fishes across invasion stages in California. Freshwater Biology, 49(5), 646-661.

McNeely, J. (2001). Invasive species: a costly catastrophe for native biodiversity. Land Use and Water Resources Research, 1(2), 1-10.

Molnar, J. L., Gamboa, R. L., Revenga, C., & Spalding, M. D. (2008). Assessing the global threat of invasive species to marine biodiversity. Frontiers in Ecology and the Environment, 6(9), 485-492.

Murua, H., & Saborido-Rey, F. (2003). Female reproductive strategies of marine fish species of the North Atlantic. Journal of Northwest Atlantic Fishery Science, 33, 23-31.

Murua, H., Kraus, G., Saborido-Rey, F., Witthames, P. R., Thorsen, A., & Junqueira, S. (2003). Procedures to Estimate Fecundity of Marine Fish Species in Relation to their Reproductive Strategy. Journal of Northwest Atlantic Fishery Science, 33, 33-54. doi: 10.2960/J.v33.a3

Pejchar, L., & Mooney, H. A. (2009). Invasive species, ecosystem services and human well-being. Trends in Ecology & Evolution, 24(9), 497-504.

Quagio-Grassiotto, I., Wildner, D. D., & Ishiba, R. (2013). Gametogenese de peixes: aspectos relevantes para o manejo reprodutivo. Revista Brasileira de Reproducao Animal, 37(2), 181-191.

Quintero-Hunter, I., Grier, H., & Muscato, M. (1991). Enhancement of histological detail using metanil yellow as counterstain in periodic acid/Schiff' s hematoxylin staining of glycol methacrytlate tissue sections. Journal Biotechnic Histochemistry, 66(4), 169-172.

Reynalte-Tataje, D. A., Agostinho, A. A., & Bialetzki, A. (2013). Temporal and spatial distribution of the fish larval assemblages of the Ivinheima River sub-basin (Brazil). Environmental Biology of Fishes, 96(7), 811-822.

Russel, D. J., Thuesen, P. A., & Thomson, F. E. (2012). Reproductive strategies of two invasive tilapia species Oreochromis mossambicus and Tilapia mariae in northern Australia. Journal of Fish Biology, 80(6), 2176-2197.

Simberloff, D., Martin, J-L., Genovesi, P., Maris, V., Wardle, D. A., Aronson, ... Vila, M. (2013). Impacts of biological invasions: what's what and the way forward. Trends in Ecology & Evolution, 28(1), 58-66.

Skora, F., Abilhoa, V., Padial, A. A., & Vitule, J. R. S. (2015). Darwin's hypotheses to explain colonization trends: evidence from a quasi-natural experiment and a new conceptual model. Diversity and Distributions, 21(5), 583-594.

Summerfelt, R. C., & Smith, L. S. (1990). Anesthesia, surgery, and related techniques. In C. B. Shreck, P. B. Moyle (Eds.), Methods for fish biology (p. 213-272). Bethesda: American Fisheries Society.

Suzuki, H. I., Vazzoler, A. E. A. M., Marques, E. E., Lizama, M. A. P., & Inada, P. (2004). Reproductive Ecology of the fish assemblages. In S. M. Thomaz, A. A. Agostinho, N. S. Hahn (Eds.), The upper Parana River and its floodplain: physical aspects, ecology and conservation (p. 271-291). Leiden, NL: Backhuys.

Vazzoler, A. E. A. M. (1996). Biologia da reproducao de peixes teleosteos: teoria e pratica. Maringa, PR: Eduem.

Vitule, J. R. S., Umbria, S. C., & Aranha, J. M. R. (2006). Introduction of the African catfish Clarias gariepinus (Burchell, 1822) into Southern Brazil. Biological Invasions, 8(4), 677-681.

Wildner, D. D., Grier, H., & Quagio-Grassiotto, I. (2013). Female germ cell renewal during the annual reproductive cycle in Ostariophysians fish. Theriogenology, 79(4), 709-724.

Winemiller, K. O. (2005). Life history strategies, population regulation, and implications for fisheries management. Canadian Journal of Fisheries and Aquatic Sciences, 62(4), 872-885.

Winemiller, K. O., & Rose, K. A. (1992). Patterns of life-history diversification in North American fishes: implications for population regulation. Canadian Journal of Fisheries and Aquatic Sciences, 49(10), 2196-2218.

Wootton, R. J. (1998). Ecology of Teleost Fish (2nd ed.). Dordrecht, DE: Kluwer Academic Publishers.

Received on August 8, 2016.

Accepted on March 9, 2017.

Gabriele Sauthier Romano de Melo (1), Herick Soares de Santana (2) and Claudenice Dei Tos (3) *

(1) Curso de graduacao em Ciencias Biologicas, Departamento de Biologia, Universidade Estadual de Maringa, Maringa, Parana, Brazil. (2) Programa de Pos-Graduacao em Ecologia de Ambientes Aquaticos Continentais, Universidade Estadual de Maringa, Maringa, Parana, Brazil. (3) Departamento de Biologia, Nucleo de Pesquisas em Limnologia, Ictiologia e Aquicultura, Universidade Estadual de Maringa, Av. Colombo, 5790, 87020-900, Maringa, Parana, Brazil. * Author for correspondence. E-mail:

Caption: Figure 1. Study area and location of the sampling sites (Baia River--1; Ivinheima River--2; Parana River--3; Guarana Lagoon--4; Patos Lagoon--5; Garcas Lagoon--6; Ressaco do Pau Veio Lagoon--7; Fechada Lagoon--8; Ventura Lagoon--9) on the upper Parana River floodplain.

Caption: Figure 2. Oocyte development in Serrasalmus marginatus. Light microscopy, PAS/Hematoxylin/ Metanil Yellow (A, B, F, G, H, I), Hematoxilin/Eosin (C, E) and Toluidine Blue (D). (A) Nest of oogonia is surrounded and among pre-follicle cells, forming germline cysts. Inside this nest the oogonia are spherical and voluminous and their nucleus widens with an evident nucleolus, bar = 22 [micro]m. (B) Cell nest with pachytene oocytes, bar = 29 [micro]m. (C) Ovarian follicle with primary growth oocyte, bar = 70 [micro]m. (D) Late primary growth oocyte shows the beginning of the formation of the cortical alveoli, bar = 145 [micro]m. (E) Early secondary growth oocyte begins the deposition of yolk, formation of the cortical alveolus, bar = 295 [micro]m. (F), Late secondary growth oocyte, bar = 295 [micro]m. (G) Full-grown oocyte, bar = 590 [micro]m. (H) The postovulatory follicle complex, bar = 295 [micro]m. (I) Follicular atresia, bar = 295 [micro]m. CA, cortical alveoli; AF, atretic follicle; BM, basement membrane; F, follicle cell; FG, full-grown oocyte; LO, leptotene oocytes; N, nucleus; NU, perinuclear nucleoli; OF, ovarian follicle; OG, oogonium; OL, ovarian lumen; PF, prefollicle cells; PG, primary growth oocyte; PO, pachytene oocyte; SG, secondary growth oocyte; Y, yolk globule; ZP, zona pellucida.

Caption: Figure 3. Reproductive phases of the ovarian cycle of Serrasalmus marginatus according to oocyte differentiation stages. Light Microscopy, Toluidine Blue (A, B, C, G, H, I, M, N, O) and PAS/Hematoxylin/Metanil Yellow (D, E, F, J, K, L, P, Q, R). (A) Early development subphase, stroma contains primary and secondary oocytes, bar = 550 [micro]m. (B) Lamella contains early secondary growth oocytes, bar = 140 [micro]m. (C) Oogonia nest in the germinal epithelium, bar = 70 [micro]m. (D) Developing phase, primary and secondary growth oocytes, bar = 600 [micro]m. (E) Secondary growth oocytes present cortical alveoli and yolk globules, bar = 300 [micro]m. (F) Oocytes with numerous cortical alveoli, bar = 150 [micro]m. (G) Spawning capable phase, shows primary growth and full-grown oocytes, bar = 550 [micro]m. (H) Full-grown oocyte with central nucleus, bar = 280 [micro]m. (I) Full-grown oocyte showing amicropyle, bar = 140 [micro]m. (J) Actively spawning subphase, showing a mature oocyte, bar = 600 [micro]m. (K) Postovulatory follicle complex and primary growth oocytes, bar = 300 [micro]m. (L) Postovulatory follicle complex, bar = 80 [micro]m. (M) Regressing phase, bar = 550 [micro]m. (N) Atretic follicle, bar = 280 [micro]m. (O) Atretic follicle and primary growth oocyte, bar = 140 [micro]m. (P) Regenerating phase, bar = 600 [micro]m. (Q) Primary growth oocyte, bar = 270 [micro]m. (R) Postovulatory follicle complex, primary growth oocyte and oogonia nest, bar = 6 [micro]m. AF = atretic follicle; CA = cortical alveolus; F = follicle cells; FG = fullgrown oocytes; Mi = micropyle; MO = maturing oocyte; N= nucleus/germinal vesicle; NC = nest of oogonia; Nu = nucleolus; OG = oogonium; OL = ovarian lumen; OW = ovarian wall; PG = primary growth oocytes; POC = postovulatory follicle complex; SG = secondary growth oocytes ; Y = yolk globules; ZP = zona pellucida.

Caption: Figure 4. Frequency of the vitellogenic oocyte diameter ([micro]m) of the ovaries of the piranha Serrasalmus marginatus sampled on the upper Parana River floodplain.

Caption: Figure 5. Spatial distribution of the gonadal development phases per river and sampling site of the piranha Serrasalmus marginatus sampled on the upper Parana River floodplain. Lpat = Patos Lagoon; Lven = Ventura Lagoon; Rivi = Ivinheima River; Lfec = Fechada Lagoon; Lgua = Guarana Lagoon; Rbai = Baia River; Lgar = Garcas Lagoon; Lpve = Pau Veio Lagoon; Rpar = Parana River.
Table 1. Diagnosis of germinal cells in different stages of oocyte
development, postovulatory follicle complex (POC) and atretic
ovarian follicles of Serrasalmus marginatus on the Parana River

Stages/POC/Atresia             Microscopic Characteristics

Primary growth       Ovarian follicle with primary growth oocyte. It
                     shows intense basophilic ooplasm and the nucleus
                     or germinal vesicle with several perinuclear
                     nucleoli (Figure 2C). A gradual increase of
                     ooplasm and the appearance of cortical alveoli
                     record the end of primary growth oocytes (Figure

Early secondary      This oocyte (Figure 2E) is showing the gradual
growth               increase of yolk in the ooplasm and cortical
                     alveoli are arranged on the periphery of the
                     ooplasm during development.

Late secondary       Late secondary growth oocyte has nuclear outline
growth               more irregular, cortical alveoli are seen on
                     periphery of ooplasm and zona pellucida more
                     developed (Figure 2F).

Full-grown oocyte    This oocyte (Figure 2G) contains a slightly
                     eccentric nucleus, surrounded by ooplasm
                     completely full of yolk globules and the
                     cortical alveoli develop as a thin peripheral
                     layer in the ooplasm.

Postovulatory        After oocyte maturation the evidence of
follicle complex     ovulation in the ovarian stroma was the
                     formation of the postovulatory follicle complex
                     observed in the lamella (Figure 2H).

Follicular atresia   Unovulated oocyte becomes atretic and its
                     degeneration and removal from the ovarian
                     follicle occurs (Figures 2I).

Table 2. Phases and subphases of reproduction based on the
microscopic characteristic of germinal cells of Serrasalmus
marginatus females on the Parana River floodplain.

Phase/subphase                Microscopic Characteristics

Initial             Ovarian stroma contains more primary growth
Development         oocytes (PG) and some secondary growth oocytes
subphase            (SG) (Figure 3A). In the SG the cortical alveoli
                    and formation of yolk globules begins to appear
                    (Figure 3B). Nests containing oogonia in
                    proliferation are observed at the edge of
                    ovarian lumen (Figure 3C).

Developing          Primary and secondary growth oocytes (Figure
                    3D). In the early and late vitellogenic oocytes,
                    the formation of yolk globules progressed in
                    their oolema (Figure 3E, F).

Spawning Capabli    Primary growth and secondary growth (early,
                    late vitellogenic and full-grown oocytes)
                    (Figure 3G). Full-grown oocytes with nucleus
                    situated at the center of the ooplasm. Its yolk
                    globules abundant except on periphery (Figure
                    3H). Micropyle recorded in the full-grown
                    oocytes (Figure3I).

Actively Spawning   Maturing oocyte with germinal vesicle takes an
subphase            eccentric position on the periphery of the
                    ooplasm at the animal pole near the micropyle
                    (Figure 3J). In this subphase atretic follicle
                    and postovulatory follicle complex also occur
                    (Figure 3K, L).

Regression          Predominance of primary growth oocytes and
                    atretic follicles (Figure 3M, N, O), and an
                    absence of secondary growth oocytes.

Regeneration        Presence of primary growth oocytes,
                    proliferating oogonia forming cell nests and
                    degenerating postovulatory follicles were
                    recorded (Figure 3P, Q, R).
COPYRIGHT 2017 Universidade Estadual de Maringa
No portion of this article can be reproduced without the express written permission from the copyright holder.
Copyright 2017 Gale, Cengage Learning. All rights reserved.

Article Details
Printer friendly Cite/link Email Feedback
Author:de Melo, Gabriele Sauthier Romano; de Santana, Herick Soares; Tos, Claudenice Dei
Publication:Acta Scientiarum. Biological Sciences (UEM)
Article Type:Ensayo
Date:Jul 1, 2017
Previous Article:The genus Senna Mill. (Leguminosae: Caesalpinioideae) in a fragment of the Ecological Station Raso da Catarina, Bahia, Brazil/O genero Senna Mill....
Next Article:Biological parameters of three Trichogramma pretiosum strains (Riley, 1879) (Hymenoptera: Trichogrammatidae) on eggs Helicoverpa armigera (Hubner,...

Terms of use | Privacy policy | Copyright © 2021 Farlex, Inc. | Feedback | For webmasters |