Abstracts
Abstract
Aim This study investigated changes in the dietary composition and trophic niche breadth of Eigenmannia desantanai in the context of hydrological periods, rivers, and ontogeny.
Methods Collections were performed monthly on the Paraguay and Amonguijá Rivers between February 2009 and January 2011.
Results A total of 338 specimens of E. desantanai were collected, 224 of which came from the Amonguijá River and 114 from the Paraguay River. In all, 21 food items were identified. Fully remains of digested animals (RDA), Chironomidae, Cladocera, and Ostracoda showed greater importance in the diet of E. desantanai. Dietary composition was influenced by hydrological periods, followed by differences between sampled rivers, and ontogeny. In contrast, only hydrological periods explained variation in the E. desantanai trophic niche breadth.
Conclusions The diet of E. desantanai is mainly composed of Chironomidae, Cladocera, and Ostracoda; however, individuals consumed other food items owing to changes in hydrological periods, followed by characteristics of the Amonguijá and Paraguay Rivers and ontogenetic variation. In this respect, the results of this study are germane to the food ecology of E. desantanai, providing guidelines for the management and conservation of the species.
Keywords: diet; tuvira; floodplain; Paraguay River; Amonguijá River
Resumo
Objetivo O estudo buscou investigar se as mudanças na composição da dieta e na amplitude de nicho trófico de Eigenmannia desantanai podem ser explicadas pelos períodos hidrológicos, rios e/ou ontogenia dos peixes.
Métodos As coletas foram realizadas mensalmente nos rios Paraguai e Amonguijá, entre Fevereiro de 2009 a Janeiro de 2011.
Resultados Foram coletados 338 exemplares de E. desantanai, sendo 224 do Rio Amonguijá e 114 do Rio Paraguai. Ao todo, foram identificados 21 itens alimentares. Restos de animais digeridos (RAD), Chironomidae, Cladocera e Ostracoda apresentaram maior importância na dieta de E. desantanai. A composição da dieta foi influenciada pelos períodos hidrológicos, seguida pelas diferenças dos rios amostrados e da ontogenia. Em contrapartida, apenas os períodos hidrológicos explicaram a variação na amplitude do nicho trófico de E. desantanai.
Conclusões A dieta de E. desantanai é composta principalmente por Chironomidae, Cladocera e Ostracoda, no entanto, os indivíduos consumiram outros alimentos devido às mudanças dos períodos hidrológicos, seguida das características dos rios Amonguijá e Paraguai e da variação ontogenética. Neste contexto, os resultados deste estudo são pertinentes à ecologia alimentar de E. desantanai, fornecendo diretrizes para o manejo e conservação da espécie.
Palavras-chave: dieta; tuvira; planície de inundação; Rio Paraguai; Rio Amonguijá
1. Introduction
The Neotropical region has a highly diversified fish fauna and, consequently, diversity of life forms and life history. A striking characteristic of Neotropical fish fauna is food plasticity (Abelha et al., 2001) since fish diet may vary according to ontogeny (Dias et al., 2017a), phenology (Cunha et al., 2018), as well as intra/interspecific interactions (Silva et al., 2017).
In dynamic and productive environments, such as the Pantanal, the flood pulse is the main determinant of the structure and function of aquatic communities (Junk et al., 1989). Particularly in this system, hydrological variation throughout the year directly interferes with the availability and variety of food items, which consequently leads to changes in the fish diet (Ferreira et al., 2014; Scanferla & Súarez, 2016). The aquatic macrophytes that colonize this floodplain also play an important role in the complexity and heterogeneity of environments (Thomaz & Cunha, 2010; Dias et al., 2017b), providing shelter for insects, mollusks, periphyton, and fish (Silva et al., 2009; Saulino & Trivinho-Strixino, 2014), influencing the food chain (Grzybkowska et al., 2018).
Among the fish species existing in this floodplain, Eigenmannia desantanai belongs to the order Gymnotiformes and lives associated with macrophytes. It was previously identified as E. trilineata Lopez & Castello, 1996, and recently described by Peixoto et al. (2015) occurring in the Pantanal basins of the Cuiabá and Paraguay Rivers (Pacheco & Da-Silva, 2009; Súarez et al., 2013). In this region, E. desantanai is considered an important economic resource, as it is used as live bait by professional fishermen (Resende et al., 2006), and from an ecological point of view, it is an important source of food for large fish, thus contributing to the maintenance of floodplain fishes (Gimenes et al., 2013).
Knowledge about the trophic ecology of this species is restricted only to the North Pantanal and with few analyzed individuals (Santos et al., 2009; Corrêa et al., 2011; Ximenes et al., 2011), being that in the southern portion of the Pantanal, the species diet is unknown. Then, we have no data about spatial, temporal, and ontogenetic variation in feeding resource use in a seasonal environment as the Pantanal. In this sense, to expand knowledge in this area, the present study aimed to investigate changes in the feeding composition and trophic niche breadth of Eigenmannia desantanai among hydrological periods, rivers, and ontogeny.
2. Material and Methods
2.1. Study area
The study was carried out in the southern portion of the Pantanal, municipality of Porto Murtinho, Mato Grosso do Sul State, Brazil (Figure 1). Fish collection was carried out in the Paraguay and Amonguija rivers, which have different characteristics in terms of environmental heterogeneity, more specifically, the Paraguay River is the main watercourse of the Pantanal and approximately 300 m wide in the study area. It has a flow of around 0.81 m.s-1 (± 0.36 SD), and on the margins, there are banks of macrophytes Eichhornia azurea (Swartz) Kunth, Polygonum ferrugineum Wedd., and Urochloa subquadripara (Trin.) R.D.Webster. The Amonguijá River is a tributary of the Paraguay River. It is about 40 m wide with a slower flow (0.20 ± 0.23 m.s-1). The sampled section has approximately 50% of its bed covered by E. azurea, E. crassipes (Mart.) Solms, and P. ferrugineum, among other species of macrophytes.
Location of sampling points along the Amonguijá (green circles) and Paraguay (gray circles) Rivers in the southern Pantanal, Porto Murtinho, MS, Brazil.
The flood pulse is considered monomodal, and in the studied region, the peak occurs in the months of May, June, and July. Thus, the collection months were categorized as dry, rising-water, flood, and falling-water.
2.2. Data collection
The collections were performed monthly, during the day, between February 2009 and January 2011 (Authorization - SISBIO 13458-1). The locations were randomly defined along the river banks and on the macrophyte banks. To capture fish, rectangular sieves (0.8 x 1.2 m) and seines (1.5 x 5 m) were used, both with a 2 mm mesh, performed by two people. The fish were anesthetized with 10 mg/L of Eugenol, packed in plastic bags, labeled, and fixed in formaldehyde (10%). In the laboratory, the fish were preserved in ethanol (70%). Weight (g), head height, total length, and standard length (mm) of each individual were measured, and then the stomach was removed.
2.3. Stomach analysis
Stomach contents were weighed in grams to the nearest 0.0001 and analyzed using a stereomicroscope and microscope. Food items were identified with the help of specific keys by McCafferty (1981), Stehr (1987), and Mugnai et al. (2010) and then quantified by the Volumetric Method and Frequency of Occurrence (Hynes, 1950; Hyslop, 1980). The Food Importance Index (IAi) was also estimated as , where IAi = food index, i = 1,2 ..., n = certain food item, Fi = food item occurrence frequency (%), and Vi= food item volume (%) (Kawakami & Vazzoler, 1980).
Food items were grouped into different categories, such as remains of digested animals (RDA) composed of animal partially or totally digested; Chironomidae; Ostracoda; Cladocera; and Others, which was composed of items that presented low volume and occurrence, being Acarina, Amphipoda, Annelida, Araneae, Coleoptera, Copepoda, Concostracoda, Ephemeroptera larvae, Gastropoda, Culicidae larvae, Megaloptera, Nematoda, Odonata, Rotifera, Trichoptera, Filamentous Algae, and seeds.
2.4. Data analysis
In order to assess possible variations in dietary composition among hydrological periods, sites, and ontogeny, Permutational Multivariate Analysis of Variance (PERMANOVA) with the Bray-Curtis Coefficient (9999 permutations) was used. This analysis was carried out using a routine “adonis” in the vegan package (Oksanen et al., 2016).
The hydrological periods were defined according to the samples collected in the different months and rivers level, i.e., from February to April (Rising-water), from May to July (Flood), from August to October (Falling-water), and from November to January (Dry). The rivers (Paraguay and Amonguijá) were used as explanatory variables (factor) to infer if their characteristics (width, depth, velocity, aquatic macrophytes abundance) can change prey availability and consequently diet composition. To investigate ontogenetic effects, we used head height measurements in order to represent size variation over the life cycle, because the partial predation of the final portion of the body of Eigenmannia specimens may impede the use of body length as a proxy of fish age.
The Threshold Indicator Taxa ANalysis (TITAN) was used to detect food items considered indicators of the sampled months and the ontogeny of individuals. This analysis is based on the indicator value (Indval) scores (Dufrêne & Legendre, 1997). For this analysis, the “titan” function included in the “TITAN2” package was used (Baker & King, 2010; Baker et al., 2015).
The Levins coefficient (spaa package) was used to estimate the amplitude of the trophic niche for each fish. A covariance analysis was applied to verify the possible influence of the hydrological periods, rivers and head height (log) on niche breadth of the fish. The covariance analysis was also used to evaluate spatial, temporal and ontogenetic effect on volume of feeding items in stomach. All statistical analyses were performed on the R platform (R Development Core Team, 2021).
3. Results
A total of 338 individuals were analyzed, 224 (total length from 29.46 to 149.82 mm) from the Amonguijá River and 114 fish (total length from 60.23 to 175.85 mm) from the Paraguay River. Considering both rivers, head height varied from 4 to 21.47mm (median = 12.96mm). Of these, 330 fish had some stomach contents.
The diet was composed of 21 food items, and those most important were Chironomidae (IAiAmonguijá = 28.9%, IAiParaguay = 29.96%), Cladocera (IAiAmonguijá = 22.7%, IAiParaguay = 16.6%), and Ostracoda (IAiAmonguijá = 5.84%, IAiParaguay = 8.06%). The remains of digested animals (RDA) represented the majority of the diet in both environments (IAiAmonguijá = 35.14%, IAiParaguay = 39.62%). Other items contributed a lower food index and, thus, were grouped into a category designated as Others (IAiAmonguijá = 7.42%, IAiParaguay = 5.76%) (Figure 2).
Alimentary Index for Eigenmannia desantanai in the Amonguijá and Paraguay Rivers at Porto Murtinho, MS, southern Pantanal, Brazil.
Considering food intake by individuals of E. desantanai, ANCOVA results showed that they varied among rivers (F = 7.29; p = 0.007), river levels (F = 16.51; p < 0.001) and fish head height (F = 57.71; p < 0.001). Food intake was higher in the Amonguijá river, in the flooding The diet composition of E. desantanai varied significantly between hydrological periods (PERMANOVA: F = 8.16; p < 0.001), between rivers (F = 6.21; p < 0.001) and head height (F = 4.84; p < 0.001). Thus, the main determinant for variation in the diet was season, followed by differences between the Paraguay and Amonguijá Rivers, and the fish head height (Figure 3).
Food intake by Eigenmannia desantanai in southern Pantanal in function of sampled river (A), river water levels (B) and (C) fish size (head height).
The TITAN analysis detected the items Copepoda, Nematoda, and Cladocera as indicators from January to June (late dry and rising-water), and the falling-water period as marked by higher consumption of RDA, Ephemeroptera larvae, and Trichoptera. The item Araneae was consumed during the whole year, however in low abundance (Figure 4).
Variation of Eigenmannia desantanai food items over the months based on Threshold Indicator Taxa Analysis. The higher the value of the Z-score, the better the indication of the item.
This analysis also showed that some items were preferentially consumed according to fish size, for example, the Rotifera and RDA categories were indicative of individuals with a head height between 10 to 13 mm, whereas the larvae of Ephemeroptera, Culicidae, and Copepoda were predominantly consumed by larger fish (Figure 5).
Variation of Eigenmannia desantanai food items along ontogeny based on Threshold Indicator Taxa Analysis. The higher the value of the Z-score, the better the indication of the item.
The trophic niche breadth of E. desantanai was influenced by the river level (ANCOVA: F = 3.76; p = 0.01) and head height (F = 7.97; p < 0.01). However rivers did not influence trophic niche breadth (F = 2.84; p = 0.09) (Figure 6). Then, a wider niche breadth was recorded in larger fish and during the flooding period.
Trophic niche breadth for Eigenmannia desantanai. A) Amonguijá and Paraguay Rivers, B) Hydrological periods and C) Head height, at Porto Murtinho, MS, southern Pantanal, Brazil.
4. Discussion
Eigenmannia desantanai lives associated with macrophyte banks (e.g Eichhornia crassipes, E. azurea, Polygonum ferrugineum and Urochloa subquadripara) that offer shelter and food resources through the roots to various organisms (e.g Hyphessobrycon eques, Odontostilbe spp., Pyrrhulina australis, Prionobrama paraguayensis) (Pacheco & Da-Silva, 2009; Súarez et al., 2013), thus, the items identified in the stomach are a reflection of the habitat of this species. The diet was composed of both animal and plant materials, with especial reference to Chironomidae, Cladocera, and Ostracoda, being ingested in a similar way among fish from the Amonguijá and Paraguay Rivers. Similar results were obtained in other studies (Peretti & Andrian, 1999; Pelicice & Agostinho, 2006; Brandão-Gonçalves et al., 2010; Dias et al., 2017a) in which they found that the diet E. trilineata was based on aquatic insects (Chironomidae), terrestrial insects (Orders Diptera, Coleoptera, Odonata, Hymenoptera), zooplankton (Ostracoda, Cladocera) and sediments. The high content of remains of digested animals (RDA) in the stomach of E. desantanai samples can be explained by the crepuscular and nocturnal behavior of the genus Eigenmannia (Mago-Leccia, 1994). Collections occurred during the day, and it is likely that prey items were already undergoing digestion.
The category others was considered accidental, or additional, at certain times of the year. These results are consistent with the Optimal Foraging Theory, which predicts that predators tend to maximize gains and reduce energy costs associated with obtaining resources, taking into account several factors, such as energy cost, satiety, and, above all, the availability of food resources (MacArthur & Pianka, 1966). Thus, this variety of accidental items mat represent a strategy used by E. desantanai to meet its energy demands when its main food sources are in short supply (Dill, 1983). Duarte et al. (2019) studied the diet of Sternarchella calhamazon (Order Gymnotiformes) in the Purus River (Amazon Basin) and demonstrated that the ingestion of various food items at low frequency resulted from availability, not food preference, since the environment changes seasonally. This same hypothesis can explain the number of low frequency of several prey items in the diet of E. desantanai.
Differences in food intake between sampled rivers, river level and fish size (in our case using head height) are expected due to environmental differences in a dynamic environment as floodplain rivers. The Amonguijá river presents higher coverage of aquatic macrophytes and lower water velocity when compared to the Paraguay river, then, it is likely that feeding availability (or simply ease to capture) is higher and competitive interactions relaxed. These hypotheses are consistent with some theoretical expectation about resource partitioning when more “adequate” habitats offer more quantity/quality of resources (Correa e Winemiller, 2014). Other important results indicated higher food intake during the flood season and by larger fish, once the increase of available area for feeding (in the flood period) also offer new habitats for foraging by E. desantanai. Larger fishes also have a larger mouth and consequently they can consume prey that is not available for smaller individuals; moreover, they have higher energy requirements to maintain their metabolism (Quirino et al., 2017; Cavalheiro & Fialho, 2019).
Season influenced dietary composition, and it was the main predictor of trophic niche breadth for E. desantanai. In periods of late dry and rising-water, the diet was represented by Copepoda, Nematoda, and Cladocera. On the other hand, in the period of falling-water, we observed a predominance of RDA, Ephemeroptera larvae, and Trichoptera. This trophic flexibility is the result of species adaptation to oscillation in the availability of prey in a floating environment (Uieda & Pinto, 2011), as is the case of the Pantanal. This pattern of alternation in the diet is expected for fish that inhabit environments subject to hydrological changes. Moreover, as each prey species responds differently to seasonal variation, the predator depends on the plasticity of food resources for survival. This variation in dietary composition has already been reported in other fish species in floodplains (e.g., Ximenes et al., 2011; Quirino et al., 2015; Scanferla & Súarez, 2016; Costa-Pereira et al., 2017).
Spatial variation in dietary composition suggests that differences in the structure of the sampled habitats may influence the food supply for E. desantanai. For example, Chironomidae and Ostracoda were more abundant in the Paraguay River, while Cladocera and Other items were more abundant in the Amonguijá River. Evidence supports that macrophyte banks can retain zooplankton organisms in floodplain environments (Hamilton et al., 1990) wherein ponds with high macrophyte coverage can have a density of zooplankton up to 100 times greater than that of rivers. In this study, the difference between these environments with greater macrophyte coverage and lower current speed in the Amonguijá River may lead to a higher zooplankton density, changing its supply and, consequently, consumption by fish. On the other hand, results did not show differences in niche breadth between sampled rivers. Then, food intake and diet composition differ between Amonguijá and Paraguay rivers, however trophic niche breadths are similar. Our results suggest that despite higher flood intake and different prey compositions in the Amonguijá river, the number of prey and proportional distribution among them is statistically equal when compared to the Paraguay river.
Ontogenetic variation in the feeding of Eigenmannia has already been evaluated (e.g., Giora et al., 2005, for E. trilineata). It was found that juveniles feed mainly on microcrustaceans, digested organic material, and autochthonous insects, while adults consume mainly the last two food items mentioned. Similar results for other fish species have also been found (e.g., Dias et al., 2017a; Barreto et al., 2008). These dietary differences result from differences in energy requirements and morphological limitations (Abelha et al., 2001). This change in dietary composition throughout ontogeny could also be a strategy to minimize the overlap of trophic niche between different age groups for E. desantanai. Other studies have reported on the sharing of food resources in fish (Zaret & Rand, 1971; Brito et al., 2019). Therefore, in addition to being influenced by the morphometric characteristics of the organisms, dietary changes throughout ontogeny can also be explained by differences in energy content, as well as by mechanisms to avoid intraspecific competition. Here, it is worth mentioning that although we detected ontogenetic variation in the preference of food items, the absence of smaller individuals in our samples impeded the investigation of the diet of small immature fish.
In conclusion, our data showed that Chironomidae, Cladocera, and Ostracoda were the main resources in the diet of E. desantanai. Dietary composition was strongly influenced by temporal variation, followed by variation between Paraguay and Amonguijá Rivers and then by ontogeny. Therefore, the results of this study are germane to the food ecology of E. desantanai, providing guidelines for the management and conservation of the species, which is considered a key economic resource in the studied region.
Acknowledgements
We are grateful to Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq), FUNDECT and Centro de Pesquisas do Pantanal (CPP) for financial support. We are also grateful for many persons that contributed with logistical support in the field and laboratory. Y. R. Súarez is supported by productivity grants from CNPq.
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Cite as: Gouveia, E.J., Rondon, P.L. and Súarez, Y.R. Feeding ecology of Eigenmannia desantanai (Gymnotiformes: Sternopygidae) in southern Pantanal, Brazil. Acta Limnologica Brasiliensia, 2022, vol. 34, e2.
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Edited by
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Associate Editor: Fernando Mayer Pelicice.
Publication Dates
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Publication in this collection
07 Jan 2022 -
Date of issue
2022
History
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Received
19 Oct 2020 -
Accepted
25 Nov 2021