SciELO - Scientific Electronic Library Online

vol.71 issue2Biochemical and microbiological tools for the evaluation of environmental quality of a coastal lagoon system in Southern BrazilLife cycle of Cyclestheria hislopi (Baird, 1859) (Crustacea, Branchiopoda) author indexsubject indexarticles search
Home Pagealphabetic serial listing  

Brazilian Journal of Biology

Print version ISSN 1519-6984

Braz. J. Biol. vol.71 no.2 São Carlos May 2011 



Trophic ecomorphology of Siluriformes (Pisces, Osteichthyes) from a tropical stream


Ecomorfologia trófica de Siluriformes (Pisces, Osteichthyes) de um riacho tropical



Pagotto, JPA.I,*; Goulart, E.I; Oliveira, EF.I,II;Yamamura, CB.I

IPrograma de Pós-graduação em Ecologia de Ambientes Aquáticos Continentais – PEA, Departamento de Biologia, Nupélia, Universidade Estadual de Maringá – UEM, Av. Colombo, 5790, Jd. Universitário, Bloco G-90, CEP 87020-900, Maringá, PR, Brazil
IIUniversidade Tecnológica Federal do Paraná – UTFPR, Campus Londrina, Av. dos Pioneiros, 3131, CEP 86036-370, Londrina, PR, Brazil




The present study analysed the relationship between morphology and trophic structure of Siluriformes (Pisces, Osteichthyes) from the Caracu Stream (22º 45' S and 53º 15' W), a tributary of the Paraná River (Brazil). Sampling was carried out at three sites using electrofishing, and two species of Loricariidae and four of Heptapteridae were obtained. A cluster analysis revealed the presence of three trophic guilds (detritivores, insectivores and omnivores). Principal components analysis demonstrated the segregation of two ecomorphotypes: at one extreme there were the detritivores (Loricariidae) with morphological structures that are fundamental in allowing them to fix themselves to substrates characterised by rushing torrents, thus permitting them to graze on the detritus and organic materials encrusted on the substrate; at the other extreme of the gradient there were the insectivores and omnivores (Heptapteridae), with morphological characteristics that promote superior performance in the exploitation of structurally complex habitats with low current velocity, colonised by insects and plants. Canonical discriminant analysis revealed an ecomorphological divergence between insectivores, which have morphological structures that permit them to capture prey in small spaces among rocks, and omnivores, which have a more compressed body and tend to explore food items deposited in marginal backwater zones. Mantel tests showed that trophic structure was significantly related to the body shape of a species, independently of the phylogenetic history, indicating that, in this case, there was an ecomorphotype for each trophic guild. Therefore, the present study demonstrated that the Siluriformes of the Caracu Stream were ecomorphologically structured and that morphology can be applied as an additional tool in predicting the trophic structure of this group.

Keywords: Loricariidae, Heptapteridae, trophic guilds, Paraná River.


O presente estudo investigou as relações entre morfologia e a estrutura trófica das espécies de Siluriformes (Pisces, Osteichthyes) do riacho Caracu (22º 45' S e 53º 15' W), afluente do rio Paraná. Foram amostrados três pontos com pesca elétrica, sendo registradas duas espécies de Loricariidae e quatro de Heptapteridae. A análise de agrupamento revelou a presença de três guildas tróficas: detritívoros, insetívoros e omnívoros. A Análise de Componentes Principais evidenciou a tendência de segregação entre dois ecomorfotipos: em um extremo do gradiente ecomorfológico estiveram dispostos detritívoros (Loricariidae), com estruturas morfológicas importantes para sustentação em substratos de corredeiras, as quais permitem a pastagem sobre detritos e materiais orgânicos incrustados no substrato. No outro extremo estiveram insetívoros e omnívoros (Heptapteridae), com estruturas morfológicas que tendem a melhorar o desempenho na exploração de recursos em hábitats estruturalmente complexos e com baixa velocidade de corrente, comumente colonizados por insetos e plantas. A Análise Discriminante Canônica revelou um caso de divergência ecomorfológica entre insetívoros e omnívoros, sendo os primeiros, detentores de estruturas morfológicas que favorecem a captura de presas que ocupam pequenos espaços entre rochas e, o segundo grupo, caracterizado por possuir corpos mais comprimidos, tendendo a explorar itens alimentares em zonas marginais de remanso. Os resultados dos testes de Mantel revelaram que a estrutura trófica apresentou relações significativas com a forma do corpo, independentemente das relações filogenéticas. Portanto, o presente estudo demonstrou que, entre os Siluriformes do riacho Caracu, existe uma estrutura ecomorfológica, o que evidenciou que a morfologia pode ser utilizada como mais uma importante ferramenta na tentativa de predizer a estrutura trófica desse grupo.

Palavras-chave: Loricariidae, Heptapteridae, guildas tróficas, rio Paraná.



1. Introduction

The study of ecomorphology involves an analysis of the relationship between body shape and environmental factors to reveal the ecological and evolutionary implications in individuals, populations, guilds and assemblages (Motta et al., 1995; Peres-Neto, 1999). At present, ecomorphological studies are based on the concept that adaptative variations in phenotype are able to produce differences in the performance of species, which consequently generate variations in resource use (Wainwright, 1994). As a result, some authors believe that morphology can predict resource use by species (Casatti and Castro, 2006; Pagotto et al., 2009; Oliveira et al., 2010).

In tributaries of the Paraná River (Brazil), Siluriformes (Osteichthyes) are one of the most abundant groups of fishes (Garutti, 1988; Agostinho et al., 1997). Considering that some species tend to exhibit trophic specialisation (Hahn et al., 2004), the ecological structure of this group can be characterised by a set of trophic guilds, with specific morphological patterns. In the present study, we evaluated the relationship of morphology with the trophic structure of Siluriformes in the Caracu Stream, a tributary of the Paraná River. Thus, we analysed the following: 1) interspecific ecomorphological patterns; and 2) relationships between morphological variables and the trophic guilds apart from the influence of phylogeny, i.e., whether trophic guilds can be predicted by body shape.

Our hypothesis was that body shape is intimately related to the exploited resource type, and consequently, morphologically analogous species tend to belong to the same trophic guild. Thus, if strong relationships of morphology with resource utilisation are found, it can be assumed that the Siluriformes of the Caracu Stream are ecomorphologically structured, which will allow ecological predictions to be made based on body shape of these species. However, if these relationships are weak, the assemblage may present an ecomorphological structure defined simply by the phylogenetic relationships among species or represent a random structure.


2. Material and Methods

2.1. Study area

The Caracu Stream (22º 45' S and 53º 15' W) is a 2nd order tributary of the left bank of the upper Paraná River (Brazil) that extends for approximately 5 km (see Figure 1). This region exhibits a warm, wet temperate climate, and the annual mean temperature is 21 °C, with December, January and February being the warmest and wettest months, and June and July the coldest and driest ones (Maack, 1981). In the present study, there were three sampling stations chosen (Sites 1, 2 and 3; see Figure 1). The means of physical and chemical variables for each sampling station are described in Table 1.

Site 1 is located in the upper stretch of the Caracu Stream (see Figure 1). It is probably the site most marked by anthropogenic alterations. The banks have a low density of vegetation, with a predominance of herbaceous species and grasses. Because it is inside an area of bovine rearing, it has an artificial enlargement that is used by animals to drink water. Thus, it can be considered a semi-lentic stretch (see Table 1), with the bottom typically composed of sand and mud. Site 2 is located in the middle stretch of the Caracu Stream (see Figure 1), and its banks are totally covered with grasses. In the past, the surrounding area was used as a pasture, but now it is destined for natural regeneration. Thus, the grasses are spreading homogeneously over the whole area and sometimes invading the water. Differently from Site 1, this station alternates areas of riffles with rocks on the bottom and few pools, which are sandy. Site 3 is the nearest to the mouth (see Figure 1), and it is characterised by the presence of a number of trees on its banks (Cecropia sp. and Inga sp.). Similar to Site 2, this stretch alternates areas of riffles with rocks on the bottom and few pools, which are sandy.

2.2. Sampling

Three samples were collected using electrofishing (2500 W, 500 V and 2A) in December, 2005, March, 2006 and September, 2006, at each sample station. Two electro-shock dip nets were let out longitudinally for 50 m against the stream flow, and block nets (5-mm mesh) were set at upstream and downstream positions. Three successive samples were realized for each station.

The collected fishes were taken to the field station of Núcleo de Pesquisas em Limnologia, Ictiologia e Aqüicultura (Nupélia), near the Caracu Stream (see Figure 1), where they were identified according to Graça (2004) and Graça and Pavanelli (2007), labelled and frozen. Voucher specimens were deposited in the Ichthyologic Collection of Nupélia: Hypostomus ancistroides NUP 332, 40 ex.; Hypostomus cf. strigaticeps NUP 3190, 1 ex.; Cetopsorhamdia iheringi NUP 3232, 1 ex.; Imparfinis schubarti NUP 4159, 1 ex.; Phenacorhamdia tenebrosa NUP 4161, 1 ex.; Rhamdia quelen NUP 1737, 1 ex.

2.3. Linear morphometric measures, areas and indices

Linear morphometric measures and areas, related to the trunk, fins, head, eyes and mouth of the fishes were selected according to Gatz-Jr. (1979), Breda et al. (2005) and Oliveira et al. (2010). In total, there were 23 morphological characters chosen that were related to the swimming behaviour and trophic ecology of species: standard length (SL), maximum body height (MBH), body midline height (BMH), maximum body width (MBW), caudal peduncle length (CPdL), caudal peduncle height (CPdH), caudal peduncle width (CPdW), caudal fin height (CH), anal fin length (AL), pectoral fin length (PtL), pelvic fin length (PvL), head length (HdL), head height (HdH), head width (HdW), eye height (EH), mouth height (MH), mouth width (MW), dorsal fin area (DA), caudal fin area (CA), anal fin area (AA), pectoral fin area (PtA), pelvic fin area (PvA) and eye area (EA).

To avoid variability induced by the substances used for preservation (Peterson and VanderKooy, 1996), all of the morphological measures were taken from specimens recently thawed. Considering the average length of the first maturation (Vazzoler, 1996; Suzuki et al., 2004), only adult fishes were used, because ontogenetic development can cause changes in body shape and feeding habits (Scharf et al., 2000; Novakowski et al., 2004). Linear measures were obtained by a digital pachymeter, with an approximation of 0.01 mm. The areas of eyes and fins were obtained from drawings of their outlines, which were scanned and input to AutoCAD 2004 software for the calculation of the internal area. Twenty-one ecomorphological indices were calculated from the morphological linear measures and areas (see Table 2).

2.4. Stomach contents

Fishes were eviscerated for analysis of their stomach contents, and species without identifiable stomachs had the anterior most portion of their intestines removed for analysis. The food items observed were grouped into six taxonomical and/or ecological categories: detritus/sediments (decomposed organic detritus, periphitic algae and inorganic sediment), terrestrial plants (Monocotyledons, Dicotyledons, fruits and remains of plants), aquatic insects (larvae of Trichoptera, Diptera, Chironomidae, Ephemeroptera and Coleoptera, and pupae of Diptera), terrestrial insects (adults of Chironomidae, Ephemeroptera, Hymenoptera, Homoptera and fragments), benthic invertebrates (adults of Nematomorpha) and fishes.

The procedure adopted to analyse the stomach contents was the volumetric method (Hellawell and Abel, 1971). Through this procedure, the volume of each food item was calculated as a percentage of the total volume of the stomach contents for each analysed species.

2.5. Data analysis

Similarity in species composition of trophic guilds was established by cluster analysis using the Bray Curtis index to obtain the distance matrix, and simple linkage as the method of connection. This procedure was carried out in PC-ORD 4.1 software (McCune and Mefford, 1999).

To evaluate trends in multivariate ecomorphological space and, then, to find patterns of interspecific diversification, there was a principal components analysis (PCA) applied to the correlation matrix (Pearson) formed by 21 ecomorphological indices. The axes were selected using a broken-stick model (Jackson, 1993), and the analysis was performed in PC-ORD 4.1 (McCune and Mefford, 1999).

Canonical discriminant analysis (CDA) was applied to verify the ecomorphological indices that maximised the differences between the trophic guilds using a stepwise-forward method (p < 0.05) (Johnson, 1998). Additionally, the CDA reclassified the groups based on the minimal distance between the observations inside the groups. The percentage of correct reclassification can be an indicative of success in the prediction (Gotelli and Ellison, 2004). This test was performed in Statistica 7.0 software.

A Mantel test was carried out to check whether the species that used the same ecological resource were the most similar morphologically. This method compared the matrix of morphological distance between the species with the models matrices for trophic structure and phylogeny. The null hypothesis was that the morphological patterns of Siluriformes from the Caracu Stream are independents of resource used and of species phylogeny.

The morphological distances were calculated based on the mean Euclidian distance among the ecomorphological indices for each pair of species, according to the expression (Equation 1):

in which: Djk = Euclidian distance, n = number of the ecomorphological indices, and xij e xik = values of ecomorphological index i to j and k species, respectively (Gotelli and Ellison, 2004).

The model matrices were obtained by attributing the value of 1 to the pair of species from the same trophic guild and 0 to the pair of species that did not satisfy these conditions. In building the model matrix of taxonomic distance, the method proposed by Pouilly et al. (2003) was used, which consists of a standardized counting of the number of nodes that separate each species along the taxonomical tree. Value 1 was attributed to species from the same genera, value 2 to different genera, but in the same family, and value 3 to those that were not in the same family.

The relationship between morphology and trophic structures could be an artifact derived from the phylogenetic distance among the species (Douglas and Matthews, 1992). A partial Mantel test was performed to evaluate the effect of phylogeny, which tested the partial correlation between two matrices, controlling the effect of a third. Initially, regressions of morphological distance by taxonomical distances and regressions of model matrices of trophic structure by taxonomical distances were carried out. Then a partial Mantel test correlating the residual matrix from the first regression (morphology x phylogeny) with the residual matrix from the trophic structure x phylogeny regression was performed. Thus, the correlation tests between the morphological distance matrix and trophic structure were performed independent of the effect of phylogeny. Both the Mantel and partial Mantel test were carried out in NTSYS-pc software (Rohlf, 1988) and the statistical significance was estimated using 20,000 permutations.


3. Results

A total of six Siluriformes species, representing two families and five genera, were sampled and analysed (see Table 3).

The diets of H. ancistroides and H. strigaticeps were dominated by organic detritus (periphytic algae and decomposing organic material) and inorganic sediments. Thus, they were classified as detritivores. Cetopsorhamdia iheringi, I. schubarti and P. tenebrosa formed the group of insectivores. All of these species were characterised by insects (terrestrial or aquatic) as their main food item. Rhamdia quelen, which fed on a large diversity of food resources, with a tendency toward the consumption of plants, was classified as an omnivore (see Table 4 and Figure 2).



The PCA showed that only the first axis was significant in explaining the ordination of the data, accounting for 49.6% of the total variability (see Table 5). According to the ordination (see Figure 3), the variation tendency of the data demonstrated clear segregation between the Loricariidae and Heptapteridae. Thus, the Loricariidae, with negative scores, presented individuals with more depressed bodies (low values for the depression index), long caudal peduncles and developed fins (except for the anal). The second family, Heptapteridae, with positive scores, presented individuals with higher and proportionally more compressed bodies, anal fins with large areas and relatively larger mouths (see Figure 3).





The models predicted by the CDA selected the 16 ecomorphological indices that most contributed to the discrimination among members of the trophic guilds (see Table 6). Therefore, the first axis, responsible for explaining 94.7% of the total variance, demonstrated clear segregation of the group of detritivores (Loricariidae) compared to the others (see Figure 4). Canonical axis 2 (5.3% of explained variability) showed the segregation between insectivores and omnivores. The insectivores, with positive scores, presented wider heads, caudal fins with a tendency toward bifurcation and larger anal fins, while the omnivores were more compressed (see Table 6 and Figure 4). The classification matrix predicted by the CDA model indicated that all of the Siluriformes species of the Caracu Stream were correctly classified into their respective trophic guilds.


The Mantel test revealed a significant correlation between morphology and diet (p = 0.02; see Table 7). However, when the matrices of morphological and phylogenetic distances were correlated, the possibility of phylogeny affecting these ecomorphological correlations could not be discarded (p = 0.07; see Table 7). Thus, a partial Mantel test was performed to control the effect of historical factors in the ecomorphological relationships. It revealed that, independent of phylogenetic relationships, the body shapes of the fishes were related to the local trophic structure (p = 0.03; see Table 7).


4. Discussion

In the Caracu Stream, the Siluriformes were grouped in three trophic guilds: detritivores, insectivores and omnivores. Despite the small number of individuals for some species, the trophic structure described in the Caracu Stream cannot be considered a random result, as shown by the Mantel tests. Moreover, our results confirm the feeding habits observed by other authors in studies with these species in streams of the same hydrographic basin (Castro and Casatti, 1997; Casatti and Castro, 1998; Casatti, 2003).

We found that the ecomorphological gradient formed two groups in multivariate space: detritivores (Loricariidae) and insectivores/omnivores (Heptapteridae). Detritivores presented long caudal peduncles and large middle fins (except for the anal), which are morphological structures that are fundamental to their success in exploiting lotic environments. Because of these structures, they are capable of performing short displacements and stabilise their bodies while they move through the flowing water (Breda et al., 2005). Additionally, the greatest problem encountered by fishes that exploit the currents of rivers and streams is remaining on the substrate. In these environments, they suffer the effect of forces of resistance that tend to elevate their body, in particular the net pressure force, which is composed of two components: a lift force, acting normal to the axis of motion, and a drag force, acting along that axis and retarding the motion (Webb, 1974). It results from the more rapid movement of water molecules across the upper surface than the lower surface of the body (Bernoulli effect). However, this effect is eliminated when the fish remains in contact with the substrate, because there is no water pressure underneath its body. Therefore, the dorsoventral flattening and the development of paired fins (which increase the area of contact with the substrate; Kerfoot-Jr. and Schaefer, 2006) are morphological adaptations that allow the Loricariidae to fix themselves to the substrate associated with rushing torrents, minimising adverse effects on these fish.

On the other side of the ecomorphological gradient were the insectivores/omnivores, which exhibit compressed bodies and large anal fins and possess a greater capacity for maneuverability (Breda, 2005). Maneuverability is defined as the ability of organisms to perform quick small-angled maneuvers (Webb et al., 1996). Thus, species with these characteristics exhibit a superior performance in the exploitation of structurally complex habitats with low current velocity (Breda, 2005).

As in the principal components analysis, the CDA results confirm that the greatest segregation tendency was between detritivores and the other guilds. Moreover, this analysis showed that, in terms of morphology, the most similar individuals were correctly classified into the same guilds, with 100% precision and a high prediction success.

According to Casatti (2003), Loricarid detritivores use pasturing as a feeding tactic. In this type of behaviour, the organisms are supported on submerged rocks or branches, generally in stretches of river rapids, where they graze on the encrusted organic material on the surface of these substrates. Consequently, they are benefitted by the long caudal peduncle and the large proportions of the caudal and pectoral fins, which aid movement through the flowing water by using quick short-distance displacements, in addition to allowing maintenance of position and balance while the fish feed in the turbulent conditions of the river rapids. In contrast, the insectivores and omnivores that we collected presented characteristics that give them a great capacity for maneuverability and efficiency in the capture of relatively large preys and plants in refuges among rocks and backwater zones (greater compression of the body, development of the anal fin and large mouths). In these habitat types there is a large deposition of allochthonous (e.g., insects and plants from the terrestrial environment) and autochthonous material (e.g., insect larvae) (Casatti and Castro, 1998).

The large variability explained by axis 1 of the CDA did not represent anything unexpected, because the segregated groups are especially distant phylogenetic lineages, thus presenting the tendency to be ecomorphologically distinct. In fact, what most attracted our attention was the separation of the insectivores and omnivores on axis 2. These two guilds belong to close phylogenetic lineages, and, consequently, exhibit great morphological similarity (thus representing a lower proportion of variability in the multivariate space); however, we found that they demonstrate a case of ecomorphological divergence.

Rhamdia quelen, as observed by Casatti and Castro (2006), possesses a more compressed body than the other Heptapterids and, thus, presents a greater capacity for maneuverability, tending to occupy marginal backwater zones, where the flooded vegetation presents a great deal of structuring and spatial complexity. In these environments, this fish assumes a generalist profile (Gomes et al., 2001) and can be considered a bottom sweeper (Casatti and Castro, 1998). On the other hand, the insectivores prefer to inhabit areas near stretches of rapids (e.g., small spaces among the rocks, where the deposition of both terrestrial and aquatic insects is intense). In these environments, these organisms actively swim among rocks, where they capture their prey individually by excavating (while moving) and turning over the substrate (Casatti and Castro, 1998). In this way, they are benefitted by high aspect ratio values of the caudal fin and by large anal fin areas that confer a greater ability for continuous swimming while looking for food and aid in maneuvers during the capture of prey deposited near the bottom, respectively.

The results of the Mantel test revealed that body shape was intimately correlated with diet, i.e., morphologically similar species tend to be grouped into the same trophic guild. However, the relationships between morphology and ecology may be simply an artifact produced by phylogenetic relationships (Douglas and Matthews, 1992). Consequently, ecomorphological studies are more convincing when developed together with methods that prove whether the relationships between morphology and ecology originated from adaptive responses to selective environmental pressures. Thus, with the aid of a partial Mantel test, which permits the control of the effect of historical factors in ecomorphological relationships, the present study revealed that independent of the phylogenetic relationships, the body shape of the fishes of the Caracu Stream was related to local trophic structure. This suggests that the effects of phylogeny, even if apparently significant, did not limit the identification of adaptive relationships between morphology and ecology. Therefore, the Siluriformes of the Caracu Stream were ecomorphologically structured and morphology can be applied as an additional tool in predicting the trophic structure of this group.

In summary, this study revealed that among the Siluriformes of the Caracu Stream, trophic structure is related to the morphology of the species, independent of their phylogenetic relationships. This structure can be explained by the interspecific ecomorphological diversification pattern, which revealed differences in the occupation of the ecomorphological space by the trophic guilds. However, it is not possible to ignore the influence of behavioural, physiological and stochastic factors on the lifestyle of the species. Therefore, despite the fact that ecomorphology can be considered an important tool in the prediction of the exploited niche, it is of interest to combine behavioural and physiological experiments with ecomorphological studies. The predictive character of these approaches would provide greater precision in the analyses and significantly contribute to our understanding about mechanisms that allow the coexistence of species.

Acknowledgements – The authors would like to thank Horácio F. Júlio-Jr. (Universidade Estadual de Maringá – UEM), Alberto C. Peret (Universidade Federal de São Carlos – UFSCAR) and the reviewers for constructive comments, Weferson J. da Graça (UEM) for identification of the collected fishes, the biologists from the Trophic Ecology Laboratory of Nupélia – UEM (Norma S. Hahn, Carlos E. Corrêa, Gisele C. Novakowski and André N. Bozza); Ciro Y. Joko and Judy Rezende for help with the fieldwork, Sidinei M. Thomaz (UEM) for help with the English version of this manuscript and PEA/Nupélia/UEM for technical and logistic support. J. P. A. Pagotto and E. F. Oliveira are grateful to the Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES/Ministério da Educação) and C. B. Yamamura to Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq/Ministério de Ciência e Tecnologia) for funding.



AGOSTINHO, AA., JÚLIO-JR. HF., GOMES, LC., BINI, LM. and AGOSTINHO CS., 1997. Composição, abundância e distribuição espaço-temporal da ictiofauna. In VAZZOLER, AEAM., AGOSTINHO AA. and HAHN NS. (Eds.). A Planície de Inundação do alto Rio Paraná: aspectos físicos, biológicos e socioeconômicos. Maringá: EDUEM. p. 179-208.         [ Links ]

BREDA, L., 2005. Ecomorfologia de Astyanax altiparanae, Moenkhausia intermedia, Roeboides paranensis e Serrasalmus marginatus (Osteichthyes-Characidae) da planície alagável do alto rio Paraná, Brasil: variações inter e intra-específica. Maringá: Universidade Estadual de Maringá. 30 p. Dissertação de Mestrado em Ecologia de Ambientes Aquáticos Continentais.         [ Links ]

BREDA, L., OLIVEIRA EF. and GOULART, E., 2005. Ecomorfologia de locomoção de peixes com enfoque para espécies neotropicais. Acta Scientiarum Biological Sciences, vol. 27, no. 4, p. 371-381. doi:10.4025/actascibiolsci.v27i4.1271        [ Links ]

CASATTI, L., 2003. Alimentação dos peixes em um riacho do parque estadual Morro do Diabo, bacia do alto rio Paraná, sudeste do Brasil. Biota Neotropica, vol. 2, no. 2, p. 1-14.         [ Links ]

CASATTI, L. and CASTRO, RMC., 1998. A fish community of the São Francisco River headwaters riffles, southeastern Brazil. Ichthyological Exploration of Freshwaters, vol. 9, no. 3, p. 229-242.         [ Links ]

-, 2006. Testing the ecomorphological hypothesis in a headwater riffles fish assemblage of the rio São Francisco, southeastern Brazil. Neotropical Ichthyology, vol. 4, no. 2, p. 203-214.         [ Links ]

CASTRO, RMC. AND CASATTI, L., 1997. The fish fauna from a small forest stream of upper Paraná River basin, southeastern Brazil. Ichthyological Exploration of Freshwaters, vol. 7, no. 4, p. 337-352.         [ Links ]

DOUGLAS, ME. and MATTHEWS, WJ., 1992. Does morphology predict ecology? Hypothesis testing within a freshwater stream fish assemblage. Oikos, vol. 65, p. 213-224.         [ Links ]

GARUTTI, V., 1988. Distribuição longitudinal da ictiofauna em um córrego da região noroeste do estado de São Paulo, bacia do rio Paraná. Revista Brasileira de Biologia = Brazilian Journal of Biology, vol. 48, no. 4, p. 747-759.         [ Links ]

GATZ-JR., AJ., 1979. Ecological morphology of freshwater stream fishes. Tulane Studies in Zoology and Botany, vol. 21, no. 2, p. 91-124.         [ Links ]

GOMES, CL., GOLOMBIESKI, JI., GOMES, ARC. and BALDISSEROTTO, B., 2001. Biologia do jundiá Rhamdia quelen (Teleostei, Pimelodidae). Ciência Rural, vol. 30, no. 1, p. 179-185.         [ Links ]

GOTELLI, NJ. and ELLISON, AM. 2004. A primer of ecological statistics. Massachusetts: Publishers Sunderland. 479 p.         [ Links ]

GRAÇA, WJ., 2004. Caracterização morfológica dos peixes da planície de inundação do alto rio Paraná - MS. Maringá: Universidade Estadual de Maringá. 259 p. Dissertação Mestrado em Ecologia de Ambientes Aquáticos Continentais.         [ Links ]

GRAÇA, WJ. and PAVANELLI, CS., 2007. Peixes da planície de inundação do alto rio Paraná e áreas adjacentes. Maringá: EDUEM. 241 p.         [ Links ]

HAHN, NS., FUGI, R. and ANDRIAN, IF., 2004. Trophic ecology of the fish assemblages. In THOMAZ, SM., AGOSTINHO, AA. and HAHN, NS. (Eds.). The upper Paraná River and its floodplain: physical aspects, ecology and conservation. Leiden: Backhuys Publishers. p. 247-269.         [ Links ]

HELLAWELL, JM. and ABEL, R., 1971. A rapid volumetric method for the analysis of the food of fishes. Journal of Fish Biology, vol. 3, p. 29-37. doi:10.1111/j.1095-8649.1971.tb05903.x        [ Links ]

JACKSON, DA., 1993. Stopping rules in principal components analysis: a comparison of heuristical and statistical approaches. Ecology, vol. 74, no. 8, p. 2204-2214. doi:10.2307/1939574        [ Links ]

JOHNSON, DE., 1998. Applied multivariate methods for data analysis. California: Cole Publishing Company, 565 p.         [ Links ]

KERFOOT-JR., JR. and SCHAEFER, JF., 2006. Ecomorphology and habitat utilization of Cottus species. Environmental Biology of Fishes, vol. 76, p. 1-13. doi:10.1007/s10641-006-9000-0        [ Links ]

MAACK, R., 1981. Geografia Física do Estado do Paraná. 2nd ed. Rio de Janeiro: Secretaria da Cultura e do Esporte do Governo do Estado do Paraná. 450 p.         [ Links ]

McCUNE, B. and MEFFORD, MJ., 1999. PC-ORD: multivariate analysis of ecological data. Version 4.01. Oregon: MjM Software Design.         [ Links ]

MOTTA, PJ., NORTON, SF. and LUCZKOVICH, JJ., 1995. Perspective on the ecomorphology of bony fishes. Environmental Biology of Fishes, vol. 44, no. 1/3, p. 23-33.         [ Links ]

NORTON, SF. and BRAINERD, EL., 1993. Convergence in the feeding mode of ecomorphologically similar species in the Centrarchidae and Cichlidae. Journal of Experimental Biology, vol. 176, p. 11-29.         [ Links ]

NOVAKOWSKI, GC., FUGI, R. and HAHN, NS., 2004. Diet and dental development of three species of Roeboides (Characiformes: Characidae). Neotropical Ichthyology, vol. 2, no. 3, p. 157-162.         [ Links ]

OLIVEIRA, EF., GOULART, E., BREDA, L., MINTE-VERA, CV., PAIVA, LRS. and VISMARA, MR. . 2010. Ecomorphological patterns of the fish assemblage in a tropical floodplain: effects of trophic, spatial and phylogenetic structures. Neotropical Ichthyology, vol. 8, n. 3, p. 569-586.         [ Links ]

PAGOTTO, JPA., GOULART, E., OLIVEIRA, EF. and YAMAMURA, CB., 2009. A ecomorfologia como ferramenta para análise da estrutura de assembléias. In LANSAC-TÔHA, FA., BENEDITO, E., OLIVEIRA, EF. (Org.). Contribuições da história da ciência e das teorias ecológicas para a Limnologia. Maringá: EDUEM. p. 327-346.         [ Links ]

PANKHURST, NW., 1989. The relationship of ocular morphology to feeding models and activity periods in shallow marine teleosts from New Zealand. Environmental Biology of Fishes, vol. 26, p. 201-211. doi:10.1007/BF00004816        [ Links ]

PERES-NETO, PR., 1999. Alguns métodos e estudos em ecomorfologia de peixes de riacho. In CARAMASCHI, EP., MAZZONI, R. and PERES-NETO, PR. (Eds.). Série Oecologia Brasiliensis: ecologia de peixes de riachos. Rio de Janeiro: PPGE-UFRJ. p. 209-236. vol. 6.         [ Links ]

PETERSON, MS. and VANDERKOOY, SJ., 1996. Preservation-induced changes in morphometrics of fishes: influence on prey size-choice in juvenile walleye, Stizostedion vitreum (Mitchill). Ecology of Freshwater Fish, vol. 5, p. 133-139. doi:10.1111/j.1600-0633.1996.tb00045.x        [ Links ]

POUILLY, M., LINO, F., BRETENOUX, JG. and ROSALES, C., 2003. Dietary-morphological relationships in a fish assemblage of the Bolivian Amazonian floodplain. Journal of Fish Biology, vol. 62, p. 1137-1158. doi:10.1046/j.1095-8649.2003.00108.x        [ Links ]

REIS, RE., KULLANDER, SO. and FERRARIS JR., CJ., 2003. Check list of the freshwater fishes of South and Central America. Porto Alegre: EDIPUCRS. 729 p.         [ Links ]

ROHLF, FJ., 1988. NTSYS-pc: numerical taxonomy and multivariate analysis system. Version 1.50. New York. 199 p.         [ Links ]

SCHARF, FS., JUANES, F., ROUNTREE, A., 2000. Predator size - prey size relationships of marine fish predators: interspecific variation and effects of ontogeny and body size on trophic-niche breadth. Marine Ecology Progress Series, vol. 208, p. 229-248. doi:10.3354/meps208229        [ Links ]

SUZUKI, HI., VAZZOLER, AEAM., MARQUES, EE., LIZAMA, MAP. and INADA, P., 2004. Reproductive ecology of the fish assemblages. In Thomaz, SM.; Agostinho, AA. and Hahn, NS. (Eds.). The upper Paraná River and its floodplain: physical aspect, ecology and conservation. Leiden: Backhuys Publishers. p. 271-291.         [ Links ]

VAZZOLER, AEAM., 1996. Biologia da reprodução de peixes teleósteos: teoria e prática. Maringá: EDUEM. 169 p.         [ Links ]

WAINWRIGHT, PC., 1994. Functional morphology as a tool in ecological research. In WAINWRIGHT, PC. and REILLY, SM. (Eds.). Ecological Morphology: integrative organismal biology. Chicago: University Chicago Press. p. 42-59.         [ Links ]

WATSON, DJ. and BALON, EK., 1984. Ecomorphological analysis of fish taxocenes in rainforest streams of northern Borneo. Journal of Fish Biology, vol. 25, p. 371-384. doi:10.1111/j.1095-8649.1984.tb04885.x        [ Links ]

WEBB, PW., 1974. Hydrodynamics and energetics of fish propulsion. Bulletin/Fisheries Research Board of Canada, vol. 190, p. 1-159.         [ Links ]

WEBB, PW., LALIBERTE, GD. and SCHRANK, AJ., 1996. Does body and fin form affect the maneuverability of fish traversing vertical and horizontal slits? Environmental Biology of Fishes, vol. 46, p. 7-14. doi:10.1007/BF00001692        [ Links ]



Received June 1, 2010
Accepted August 5, 2010
Distributed May 31, 2011