Figures
Abstract
This study evaluated feeding patterns and ontogenetic variations in a non-native fish species (Plagioscion squamosissimus) in an isolated lake in the Upper Paraná River floodplain. Quarterly samplings were performed from April 2005 to February 2006 using plankton nets to capture larvae, seining nets for juveniles, and gill nets and trammel for adults. Stomach contents (n = 378) were examined according to the volumetric method in which the volume of each food item was estimated using graduated test tubes or a glass counting plate. During early development (larval stage), P. squamosissimus consumed mainly Cladocera and Copepoda. Juveniles showed a more diverse diet, including shrimp (Macrobrachium amazonicum), fish, aquatic insects (Trichoptera, Ephemeroptera, Chironomidae and pupae of Diptera) and plants. It was notable the high proportion of cannibalism (23.3%) in this stage. Adults consumed predominantly shrimp and fish. The use of food resources varied significantly between development stages (ANOSIM; r = 0.458; p<0.005), showing changes in food preferences during ontogeny. The Similarity Percentage Analysis (SIMPER) indicated that Cladocera and Copepoda were responsible for the differences observed between the larval stages of pre-flexion, flexion and post-flexion. M. amazonicum and Chironomidae were responsible for the differences between juvenile and larval stages, while M. amazonicum and other fishes caused the differences between adults and other ontogenetic stages. These results are confirmed by the relationship between standard length and developmental periods (ANCOVA; r2 = 0.94; p<0.0001). In general, there were low values of trophic niche breadth. The essentially carnivorous habit from the early stages of P. squamosissimus and the predominant use of M. amazonicum by adults have important roles in feeding patterns of the species, suggesting a major contribution to its success and establishment, especially in lentic environments.
Citation: Neves MP, Delariva RL, Guimarães ATB, Sanches PV (2015) Carnivory during Ontogeny of the Plagioscion squamosissimus: A Successful Non-Native Fish in a Lentic Environment of the Upper Paraná River Basin. PLoS ONE 10(11): e0141651. https://doi.org/10.1371/journal.pone.0141651
Editor: Robert Britton, Bournemouth University, UNITED KINGDOM
Received: June 23, 2015; Accepted: October 12, 2015; Published: November 2, 2015
Copyright: © 2015 Neves et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited
Data Availability: All relevant data are within the paper and its Supporting Information files.
Funding: The authors have no support or funding to report.
Competing interests: The authors have declared that no competing interests exist.
Introduction
Plagioscion squamosissimus, Heckel, 1840, (Sciaenidae, Perciformes), commonly known as curvina, is considered carnivorous in its natural habitat in the Amazon basin. Initially, this species was introduced into northeastern Brazil, and was subsequently released by the Energy Company of São Paulo (CESP) in 1967 in the Pardo River where it spread throughout the Paraná River basin [1, 2, 3]. In all environments, it has become successful, being among the dominant species in various reservoirs, where, in some, it is also one of the main species for commercial fishing [4, 5, 6, 7].
The significance of this species in the Upper Paraná River, given by its high abundance in regions of the Itaipu Reservoir [8, 9] and in several environments of the floodplain upstream, including environmental protection areas like the Parque Nacional de Ilha Grande [10, 11] and the Parque Estadual das Várzeas do Rio Ivinhema [12], places this species in a prominent position, especially because of its economic importance and ecological interactions. In this context, it becomes essential to address its biological characteristics, especially its feeding habits in all stages of the life cycle.
The initial ontogeny of fish can be considered a series of vulnerable periods; the most important is the transition between endogenous and exogenous feeding, which is a period where the survival of the young depends on the quantity and availability of adequate food at the first feeding. Therefore, the success or failure of a population is largely determined during the early life history [13]. Therefore, information on the diet of a species in the larval period, as well as adults, enables the elucidation of its ecological relationships with other species. In addition, assessing the trophic position along the ontogenetic development of non-native species allows researchers to find evidence relative to their success and establishment in environments, as well as the impact of their presence on other species. Moreover, studies on the biology of non-native species in protected areas became relevant, mainly when considering biological invasions with consequent fauna homogenization as one of the main threats and causes of biodiversity loss [14, 15].
The majority of studies on P.squamossimus have reported the trophic ecology of adults in reservoirs [7, 16, 17, 18], but information on feeding during initial development is lacking, primarily considering natural environments. Moreover, even more incipient studies have concurrently evaluated the diet of larvae, juveniles and adults in the same space and time. Thus, evaluating the feeding during ontogeny allows researchers to assess the way growth and morphological changes interfere with trophic relationships, and to understand the interactions in a particular community [19, 20, 21, 22].
The selectivity and the ability to effectively capture food are important factors that contribute to the success and establishment of a species [20, 23, 24]. Based on this premise, this study tested the hypothesis that P. squamosissimus consumes different food resources throughout its life cycle according to body size. In this context, we analyzed the diet of this species in an isolated oxbow lake of the Parana River. It is, therefore, essential to understand the ontogeny influences on the success of the species in such a biotope. Specifically, the objectives of this study were: (i) to describe the diet of P. squamosissimusat different stages of its life cycle (larval to adult); (ii) to check for differences in diet according to ontogeny; (iii) to determine the food resources that contributed most to the diet in each stage of the life cycle; (iv) to show the relationship between the length (Ls) at different stages of the life cycle and the consumption of different food resources; and (iv) to evaluate changes in ecological niche breadth according to ontogeny.
Material and Methods
Ethics statement
Fish samples were collected with authorization from Instituto Brasileiro do Meio Ambiente e dos Recursos Naturais Renováveis (IBAMA) (process number 02001004095/04-98, license numbers 120/2004 and 204/2005), under the responsibility of the researcher Rosilene Luciana Delariva. This study was approved by Ethics Committee on Animal Use of the Universidade Paranaense (CEPEEA) (Permit Number: 13/04) and was conducted in accordance with protocols in their ethical and methodological aspects, for the use of fish.
Study area
The Xambrê Lake is located on the left bank of the Paraná River, within the limits of the Parque Nacional de Ilha Grande (Fig 1). The National Park is formed by a fluvial archipelago with hundreds of islands. The alluvial deposits that originated in the floodplain of the Upper Paraná River are related to the first wet event of the Superior Quaternary, while the current lagoons and oxbow lakes in of the National Park area were formed more recently in the second wet event (1500 AP)[25]. The studied environment is an isolated oxbow lake, approximately 5 km long, 1 km wide and about 3 meters deep. It has an extensive floodplain area on its right margin that separates it from the Paraná River. Currently, it is maintained by groundwater and a small stream. Its connection with the Paraná River was sporadic in years with very high floods; the last record was in 1996. However, after the construction of the Porto Primavera Reservoir, there were no such floods to connect the lake with the Paraná River [10, 26]). Its right bank is colonized by shrubby vegetation and aquatic macrophytes, while the left bank is bordered by arboreal vegetation.
Sampling
Fish (larval, juvenile and adult developmental stages) were collected quarterly from April 2005 to February 2006, at two sites in the Xambrê Lake. Samples of the larval stages were taken at night with a plankton net (0.5 mm mesh size). The net was towed on the water surface behind a boat at low speed for 10 min in the subsurface waters (approximately 20 cm deep). Samples were transferred to polyethylene flasks and preserved in 4%formalin buffered with calcium carbonate. Juveniles were collected using the seine operated in the left marginal area of the lake, during dusk (19.00h). Adult specimens were caught using gill nets (mesh sizes of 2.4, 3, 4, 5, 6, 7, 8, 9, 10, 12, 14, and 16 cm between opposite knots) and trammel nets (with inner mesh sizes of 6, 7, and 8 cm between opposite knots), both 20 m long. The effort was the same at each site. Nets remained set for 24 h and were checked every 8 h (morning, afternoon, and night).
Laboratory procedures
Identification of fish larvae was performed according identification keys [27], and individuals were characterized according to the degree of flexion of the terminal region of the notochord and development of the fins and separated into stages of pre-flexion, flexion, and post-flexion [27, 28].We measured the standard length (SL) of fish larvae specimens with an ocular micrometer under a stereomicroscope. Adult and juvenile specimens were identified [29], weighed on analytical balance, measured (standard and total length, in cm), and then eviscerated. Voucher specimens were deposited in the fish collection of Gerpel (Grupo de Pesquisas em Recursos Pesqueiros e Limnologia), Universidade Estadual do Oeste do Paraná, Brazil (lot Cig 2380).
Diet composition analysis
To characterize the diet of larval stages, the digestive tube was removed through a longitudinal cut in the abdomen using a probe or scalpel, when necessary. Digestive tubes were then opened on blade and covered with coverslip. Posteriorly, fields were randomly chosen, and the items were identified, counted, summed and multiplied by an approximate value of a known volume, obtaining the total volume of items in each digestive tube analyzed. For individuals at pre-flexion and flexion stages all the digestive tube content was analyzed. Larvae at the post-flexion stage that already showed a clear differentiation of the digestive tube, had only the stomach content and 2/3 of the intestine analyzed, due to a high degree of digestion in the final portion.
The diet analysis for juvenile and adult stages was based on the stomach contents of 32 adults and 127 juveniles relating to all stomachs containing food (fullness equal to or greater than 50%). Food items were identified under optical and stereoscopic microscopes to the lowest taxonomic level possible, using the identification keys for algae [30] and invertebrates [31]. In order to quantify the food items, we used the volumetric method; i.e., the total volume of a food item taken by the fish population is given as a percentage of the total volume of all stomach contents [32], using graduated test tubes and a glass counting plate [33].
Data analysis
Aiming to evaluate the sampling sufficiency of stomach/intestine contents of P. squamosissimus, rarefaction curves were constructed for different ontogenetic periods. In this analysis, each point of the curve was the result of a mean value obtained by randomization in the order of the samples, with a standard deviation assigned for each value.
To test the null hypothesis of no difference in diet composition between different developmental stages of P.squamosissimus summarized by the nMDS (distance matrix), we used an ANOSIM (Analysis of Similarities) based on Bray-Curtis distance. These tests are applied in ecology for comparing the taxonomic composition in more groups of samples [34]. If two stages are different in their use of food resources, we expect smaller distances within each group than between groups.
Finally, we used discriminant analysis (SIMPER-similarity percentage) to determine which food resources were responsible for dissimilarity between groups (developmental stages of the fish life cycle) [35]). We used the Bray-Curtis distances to distinguish the diet composition and participation of each food resource between different stages of development. The general dissimilarity was calculated using all resources, where as the dissimilarity resource-stage was calculated for separated resources.
Food resources and standard length were compared between developmental stages by an Analysis of Covariance, using the volume of food resources as covariate (ANCOVA, p<0.05), to reduce the bias of each developmental stage [36].
In order to demonstrate the relative degree of specialization in the diet of the developmental stages, the trophic niche breadth (dietary breadth) was estimated based on the volume of food items, using the standardized Levins’ Index [37], which ranges from 0, when a species consumed only one type of food, to 1, when a species consumed similarly all the food items. This is given by the formula:
where: Bi = standardized trophic niche breadth; Pij = proportion of food item j in the diet of species i; n = total number of food items.
The rarefaction curves, ANOSIM and SIMPER were run using the software PAST 1.68 [38]. ANCOVA was performed using the software Statistica 7.0 [39].
Results
Diet composition
The rarefaction curve was asymptotic to each ontogenetic stage sampled, suggesting that the number of individuals analyzed was sufficient to represent the diet of each stage (Fig 2).
The diet of the larval stage was mainly composed of Copepoda (Cyclopoida and Calanoida) and Cladocera; in the pre-flexion stage, the diet also included algae (diatoms) and in the flexion and post-flexion stages, Gastropoda and Chironomidae were also consumed. Juveniles had a more diverse diet, consuming shrimp (Macrobrachium amazonicum), fish, aquatic insects (Trichoptera, Ephemeroptera, Chironomidae and pupae of Diptera) and plants. There was considerable cannibalism in the juvenile stage (23.3% consumption of P. squamosissimus juveniles). Adults predominantly consumed shrimp and fish (Table 1 and S1 Table).
Ontogenetic variations in the diet
The food resources varied significantly between developmental stages (ANOSIM; Bray-Curtis; 9999 permutations; r = 0.458; p = 0.0001). In fact, all distance measures based on the volume of food resources indicated significant differences (p<0.05), suggesting that the food preference changes during ontogeny of the species.
The Similarity Percentage (SIMPER) analysis indicated that Cladocera and Copepoda were responsible for the observed differences between the larval stages of pre-flexion vs. flexion vs. post-flexion. M. amazonicum and Chironomidae accounted for the differences between juveniles and larval stages (pre-flexion, flexion and post-flexion). M. amazonicum and other fishes were responsible for the differences between adult and other stages of the life cycle (Table 2).
Values of standard length were significantly different between developmental stages (ANCOVA; r2 = 0.94; p<0.0001) (Table 3 and Fig 3). Copepoda was a specially adjusted food item to individuals with smaller size (larval stages), while M. amazonicum, plant remains, Ephemeroptera, Trichoptera and other fishes, including P. squamosissimus, were adjusted to juveniles and adults.
Trophic specialization
In general, there were low values of trophic niche breadth, and the early stages (larval stages) showed the lowest values. As the individuals grew, the trophic niche breadth gradually increased with the participation of new food items (Fig 4).
Discussion
The high consumption of prey was found in all developmental stages. The items recorded in stomach contents were substantially comprised of different taxonomic groups of animals present in the layers of the water column. This result indicates that this species can be considered a generalist carnivorous feeder. In addition, our finding clearly shows that the diet of P. squamosissimus includes an ontogenetic shift in the selectivity and acquisition of food items, increasing proportions of larger and more evasive prey as fish grow. This widespread observation seems to be a common trend in fish [22, 23], and reinforces the importance of this type of study for understanding not only the trophic requirements in the early stages (most critical),but also factors influencing population sizes of adult fish.
In the early developmental stage (larvae), the species consumed mainly Cladocera and Copepoda at different proportions. These microcrustaceans are large and agile prey, whose capture can be associated with mouth opening size, visual acuity and swimming ability [20, 40]. However, our results showed no difference in diet between larval developmental stages, indicating that, even in the early stages, regardless of reduced swimming ability and visual acuity (especially at pre-flexion) [20], larvae were able to capture these prey. Further, the presence of benthic organisms, such as gastropods, insect larvae and aquatic insects in the stomachs of larvae at flexion and post-flexion stages, as well as of juveniles, indicates that they already have the swimming ability to explore the sediment in search of food. Typically, the most developed stages (especially juveniles) already have well-developed fins, which promote a more effective displacement. After reaching a certain degree of development, larvae migrate to more structured regions such as marginal areas. This migration pattern, known as ontogenetic migration or lateral migration, is described for several fish species [41]). In this type of migration, at least one stage of the life cycle takes place in a different environment from the other. In this way, despite the low swimming ability of the earliest larval stages when compared to adults, the lateral migration during this period would have remarkable trophic consequences. The carnivorous habit, beginning at this stage of the life cycle, is favored in marginal areas that present both shelter and abundant food [20, 21].
The transition between endogenous and exogenous feeding is crucial for the survival of larvae [13, 19], in which there are many morphological changes in the mouth and digestive tract [42, 43]. The carnivorous habit displayed from the earliest developmental stages gives several advantages to the species. This is critical, especially in the larval stage, which is considered the period of the highest vulnerability and mortality [44, 45]. The consumption of energetically advantageous prey allows the larvae to overcome this critical period and reach the juvenile stage successfully [40].
The broader food spectrum of juveniles may be related to greater swimming performance and increased complexity of the buccal apparatus which favors the capture and ingestion of energy-efficient prey, resulting in rapid growth and survival. Besides, P. squamosissimus has a defined stomach with pyloric caeca in the initial stages [19], which provides the species with the advantage of digesting larger prey. Thus, behavioral and structural adaptations, such as food preference and a complex mouth, are advantageous for capturing mobile organisms, a typical tactic of carnivores [46].
In this study, the high occurrence of cannibalism in the P. squamosissimus diet is noteworthy. Most studies on the diet of this species did not detect cannibalism, e.g. [3, 7, 16, 21, 47, 48], suggesting that it is not a common feeding strategy. Although cannibalistic behavior has been reported in the literature associated with a wide variety of taxa, habitats and life history strategies, it is particularly well represented in piscivorous [49, 50], where larger individuals predate upon small ones. Thus, the predation by older and unrelated conspecifics accounts for the majority of cases of cannibalism in fish [51, 52]. Herein, however, the ingestion of individuals of their own species was exclusive of juveniles, which may be related to some behaviors commonly displayed by predators: i) taking advantage of the high abundance of juveniles. Even though we do not have data about the availability of prey in the environment, this factor is relevant when analyzing the composition and relative abundance of the fish fauna in marginal areas of the studied lake, where it was observed that P. squamosissimus was the most abundant species, being essentially represented by immature individuals [26]. In addition, the period of highest cannibalism (stomach contents in late January and March) coincided with the sudden increase in the availability of juveniles, a fact supported by the occurrence of spawning and high densities of larvae of this species in the Upper Paraná River floodplain, especially during the high water-level season associated with high temperatures [10, 53, 54,55]; ii)the intake of prey being advantageous for growth and development, thus maintaining the energy within the population. In this aspect, conspecifics represent a diet of high nutritional quality, with minerals and amino acids in the optimal proportion for maximal growth [51, 56]. As a result, more importantly, cannibalism at an early age accumulates energy for growth, so the species can escape the predation window of other predators; iii) the regulation of population abundance, which allows the species to minimize the intraspecific competition in the adult stage. The regulatory role of cannibalism in experimental populations has been clearly demonstrated [57], but the situation in wild populations is still largely controversial [49, 51]. In this sense, although it is hard to observe the latter two behaviors in natural populations, in the case studied here, none of them can be discarded. Additionally, the typed isolated oxbow lake can also be another factor that induces the cannibalisminfluenced by the higher population density of juveniles because of the lack of chances for dispersal. Furthermore, possibly all the factors above must act concurrently.
For the diet of both juveniles as adults, M. amazonicum was an important resource, as verified in other studies [7, 16, 21, 47, 48]. This food preference is supported by the high participation of shrimp in the diet of this species in its original environment (Amazon basin) [58]. In addition to the preference, this important contribution may be related to the high abundance of this resource in the studied lake [10, 59]. Along with these factors, the body morphology of curvina, likewise, can assist and facilitate the capture of this prey [21, 60]. The presence of an extensible terminal mouth allows for capture in structured places, especially in shallow environments colonized by aquatic macrophytes, as observed in the sampling sites and reported in another study in the Upper Paraná River floodplain, upstream of the current study area [47].
In the adult stage, although shrimp consumption remained above 50%, the consumption of fish increased. This can be explained by the optimal foraging theory, which predicts that the predator tends to preferentially consume types or sizes of prey that are energetically more favorable as to maximize its fitness [23, 61]. In general, predators select small prey when they are at greater abundance and availability. To compensate for the energy cost, the number of small prey should be substantially greater than the number of larger prey [21].
Accordingly, the characterization of feeding habits during the ontogeny of P. squamosissimus provides information that associates the food items with the stages of the life cycle, showing food preferences throughout the ontogenetic development. The diet included both increased prey size and changes in types of prey related to growth and development, consistently demonstrated by the model (ANCOVA). The obtained results clearly show the direct relationships between developmental stages and the type of items consumed. It was possible to verify food preferences associated with body characteristics at each stage of the ontogenetic development.
The carnivorous behavior from the early stages is supported by low values of trophic niche breadth. Meanwhile, along the ontogenetic development, food items are replaced and added, with greater variation in juveniles because of the greater richness of the items consumed. The feeding diversity in juvenile fish is commonly higher than during the larval period, and there is often an increased importance of species-specific dietary traits. At this stage, the acquisition of energy for growth and survival is extremely important. However, some limitations on morphological traits, such as mouth size and habitat where juveniles occur (marginal areas), lead to the ingestion of several smaller items, like shrimp and aquatic insects. Furthermore, adults are more selective in capturing prey, restricting their diets to foods with a favorable energy balance, since their morphological characteristics reflected in swimming ability and body size enable the capture of larger, more agile prey, such as fish.
In conclusion, this study provided novel insights into the feeding ecology of curvina. The results support the initial hypothesis that P. squamosissimus consumes different food resources according to body size, directly related to the degree of development, but exhibiting carnivorous habits from the early stages. Moreover, the predominant consumption of M. amazonicum, by juveniles and adults, as well as the morphological and behavioral characteristics associated with the use of energetically favorable food items (including significant cannibalism among juveniles), should play a key role in the colonization of this species, especially in lentic environments. The successful colonization of non-native species is expected, as is the case with curvina, mainly in situations where the absence of predators, the abundance of preferential food resources and the morphological traits provide a competitive advantage in the early stages. These factors, although some indirectly inferred, cannot be discarded, as they show the success and establishment of this species in new environments.
Supporting Information
S1 Table. Food items consumed (percentage volume)by P. squamosissimus developmental stages in Xambrê Lake, Upper Paraná River floodplain,Paraná State,Brazil.
SL = standard Length;N = stomachs analyzed; Food items: Bacil = Bacillariophyta; Plant = Plant remains; Gastr = Gastropoda; Copep = Copepoda; Clado = Cladocera; Macro = Macrobrachium amazonicum; Chiron = Chironomidae; Ephem = Ephemeroptera; Trich = Trichoptera; Oaqin = Other aquatic insects; Psqua = Plagioscion squamosissimus; Ofish = Other fishes.
https://doi.org/10.1371/journal.pone.0141651.s001
(DOCX)
Acknowledgments
We thank CORIPA (Consórcio Intermunicipal para Conservação do Remanescente do rio Paraná e Áreas de Influência) for providing logistical support for sampling. We also thank all our colleagues for helping in field work.
Author Contributions
Conceived and designed the experiments: RLD PVS. Performed the experiments: MPN. Analyzed the data: ATBG. Contributed reagents/materials/analysis tools: RLD PVS. Wrote the paper: MPN RLD.
References
- 1.
Cruz JA, Moreira JA, Verani JR, Girardi L, Torloni CEC. Levantamento da ictiofauna e aspectos da dinâmica de populações de algumas espécies do reservatório de Promissão-SP (1ª. Etapa). São Paulo: CESP; 1990.
- 2.
Torloni CEC, Côrrea ARA, Carvalho AAC Jr, Santos U, Gonçalves JL, Gereto EJ, et al. Produção pesqueira e composição das capturas em reservatórios sob concessão da CESP nos rios Tietê, Paraná e Grande, no período de 1986 a 1991. São Paulo: CESP; 1994.
- 3. Bennemann ST, Capra LG, Galves W, Shibatta OA. Dinâmica trófica de Plagioscion squamosissimus (Perciformes, Sciaenidae) em trechos de influência da represa Capivara (rios Paranapanema e Tibagi). Iheringia Ser. Zool. 2006; 96: 115–119.
- 4. Hahn NS, Loureiro VE, Delariva RL. Atividade alimentar da curvina Plagioscion squamosissimus (Heckel,1840) (Perciformes, Sciaenidae) no rio Paraná. Acta Scien. 1999; 21:309–314.
- 5. Félix RTS, Severi W, Santos AJG, El-Deir ACA, Soares MG, Evêncio Neto J. Desenvolvimento ovariano de Plagioscion squamosissimus (Heckel, 1840) (Actionopterygii, Perciformes), no reservatório de Pedra, Rio de Contas, Bahia. Biota Neotrop. 2009; 9: 131–136.
- 6. Santos NCL, Medeiros TN, Rocha AAF, Dias RM, Severi W. Uso de recursos alimentares por Plagioscion squamosissimus–piscívoro não-nativo no reservatório de Sobradinho-BA, Brasil. Bol. Inst. Pesca. 2014; 40: 397–408.
- 7. Ferreira-Filho VP, Guerra TP, Lima MCS, Teixeira DFF, Costa RR, Araújo IMS, et al. Padrões ecomorfológicos associados à dieta de Plagioscion squamosissimus (Perciformes, Scianidae) em reservatório permanente, no Nordeste do Brasil. Iheringia Sér. Zool. 2014; 104:134–142.
- 8. Freire AG, Agostinho AA. Ecomorfologia de oito espécies dominantes da ictiofauna do reservatório de Itaipu (Paraná, Brasil). Acta Limnol. Bras. 2001; 13: 1–9.
- 9. Langeani F, Castro RMC, Oyakawa OT, Shibatta OA, Pavanelli CS, Casatti L. Diversidade da ictiofauna do Alto Rio Paraná: composição atual e perspectivas futuras. Biota Neotrop. 2007;7: 1–17.
- 10. Daga VS, Gogola TM, Sanches PV, Baumgartner G, Baumgartner D, Piana PA. Fish larvae assemblages in two floodplain lakes with different degrees of connection to the Paraná River, Brazil. Neotrop Ichthyol. 2009; 7: 429–438.
- 11. Baumgartner G, Gubiani EA, Delariva RL, Sanches PV. Spatial Patterns in Fish Assemblages of Ilha Grande National Park, Brazil. Wetlands. 2010; 30: 309–320.
- 12. Reynalte-Tataje DA, Nakatani K, Fernandes R, Agostinho AA, Bialezki A. Temporal distribution of ichthyoplankton in the Ivinhema river (Mato Grosso do Sul State/Brazil: Influence of environmental variables. Neotrop Ichthyol. 2011; 9: 427–436.
- 13.
Kamler E. Early Life History of Fish. London: Chapman and Hall; 1992.
- 14. Daga VS, Skóra F, Padial AA, Abilhoa V, Gubiani EA, Vitule JRS. Homogenization dynamics of the fish assemblages in Neotropical reservoirs: comparing the roles of introduced species and their vectors. Hydrobiologia. 2015; 746: 327–347.
- 15. Thomaz SM, Kovalenko KE, Havel JE, Kats LB. Aquatic invasive species: general trends in the literature and introduction to the special issue. Hydrobiologia. 2015; 746: 1–12.
- 16. Teixeira I, Bennemann ST. Ecomorfologia refletindo a dieta dos peixes em um reservatório no sul do Brasil. Biota Neotrop. 2007; 7: 68–76.
- 17. Hahn NS, Fugi R. Alimentação de peixes em reservatórios brasileiros: alterações e consequências nos estágios iniciais do represamento.Oecol. Bras. 2007; 11: 469–480.
- 18. Pereira LS, Agostinho AA, Gomes LC. Eating the competitor: a mechanism of invasion. Hydrobiologia. 2015; 746: 223–231.
- 19. Makrakis MC, Nakatani K, Bialetzki A, Sanches PV, Baumgartner G, Gomes LC. Ontogenetic shifts in digestive tract morphology and diet of fish larvae of the Itaipu Reservoir, Brazil. Environ. Biol. Fishes. 2005; 72: 99–107.
- 20. Makrakis MC, Nakatani K, Bialetzki A, Gomes LC, Sanches PV, Baumgartner G. Relationship between gape size and feeding selectivity of fish larvae from a Neotropical reservoir. J. Fish Biol. 2008; 72: 1690–1707.
- 21. Bozza AN, Hahn NS. Uso dos recursos alimentares por peixes imaturos e adultos de espécies piscívoras em uma planície de inundação neotropical. Biota Neotrop. 2010; 10: 217–226.
- 22. Yaniv S, Elad D, Holzman R. Suction feeding across fish life stage: flow dynamics from larvae to adults and implications for prey capture. J Exp Biol. 2014; 217: 3748–3757. pmid:25189373
- 23.
Gerking SD. Feeding Ecology of Fish. San Diego: Academic Press Inc.; 1994.
- 24. Pepin P, Robert D, Bouchard C, Dower JF, Falardeau M, Fortier L, Jenkins GP, Leclerc V, Levesque K, Llopiz JK, Meekan MG, Murphy HM, Ringuette M, Sirois P, Sponaugle S. Once upon a larva: revisiting the relationship between feeding success and growth in fish larvae. ICES J Mar Sci. 2015; 72: 359–373.
- 25.
Campos JB. Caracterização física e ambiental da área do Parque Nacional de Ilha Grande. In: Campos JB (Org.). Parque Nacional de Ilha Grande reconquista e desafios. Maringá: IAP/Coripa; 2001.
- 26. Delariva RL, Canteri FC, Sanches PV, Baumgartner G.Composição e estrutura da ictiofauna de área marginal da lagoa Xambrê, Parque Nacional de Ilha Grande, PR, Brasil. Rama. 2009; 2: 141–153.
- 27.
Nakatani K, Agostinho AA, Baumgartner G, Bialetzki A, Sanches PV, Makrakis MC, et al. Ovos e larvar de peixes de água doce: desenvolvimento e manual de identificação. Maringá: EDUEM; 2001.
- 28. Ahlstrom EH, Ball OP. Description of eggs and larvae of jack mackerel (Trachurus symmetricus) and distribution and abundance of larvae in 1950 and 1951. Fishery Bulletin. 1954; 56: 209–245.
- 29.
Graça WJ, Pavanelli CS. Peixes da planície de inundação do Alto rio Paraná e áreas adjacentes. Maringá: EDUEM; 2007.
- 30.
Bicudo CEM, Bicudo RMT. Algas de águas continentais brasileiras chave ilustrada para identificação de gêneros. São Paulo: Fundação Brasileira para Desenvolvimento do Ensino de Ciências; 1970.
- 31.
Mugnai R, Nessimian JL, Baptista DF. Manual de identificação de macroinvertebrados aquáticos do Estado do Rio de Janeiro. Rio de Janeiro: Technical Boocks; 2010.
- 32. Hyslop EJ. Stomach content analysis: a review of methods and their application. J. Fish Biol. 1980; 17: 411–429.
- 33. Hellawell JM, Abel R. A rapid volumetric method for the analysis of the food of fishes. J. Fish Biol. 1971; 3: 29–37.
- 34.
Hammer Ø, Harper DAT. Paleontological Data Analysis. Blackwell; 2006.
- 35. Clarke KR. Non-parametric multivariate analysis of changes in community structure. Aust. J. Ecol. 1993;18:117–143.
- 36.
Zar JH. Biostatistical Analysis – 5ª edition. New Jersey: Prentice Hall International; 1999.
- 37. Hurlbert SH. The measurement of niche overlap and some relatives. Ecology. 1978; 59: 67–77.
- 38. Hammer DA, Harper T, Ryan PD. PAST: Paleontological Statistics Software package for education and data analysis. Paleontologia Electronica. 2001; 4: 1–9.
- 39.
Statsoft Inc. Statistica (data analysis software system), version 7.0. Tulsa. 2004. Available at: http://www.statsoft.com.
- 40. Nunn AD, Tewson LH, Cowx IG. The foraging ecology of larval and juvenile fishes. Rev Fish Biol Fish. 2012; 22: 377–408.
- 41. Garutti V, Figueiredo-Garutti ML. Lateral migration of Liposarcus anisitsi (Siluriformes,Loricariidae) in the Preto River,Alto Parana Basin, Brazil.Iheringia Ser. Zool. 2000; 88: 25–32.
- 42. Lima AF, Makrakis MC, Gimenes MF, Makrakis S, Silva PS, Assumpção L. Mudanças morfológicas no trato digestório e composição da dieta de larvas e juvenis do linguado Catathyridium jenynsii no reservatório de Itaipu, rio Paraná, Brasil. Iheringia Ser. Zool. 2013; 103: 214–221.
- 43. Dabrowski K. The feeding of fish larvae: present << state of the art>> and perspectives (*). Reprod Nutr Dévelop.1984; 24: 807–833.
- 44. Wittenrich ML, Rhody NR, Turingan RG, Main KL. Coupling osteological development of the feeding apparatus with feeding performance in common snook, Centropomus undecimalis, larvae: Identifying morphological constraints to feeding. Aquaculture. 2009; 294: 221–227.
- 45. Rønnestad I, Yúfera M, Ueberschar B, Ribeiro L, Saele Ø, Boglione C. Feeding behaviour and digestive physiology in larval fish: current knowledge, and gaps and bottlenecks in research. Reviews in Aquaculture. 2013; 5: 59–98.
- 46. Uieda VS, Pinto TLF. Feeding selectivity of ichthyofauna in a tropical stream: space-time variations in trophic plasticity. Community Ecol. 2011; 12: 31–39.
- 47. Almeida VLL, Hahn NS, Vazzoler AEAM. Feeding patterns in five predatory fishes of the high Paraná River floodplain (PR, Brazil).Ecol Freshw Fish. 1997; 6: 123–133.
- 48. Costa SAGL, Peretti D, Pinto JEM Jr., Fernandes MA,Gurgel AM Jr.. Espectro alimentar e variação sazona da dieta de Plagioscion squamosissimus (Heckel, 1840) (Osteichthyes, Scianidae) na lagoa do Piató, Assu, Estado do Rio Grande do Norte, Brasil. Acta Scient. Biol. Scien. 2009; 31: 285–292.
- 49. Fox LR. Cannibalism in Natural Populations. Annu Rev Ecol Syst. 1975; 6: 87–106.
- 50.
Wooton RJ. Ecology of teleost fishes. London: Chapman & Hall; 1990.
- 51. Smith C, Reay P. Cannibalism in teleost fish. Rev. Fish Biol. Fish. 1991; 1: 41–64.
- 52. Baras E, Dugué R, Legendre M. Do cannibalistic fish forage optimally? An experimental study of prey size preference, bioenergetics of cannibalism and their ontogenetic variations in the African catfish Heterobranchus longifilis. Aquat. Living Resour. 2014; 27: 51–62.
- 53. Baumgartner MST, Nakatani K, Baumgartner G, Makrakis MC. Spatial and temporal distribution of “Curvina” larvae (Plagioscion squamosissimus HECKEL, 1840)and relationship to some environmental variables in the upper Paraná River floodplain, Brazil. Braz J Biol. 2003; 63: 381–391. pmid:14758697
- 54. Bialetzki A, Nakatani K, Sanches PV, Baumgartner G. Eggs and larvae of the “curvina” Plagioscion squamosissimus (Heckel, 1840) (Osteichthyes, Scinidae) in the Baía River, Mato Grosso do Sul State, Brazil. J Plankton Res. 2004; 26: 1327–1336.
- 55. Gogola TM, Gonzáles LMA, Daga VS, Silva PRL, Sanches PV, Gubiani EA, Delariva RL. Spatial and temporal distribution patterns of ichthyoplankton in a region affected by water regulation by dams. Neotrop Ichthyol. 2010; 8: 341–349.
- 56. Gallagher CP, Dick TA. Winter feeding ecology and the importance of cannibalism in juvenile and adult burbot (Lota lota) from the Mackenzie Delta, Canada. Hydrobiologia. 2015; 1–16.
- 57. Fessehaye Y, Kabir A, Bovenhuis H, Komen H. Prediction of cannibalism in juvenile Oreochromis niloticus based on predator to prey weight ratio, and effects of age and stocking density. Aquaculture. 2006; 255: 314–322.
- 58. Goulding M, Ferreira E. Shrimp-eating fishes and a case of prey switching in Amazon rivers. Rev. Bras. de Zool. 1984;2: 85–97.
- 59. Bialetzki A, Nakatani K, Baumgartner G, Bond-Buckup G. Occurrence of Macrobrachium amazonicum (heller) (Decapoda, Palaemonidae) ln Leopoldo's inlet (Ressaco do Leopoldo), Upper Paraná River, Porto Rico, Paraná, Brazil. Rev. Bras. Zool. 1997; 14: 379–390.
- 60. Bialetki A, Nakatani K, Sanches PV, Baumgartner G. Spatial and temporal distribution of larvae and juvenile of Hoplias aff malabaricus (Characiformes, Erytrinidae) on the floodplain of the Upper Paraná River, Brazil. Braz J Biol. 2002; 62: 211–222. pmid:12489393
- 61. Pyke GH.Optimal foraging theory a critical review.Annu Rev Ecol Syst. 1984;15:523–575.