- Research article
- Open Access
Trophic diversity in the evolution and community assembly of loricariid catfishes
BMC Evolutionary Biology volume 12, Article number: 124 (2012)
The Neotropical catfish family Loricariidae contains over 830 species that display extraordinary variation in jaw morphologies but nonetheless reveal little interspecific variation from a generalized diet of detritus and algae. To investigate this paradox, we collected δ13C and δ15N stable isotope signatures from 649 specimens representing 32 loricariid genera and 82 species from 19 local assemblages distributed across South America. We calculated vectors representing the distance and direction of each specimen relative to the δ15N/δ13C centroid for its local assemblage, and then examined the evolutionary diversification of loricariids across assemblage isotope niche space by regressing the mean vector for each genus in each assemblage onto a phylogeny reconstructed from osteological characters.
Loricariids displayed a total range of δ15N assemblage centroid deviation spanning 4.9‰, which is within the tissue–diet discrimination range known for Loricariidae, indicating that they feed at a similar trophic level and that δ15N largely reflects differences in their dietary protein content. Total range of δ13C deviation spanned 7.4‰, which is less than the minimum range reported for neotropical river fish communities, suggesting that loricariids selectively assimilate a restricted subset of the full basal resource spectrum available to fishes. Phylogenetic regression of assemblage centroid-standardized vectors for δ15N and δ13C revealed that loricariid genera with allopatric distributions in disjunct river basins partition basal resources in an evolutionarily conserved manner concordant with patterns of jaw morphological specialization and with evolutionary diversification via ecological radiation.
Trophic partitioning along elemental/nutritional gradients may provide an important mechanism of dietary segregation and evolutionary diversification among loricariids and perhaps other taxonomic groups of apparently generalist detritivores and herbivores. Evolutionary patterns among the Loricariidae show a high degree of trophic niche conservatism, indicating that evolutionary lineage affiliation can be a strong predictor of how basal consumers segregate trophic niche space.
In rivers of tropical South America, loricariid catfishes (also known as plecos or suckermouth armored catfishes) are ubiquitous and easily identified by their distinctive armored plating and ventrally positioned jaws with a fleshy oral disk. Loricariid jaws permit efficient foraging on benthic food items and span a wide range of morphologies, from robust jaws specialized for gouging wood [1–4]; Figure 1B, to gracile jaws for winnowing loose sediments, and pincer-like jaws for probing crevices [1–3]; Figure 1A. Despite their taxonomic richness and jaw diversity, loricariids display relatively little dietary diversity. We reviewed published studies of loricariid gut contents spanning over 100 species, 20 drainages, and 13 countries (Additional file 1: Table S1). Findings from these studies reveal diets dominated by fine particulate detritus, usually of undetermined origin, mixed with lesser fractions of algae, other plant matter, and occasionally benthic invertebrates.
Detritus is the principle pathway by which primary production enters food webs globally . In rivers, detritus is foundational to metazoan food webs  and critical to ecosystem function . This is especially true in tropical rivers, where detritivorous fishes are highly diverse and abundant enough to support major commercial fisheries . Unlike predators, which commonly select prey based on their general morphology , detritivores selectively forage based on cryptic and continuously variable aspects of the elemental and nutritional composition of detritus [1, 10–12]. Although presumably detectable by detritivores [10, 11], variation in detrital quality is difficult to quantify and remains poorly understood. The extent to which dietary discrimination yields niche partitioning within local detritivore assemblages and the influence of phylogeny on partitioning of detritivore trophic niches are just beginning to be examined [1, 13].
A growing body of theoretical  and empirical [14, 15] research suggests that diverse, sympatric, and apparently functionally redundant assemblages of herbivores may coexist via partitioning of relatively cryptic elemental and nutritional gradients of the food resource spectrum. Sympatric herbivorous insects partition trophic niches according to ratios of carbohydrate and protein , and apparently non-selective, filter-feeding bivalves demonstrate similarly cryptic niche differentiation along stoichiometric gradients . Taxonomic groupings observed in these and other studies [16, 17] suggest that phylogeny strongly influences the biochemical composition of these consumers’ diets; however, modern phylogenetic comparative methods have yet to be applied to investigations of niche partitioning among detritivores. Herein, we examine the evolutionary context of trophic niche diversity among detritivorous loricariids by estimating trophic positions of individuals in local assemblage isotope space, then regressing these data onto the most recent and comprehensive phylogeny for the family.
Stable isotope analysis provides a powerful means for investigating trophic ecology [1, 8, 9, 15], in part because it can more effectively reveal trophic partitioning among detritivores than gut contents analysis . Detritivores have rapid gut passage rates , derive major nutritional contributions from microbial decomposers [1, 18], and selectively feed upon heterogeneous yet amorphous detrital fractions [10, 11]. These features reduce the utility of visual analysis of gut contents, but lend themselves to isotope analyses capable of quantifying and integrating food items assimilated over periods spanning several days to weeks . Consumer tissue δ13C reflects an average aggregate isotopic signature of all basal production sources assimilated , and δ15N corresponds to variation in trophic level and dietary protein content . Studies inferring community trophic structure from isotopic data often lack precision in differentiating basal resource categories [21, 22]; however, even without finely resolved basal resource data, distributions of consumers in isotope biplot space can be used to examine trophic niche size, spacing in community niche space, resource partitioning , and niche shifts in time or space [24, 25].
Herein, we introduce a novel method that builds upon several recently proposed approaches for comparing community trophic structure using the isotopic centroid (the mean for all species in a local assemblage) as a reference point [23–25]. Instead of calculating only distances from the centroid to component taxa  or patterns of centroid movement through absolute isotope space [24, 25], we use vectors to describe both distance and position of consumer taxa relative to their local assemblage centroid, and use the centroid as a means of standardization that allows datasets from different times and places to be combined. Assemblage centroid-standardized isotope vector analysis (ACSIVA) produces a metric that describes an individual consumer’s trophic position in relation to other consumers in the same habitat (in contrast to the traditional practice of presenting isotopic ratios of consumers in relation to either resources or an arbitrary isotopic standard [1, 19–22]). ACSIVA facilitates comparisons across geographic and temporal ranges as well as phylogenetic regressions to reveal evolutionary influence on contemporary assemblage structure.
Given that loricariid diets are largely limited to detritus, algae, and in special cases other basal resources such as wood  (see Additional file 1: Table S1 for summary of published diet studies), we predicted that the total range of species δ15N centroid deviations would reflect a single trophic level (i.e., this range will be less than the 5.2‰ maximum tissue–diet discrimination range reported for Loricariidae ). Also, given recent research  suggesting that loricariids with derived jaw morphologies  defined by narrow, medial clusters of elongate teeth (e.g., Figure 1A) could use these teeth to supplement their detritivorous diet with insect larvae pried from holes in benthic substrates (Additional file 1: Table S1), we predicted that taxa with these jaws will be 15 N-enriched relative to loricariids with broader jaws and greater numbers of shorter teeth designed for scraping or raking (e.g., Figure 1C). Finally, given the potential that dietary enrichment with insect protein may correspond with specialized morphologies or behaviors [1, 2], and that vertical (δ15N) trophic position can likely be maintained across food chains supported by primary production sources with different δ13C signatures [20–23], we predicted that the relative position of loricariids along the δ15N axis should be more phylogenetically conserved than distributions across the δ13C axis.
Mean values for loricariid species displayed a total range of δ15N assemblage centroid deviation spanning 4.9‰ and a total range of δ13C deviation spanning 7.4‰ (Figure 2B). As predicted, total δ15N range fell within the tissue–diet discrimination range (i.e., trophic fractionation range), observed in a controlled laboratory study of Loricariidae (4.1–5.2‰) , suggesting that loricariids essentially occupy a single trophic level within which δ15N variation corresponds to differences in dietary protein content . Total δ13C range of species means was less than the distribution of δ13C ranges (10–17.5‰) reported for entire fish communities in four different Neotropical rivers , suggesting that loricariids selectively consume and assimilate a restricted subset of the basal production spectrum supporting fish biomass in these ecosystems.
Phylogenetic regressions were conducted first on the entire data set of 649 individual assemblage centroid-standardized vectors (Figure 2A, Table 1). Because of the highly uneven distribution of sample sizes across sites and the potential for site bias, a second analysis was conducted on a more restricted data set consisting of 120 vectors representing the mean trophic niche of each genus at each site (Figure 2B, Table 2). In each case, the phylogenetic regression took full consideration of the two-dimensional (X = δ13C, Y = δ15N) character of the data but for interpretational clarity, cladograms color-coded to represent evolutionary shifts along the vertical δ15N axis (Figure 3A, B, Additional file 2: Figure S1) are presented separately from cladograms representing variation along the horizontal δ13C axis (Figure 4C, Additional file 3: Figure S2). In the analysis of individual vectors, 20 of 33 genera had a mean vector significant at P < 0.1 (Figure 3A, Table 1). In the analysis of genus mean vectors, the number of genera with statistically significant mean vectors dropped to seven (Figure 3B, Table 2), largely because many loricariid genera have geographically restricted ranges and most were represented in this study at only one or few sites (Table 1). Regardless, the evolutionary patterns recovered by these analyses were nearly identical (Figure 3A, B). Both recovered a basal division between 15 N-enriched Astroblepidae and 15 N-depleted Loricariidae, which is consistent with gut contents data describing Astroblepidae as predominantly insectivorous and Loricariidae as predominantly herbivorous-detritivorous (See Additional file 1: Table S1 for summary of published diet data). Within Loricariidae, both analyses also revealed seven transitions between relatively 15 N-depleted and relatively 15 N-enriched diets, however the locations (nodes) of transition differed slightly (Figure 3A, B). Both analyses also recovered a phylogenetically conserved reversion to 15 N-enriched diets at the base of the highly diverse tribe Ancistrini, with only three of 18 ancistrin genera reverting back to relatively 15 N-depleted diets (Ancistrus, Dekeyseria, and Panaque in the first analysis, Figure 3A; Ancistrus, Dekeyseria, and Lasiancistrus in the second analysis, Figure 3B).
The only ancistrin exception to be recovered in either analysis as both 15 N-depleted and 13 C-enriched, was Panaque, one of only two extant fish lineages– both in the Loricariidae – known to specialize on a diet consisting almost entirely of wood [1–4]. The other wood-eating lineage is the Hypostomus cochliodon group (tribe Hypostomini), a clade that has converged evolutionarily on a Panaque-like jaw morphology [1–3] and was also recovered in the individual analysis as having an isotope vector nearly parallel to that of Panaque (see Additional file 2 for mean genus vectors from the individual analysis). Moreover, vectors derived from both the individual mean and genus mean for the Loricariinae genera Loricaria and Pseudoloricaria were 15 N-depleted and 13 C-enriched, and these genera have also been reported to consume fractions of allochthonous plant material (e.g., seeds, fruits, leaves, and flowers) in addition to detritus (see Additional file 1: Table S1). Although these parallelisms provide evidence that vector direction corresponds with dietary niche, the pattern was only partially corroborated in our reduced analysis of mean genus vectors (Figure 3B), perhaps due to insufficient sample size. Likewise, jaw morphologies among non wood-eating Ancistrini displayed gross correspondence with patterns of 15 N-enrichment that were most apparent in the individual analysis (Additional file 2: Figure S1). Genera for which fewer, larger, and more medially clustered teeth (Figure 1A) are taxonomically diagnostic (e.g., Pseudacanthicus, Leporacanthicus, Spectracanthicus, Scobinancistrus, Lithoxus) tended to be more 15 N-enriched than genera with long rows of many small teeth (Figure 1C; e.g., Ancistrus, Baryancistrus, Lasiancistrus, Chaetostoma, Dekeyseria; Additional file 2: Figure S1) [1–3].
Evolutionary patterns of 13 C assimilation were different from those of 15 N. Phylogenetic regression of genus mean vectors computed from individual values recovered 11 transitions between relatively 13 C-enriched and relatively 13 C-depleted lorcariids (Additional file 3: Figure S2), and regression of genus vectors computed from their means at each site recovered 14 transitions (Figure 3C; versus seven transitions for δ15N recovered in both analyses). These discrepancies support our hypothesis that loricariid catfishes are more evolutionarily flexible with regard to specific primary production sources consumed compared with the protein content of their diet. Nonetheless, δ13C distributions of loricariids also show some evidence of trophic specialization.
Most neotropical fish communities, including loricariid assemblages, avoid consuming or assimilating 13 C-enriched C4 grasses and selectively consume and assimilate larger fractions of relatively 13 C-depleted C3 macrophytes, algae, and particulate organic carbon [1, 8, 22, 26]. This may explain the much narrower total range of loricariid mean species δ13C centroid deviation (Figure 2B) relative to published ranges of neotropical river fish communities containing diverse species representing multiple families and ecological strategies . Moreover, this subset of basal resources that are preferentially consumed shows relatively broad but consistent patterns of δ13C variation that can be used to inform our understanding of trophic diversification and specialization among loricariid lineages. Particulate organic carbon is typically most 13 C-depleted, C3 macrophytes are most 13 C-enriched, and algae, although showing large variation in time and space, tend to have intermediate δ13C signatures . Phylogenetic regressions based on the individual-based genus means and site-based genus means revealed similar evolutionary patterns among the Loricariinae (Figure 3C; Additional file 3: Figure 2): Harttiini plus Farlowellini and their common ancestor consume and assimilate relatively 13 C-depleted resources (e.g., particulate organic carbon), whereas their sister clade (Loricariini) specializes on relatively 13 C-enriched resources (e.g., macrophytes). Both data sets also indicate that the genus Harttia underwent a reversion to a relatively 13 C-enriched diet. These patterns are corroborated by both gut contents and jaw functional morphological data. Gut contents reveal large fractions of higher plants and plant parts in diets of the Loricariini genera Loricaria, Pseudoloricaria, and Rineloricaria (whereas Sturisoma and Farlowella feed mostly on amorphous detritus; Additional file 1: Table S1), and Loricariini occupy a unique, non-overlapping region of jaw functional morphospace distinct from all other loricariids .
Evolutionary diversification of Loricariidae in assemblage isotope-niche space demonstrates the potential for herbivores and detritivores to radiate adaptively by partitioning seemingly homogenous food resources along elemental-nutritional gradients. Phylogenetic analyses of both individual and grouped (genus x site mean) data partitions revealed concordant patterns of early diversification into opposite ends of a gradient in dietary protein content as inferred from relative 15 N enrichment (Figure 3A, B). In contrast to its sister lineage (Astroblepidae), Loricariidae was recovered as plesiomorphically 15 N-depleted, reflecting an evolutionary transition to a mostly herbivorous-detritivorous diet contemporaneous with the origin of a major functional innovation of the jaw that is synapomorphic for Loricariidae: a novel adductor mandibulae division that inserts directly onto the upper jaw . Within Loricariidae, the basal lineages (Hypoptopomatinae, Loricariinae, Hypostomini, and Pterygoplichthyini) were recovered as plesiomorphically 15 N-depleted, whereas Ancistrini was revealed to have undergone a derived shift back toward 15 N-enriched diets. 15 N-enrichment of Ancistrini combined with its nested phylogenetic position suggests that members of this clade may have specializations allowing them to consume basal resources with more protein , indicative of a higher quality diet.
Several concordant aspects of Ancistrini morphology, behavior, ecology, and biogeography point to a mechanism by which community ecological processes may have contributed to observed evolutionary patterns in δ15N. Ancistrins are distinguished by having well-developed lateral clusters of quill-like cheek-spines (odontodes; Figure 1a) [3, 28] that are forcefully erected and used as weapons during inter- and intra-specific threat displays. In aquaria, these threat displays are particularly associated with competition for food and territory (NKL, KOW, JWA, pers. obs.). In natural habitats, ancistrins are known to display remarkably even spacing along the stream bed , and biogeographical research  has observed that phylogenetically basal, non-ancistrin loricariids are often limited to regions occupied by few or no ancistrins. Together with observed patterns of 15 N-enrichment, these lines of evidence suggest that the Ancistrini may use aggression and territoriality to outcompete non-ancistrin taxa for access to relatively high-quality benthic resources. This, in turn, may have contributed to their taxonomic and functional diversity: The Ancistrini includes almost 30% (243 spp.) of the 831 currently recognized species in Loricariidae  and they demonstrate broader jaw morphological diversity than any other tribe in the family .
In addition to the paradox of low apparent dietary diversity (Additional file 1: Table S1) accompanied by high jaw diversity  that motivated this study, the Loricariidae confront stoichiometric challenges that may partially explain patterns of trophic differentiation that are only chemically discernable. Loricariids have a dense endoskeleton and are covered with dermal plates composed primarily of calcium phosphate (Figure 1), giving them a high physiological demand for dietary phosphorus [10, 16]. Paradoxically, the rivers and streams inhabited by loricariids  as well as the detritus and biofilm that most loricariids consume  tend to be highly P deficient. Discrepancies between dietary P availability and physiological P demand are sufficiently great among the loricariid species investigated to date, that these fishes are the only vertebrates known to have their somatic growth limited by P availability under natural conditions . Given these extreme stoichiometric challenges, loricariid fitness should be particularly sensitive to variation in the C:N:P ratios of food resources , and stoichiometric gradients likely provide an important dimension for niche segregation [12, 14, 15]. Indeed, in the only loricariid assemblage for which stoichiometric data are available, species exhibited interspecific variation along a continuous gradient in whole-body %P . Although relationships between the C:N:P ratios and the isotopic signatures of loricariid trophic resources remain uninvestigated, diversification of aquatic consumers along an δ15N/δ13C gradient has been shown to be consistent with differential assimilation of dietary components diverging in elemental ratios .
The most remarkable and perhaps most stoichiometrically unbalanced dietary specialists within Loricariidae are species of the wood-eating genus Panaque (tribe Ancistrini) and the Hypostomus cochliodon group (tribe Hypostomini). Both of these distantly related lineages possess specialized jaws and chisel-like teeth (Figure 1B) [1–4], and have gut contents dominated by wood particles [1, 4, 33]. Nearly parallel isotopic vectors between Panaque and the H. cochliodon group (Additional file 2: Figure S1) recovered in the analysis of individual vectors suggests that these lineages occupy a similar yet distinctive trophic niche relative to sympatric loricariids. Nearly parallel isotopic vectors between these wood-eaters and the Loricariinae genera Loricaria and Pseudoloricaria, which are known to consume large fractions of terrestrial seeds, fruits, leaves, and flowers (see Additional file 1: Table S1), supports the correspondence of this isotopically defined niche with a diet of allochthonous plant material. Despite the convergence of wood-eaters on a diet that is rare among vertebrates and unique among fishes, detailed analyses of the digestive physiology of these loricariids has shown them to be unspecialized and functionally similar to non-wood-eating loricariids [33, 34]. Loricariids as a whole are largely unable to digest lignocellulose, and instead derive most nutrients and energy from easily digestible breakdown products (e.g., disaccharides and dipeptides) that are produced during microbial degradation of submerged, decomposing wood [1, 33, 34].
Further examples of correlation between jaw morphology and a lineage’s position in δ15N/δ13C assemblage isotope space can be seen among the non-wood-eating Ancistrini and Loricariini (Figure 3). Ancistrin genera that are diagnosed by having jaws with fewer, larger, and more centrally clustered teeth (Figure 3A; Leporacanthicus, Lithoxus, Pseudacanthicus, Scobinancistrus, Spectracanthicus) are more 15 N-enriched than genera characterized by having larger numbers of smaller teeth arranged in long rows (Figure 3A; Ancistrus, Baryancistrus, Chaetostoma, Dekeyseria, Lasiancistrus). These data together with limited gut contents data suggest that the pincer-like jaws of the former group may be specialized for consumption of invertebrates residing in holes and crevices in wood, rocks, and clay nodules in a manner also hypothesized for tube-snouted species of electric fishes [1, 35]. In contrast, broad, brush-like jaws of the latter group appear specialized for scraping benthic substrates to dislodge and ingest fractions of detritus and biofilm that are lower in protein content . The Loricariini are distinguished by having jaws that are morphologically and functionally distinct from all other Loricariids  and they show a derived preference for relatively 13 C-enriched food resources (Figure 3C; Additional file 3: Figure S2) consistent with a dietary preference for the various parts of true plants (i.e., seeds, leaves, flowers; Additional file 1: Table S1). Finally, our conclusions are consistent not only with the isotopic signatures of consumers and with an understanding of jaw functional morphology , but also with local-scale variation in the taxonomic and elemental composition of benthic algal turfs, biofilms and detritus [1, 10, 14, 20, 36–38].
Our study introduces the ACSIVA method of visualizing a consumer’s trophic position relative to sympatric taxa in isotope biplot space, and uses this method to integrate isotopic data both spatially across landscapes and evolutionarily across a phylogeny. Our analysis suggests that Loricariidae should be seen not only as a highly diverse phyletic radiation, but also as an ecological radiation that has diversified along trophic niche dimensions that were heretofore cryptic, yet consistent with previously observed jaw morphological diversity . Current understanding of ecological radiation has been heavily influenced by studies of plants and vertebrates that diversified among island archipelagos and lakes, but there are few prominent examples of ecological radiations in river basins or among the detritivores and herbivores that dominate food webs in tropical rivers and virtually all other ecosystems. The frequently amorphous appearance and low taxonomic resolution achievable for gut contents of most herbivores and detritivores may account for our currently poor understanding of niche relationships within this important trophic guild. Detritivores and herbivores appear to select food items based more on chemical and nutritional qualities than taxonomy or morphology [1, 10–12, 14, 15]. By estimating molecular patterns of food resource assimilation over time, stable isotope, fatty acid signature analysis , and nutritional physiological approaches  provide powerful tools for investigating herbivore and detritivore niche diversification and partitioning.
We sampled 32 genera (79 species) of Loricariidae and 1 genus (3 species) of Astroblepidae in 19 assemblages distributed across the Amazon, Orinoco, and Essequibo drainage basins (Figure 4, Table 1; see Additional file 5: Table S2 for a list of species by locality). Each assemblage study site consisted of a reach less than 200 m long, with shallow habitat that was thoroughly sampled on a single day at the end of each region’s dry season by experienced personnel using combinations of nets, rotenone, and electricity. Fish specimens were euthanized by emersion in a 1% solution of tricaine methanesulfonate (MS-222), and then small (<1 gm) samples of postdorsal-fin epaxial muscle were excised and preserved with approximately 2 tsp table salt (NaCl) in small ziplock bags according to standard methods . Specimens from which samples were excised were fixed in 10% formalin and deposited in institutions in North America (Auburn University Museum, Auburn, AL; Academy of Natural Sciences, Philadelphia, PA) and South America (Natural Sciences Museum of Guanare, Venezuela; San Marcos University Natural History Museum, Lima, Peru; University of São Paulo Zoological Museum, Brazil; University of Guyana Biodiversity Center, Georgetown, Guyana). All animal handling was approved by Auburn University Institutional Animal Care and Use Committee protocols 2004–0694 and 2007–1239.
Tissue samples (649 total) were processed following standard protocols , with δ13C and δ15N mass spectrometric isotope analyses performed at the Analytical Chemistry Laboratory, University of Georgia, Athens, using a Carlo Erba CHN elemental analyzer and a Finnigan Delta C mass spectrometer. In order to avoid biases in the calculation of the centroid due to sample-size, all δ13C and δ15N signatures for each species were grouped and a mean for each species was calculated. These mean species values were then used to compute each local assemblage centroid (See Additional file 4: Figures S3–10 for isotope biplots of all local assemblages examined, including means and standard deviations for all species examined). To determine the statistical significance of the mean vector for a given taxon, all vectors between the assemblage centroid and each individual in an assemblage were calculated trigonometrically, producing 649 individual x assemblage vectors (Figure 2A). For the phylogenetic regressions, genera were used as operational taxonomic units because most represent species with similar trophic ecologies and jaw morphologies  and because they represent well-supported clades at the limit of phylogenetic resolution currently available for family Loricariidae. Hypostomus, which has a broad range of jaw morphologies, was broken into a group represented by members similar to the type of the genus H. plecostomus and the wood-eating species of the H. cochliodon group .
The 649 vectors were used to run two analyses, an individual-based analysis, and a genus x site analysis: In the individual-based analysis the 649 vectors were subdivided into genera irrespective of site and a single mean vector was calculated for each genus. In the analysis of genus x site means, 120 vectors representing the mean vector for each genus at each site were calculated from the 649 original individual vectors (Figure 2C). In the first analysis, sample sizes were highly unevenly distributed across sites so that results would be biased toward those sites with the highest sample sizes. This was addressed in the second analysis by reducing all individual samples at a given site to a single mean vector. The statistical significance of the mean vector for each genus in each analysis was evaluated using Rayleigh’s Z (Tables 1, 2; Figure 3), and the uniformity of vector distribution was evaluated using Rao’s spacing test (Tables 1, 2). All vector calculations were performed using Oriana software (v4.0 for PC, Kovach Computing Services).
Given the potential that both direction and length of taxon-specific assemblage centroid standardized vectors may vary in response to assemblage size alone, without an accompanying shift in relative trophic position of the taxon, we examined correlations between these variables and assemblage species richness in a limited subset of five genera for which sample sizes allowed statistical tests (Table 3). Tests were conducted on both individual vectors and on genus mean vectors: Individual vectors for three of five genera showed a significant relationship between vector direction and assemblage size, but only one of these (Chaetostoma) also had a significant relationship between vector length and assemblage size (Table 3: Test 1). None of these relationships were detected in the analysis of genus mean vectors (Table 3: Test 2). Given that taxon identity is the major independent variable examined herein, and that results of phylogenetic regressions run using both the individual and restricted (genus mean) datasets were almost indistinguishable, systematic effects of assemblage size should be nominal relative to taxon identity and trophic position.
Ancestral state reconstructions were performed via a phylogenetic least-squares (PLS) criterion  that considered both phylogeny [3, 43, 44] and branch length. Vector data contain both angle (direction) and magnitude (length) components that are not independent; however, vectors can be projected into Cartesian coordinate space yielding X and Y components that are independent. Analyzing these separately preserves both angle and magnitude. Angles were converted to radians in Microsoft Excel (v12.3.2 for Mac OSX). X was calculated as vector length times the cosine of the angle in radians, and Y was calculated as vector length times the sine of the angle in radians. All resulting values for X and Y were between −1 and 1. Given that PLS requires positive values, all values were shifted to positive by adding 1.
A published data matrix  was culled in MacClade to include only those genera present in this analysis. In cases where more than one species per genus was present in the phylogenetic data matrix, the type species was retained, if available, or only the first species in the matrix was used. The species in the phylogenetic analysis and this study may not be the same, but there was little intrageneric variation and poor resolution of intrageneric lineage relationships in the phylogenetic analysis . Genus groupings were therefore selected as the primary taxonomic units of comparison in our study. Isotope data were averaged by genus, and to determine if taxon choice factored into the results, the PLS was also run without branch lengths. A tree was built manually in MacClade with identical relationships to the published phylogeny, and branch lengths (number of character changes per branch) were obtained in PAUP* and saved into a tree file; Loricariinae taxa not present in the dataset were added according to relationships in the only published comprehensive phylogeny for Loricariinae  and were given a branch length of one because branch lengths in PLS cannot equal zero. X and Y data were added to the phylogenetic matrix in MacClade as continuous characters.
PLS was performed in Mesquite by opening the character matrix and then opening the trees with and without branch lengths. Ancestral values for X and Y were calculated by tracing character history and exporting the resulting values by node. Angles were determined by subtracting one from each value, finding the angle in radians by taking the arctangent of Y/X, converting the angle to degrees (results are from −90° to 90°), and then placing the angle into the correct quadrant by either keeping the same value or adding 180° or 360° as indicated by positive and negative values of X and Y. For visualization on the phylogeny, angular data were segregated into color-coded 45° segments (Figure 2, Additional file 2: Figure S1).
NKL has conducted research on loricariid biogeography, functional morphology, and trophic ecology for his dissertation and post-doc and is currently working to generate a multi-gene phylogeny for the Ancistrini. KOW has spent 30 years investigating the trophic ecology of tropical river fish communities around the world. JWA completed the first comprehensive, genus-level phylogeny for Loricariidae, and has published extensively on loricariid taxonomy, systematics, and morphology.
Lujan NK, German DP, Winemiller KO: Do wood grazing fishes partition their niche?: Morphological and isotopic evidence for trophic segregation in Neotropical Loricariidae. Functional Ecology. 2011, 25: 1327-1338. 10.1111/j.1365-2435.2011.01883.x.
Lujan NK, Armbruster JW: Morphological and functional diversity of the mandible in suckermouth armored catfishes (Siluriformes, Loricarioidea). J Morphol. 2012, 273: 24-39. 10.1002/jmor.11003.
Armbruster JW: Phylogenetic relationships of the suckermouth armoured catfishes (Loricariidae) with emphasis on the Hypostominae and the Ancistrinae. Zoological Journal of the Linnean Society. 2004, 141: 1-80. 10.1111/j.1096-3642.2004.00109.x.
Schaefer SA, Stewart DJ: Systematics of the Panaque dentex species group (Siluriformes: Loricariidae), wood-eating armored catfishes from tropical South America. Ichthyological Exploration of Freshwaters. 1993, 4: 309-342.
Cebrian J: Patterns in the fate of production in plant communities. Am Nat. 1999, 154: 449-468. 10.1086/303244.
Winemiller KO: Spatial and temporal variation in tropical fish trophic networks. Ecological Monographs. 1990, 60: 331-367. 10.2307/1943061.
Power ME, Sun A, Parker G, Dietrich WE, Wootton JT: Hydraulic food-chain models: An approach to the study of food-web dynamics in large rivers. Bioscience. 1995, 45: 159-167. 10.2307/1312555.
Benedito-Cecilio E, Araujo-Lima CA, Forsberg BR, Bittencourt MM, Martinelli LC: Carbon sources of Amazonian fisheries. Fisheries Management and Ecology. 2000, 7: 305-315.
Layman CA: Winemiller KO, Arrington DA, Jepsen DB: Body size and trophic position in a diverse tropical food web. Ecology. 2005, 86: 2530-2535. 10.1890/04-1098.
Hood JM, Vanni MJ, Flecker AS: Nutrient recycling by two phosphorus rich grazing catfish: the potential for phosphorus-limitation of fish growth. Oecologia. 2005, 146: 247-257. 10.1007/s00442-005-0202-5.
Bowen SH: Detritivory in neotropical fish communities. Environ Biol Fishes. 1983, 9: 137-144. 10.1007/BF00690858.
Hall SR: Stoichiometrically explicit competition between grazers: species replacement, coexistence, and priority effects along resource supply gradients. Am Nat. 2004, 164: 157-172. 10.1086/422201.
Alexandrou MA, Oliveira C, Maillard M, McGill RAR, Newton J, Creer S, Taylor MI: Competition and phylogeny determine community structure in Müllerian co-mimics. Nature. 2011, 469: 84-87. 10.1038/nature09660.
Behmer ST, Joern A: Coexisting generalist herbivores occupy unique nutritional feeding niches. Proc Natl Acad Sci. 2008, 105: 1977-1982. 10.1073/pnas.0711870105.
Atkinson CL, Opsahl SP, Covitch AP, Golladay SW, Conner LM: Stable isotopic signatures, tissue stoichiometry, and nutrient cycling (C and N) of native and invasive freshwater bivalves. J North Am Benthol Soc. 2010, 29: 496-505. 10.1899/09-083.1.
Frost PC, Tank SE, Turner MA, Elser JJ: Elemental composition of littoral invertebrates from oligotrophic and eutrophic Canadian lakes. J North Am Benthol Soc. 2003, 22: 51-62. 10.2307/1467977.
Vanni MJ, Flecker AS, Hood JM, Headworth JL: Stoichiometry of nutrient recycling by vertebrates in a tropical stream: linking species identity and ecosystem processes. Ecol Lett. 2002, 5: 285-293. 10.1046/j.1461-0248.2002.00314.x.
Maltby L: Detritus processing. The Rivers Handbook. Edited by: Calow P, Petts G. 1994, Oxford: Blackwell Scientific Publications, 331-353.
German D, Miles RD: Stable carbon and nitrogen incorporation in blood and fin tissue of the catfish Pterygoplichthys disjunctivus (Siluriformes, Loricariidae). Environ Biol Fishes. 2010, 89: 117-133. 10.1007/s10641-010-9703-0.
Kelly LJ, del Rio CM: The fate of carbon in growing fish: an experimental study of isotopic routing. Physiol Biochem Zool. 2010, 83: 473-480. 10.1086/649628.
Winemiller KO, Akin S, Zeug SC: Production sources and food web structure of a temperate tidal estuary: integration of dietary and stable isotope data. Mar Ecol Prog Ser. 2007, 343: 63-76.
Jepsen DB, Winemiller KO: Structure of tropical river food webs revealed by stable isotope ratios. Oikos. 2002, 96: 46-55. 10.1034/j.1600-0706.2002.960105.x.
Layman CA, Arrington DA, Montaña CG, Post DM: Can stable isotope ratios provide for community-wide measures of trophic structure. Ecology. 2007, 88: 42-48. 10.1890/0012-9658(2007)88[42:CSIRPF]2.0.CO;2.
Schmidt SN, Olden JD, Solomon CT, Vander Zanden MJ: Quantitative approaches to the analysis of stable isotope food web data. Ecology. 2007, 88: 2793-2802. 10.1890/07-0121.1.
Turner TF, Collyer ML, Krabbenhoft TJ: A general hypothesis-testing framework for stable isotope ratios in ecological studies. Ecology. 2010, 91: 2227-2233. 10.1890/09-1454.1.
Forsberg BR, Araujo-Lima CARM, Martinelli LA, Victoria RL, Bonassi JA: Autotrophic carbon sources for fish of the Central Amazon. Ecology. 1993, 74: 643-652. 10.2307/1940793.
Schaefer SA, Lauder GV: Historical transformation of functional design: evolutionary morphology of feeding mechanisms in loricarioid catfishes. Syst Zool. 1986, 35: 489-508. 10.2307/2413111.
Geerinckx T, Adriaens D: The erectile cheek-spine apparatus in the bristlenose catfish Ancistrus (Loricariidae, Siluriformes), and its relation to the formation of a secondary skull roof. Zoology. 2006, 109: 287-299. 10.1016/j.zool.2006.04.001.
Power ME: Habitat quality and the distribution of algae-grazing catfish in a Panamanian stream. J Anim Ecol. 1984, 53: 357-374. 10.2307/4521.
Lujan NK, Armbruster JW: The Guiana Shield. Historical Biogeography of Neotropical Freshwater Fishes. Edited by: Albert J. 2011, University of California Press, 211-224.
Eschmeyer WN, Fricke R: Catalog of Fishes electronic version. 2011, http://research.calacademy.org/research/ichthyology/catalog/fishcatmain.asp,
Castillo MM, Kling GW, Allan JD: Bottom-up controls on bacterial production in tropical lowland rivers. Limnol Oceanogr. 2003, 48: 1466-1475. 10.4319/lo.2003.48.4.1466.
German DP: Inside the guts of wood-eating catfishes: can they digest wood?. J Comp Physiol B. 2009, 179: 1011-1023. 10.1007/s00360-009-0381-1.
German DP, Bittong RA: Digestive enzyme activities and gastrointestinal fermentation in wood-eating catfishes. J Comp Physiol B. 2009, 179: 1025-1042. 10.1007/s00360-009-0383-z.
Marrero C, Winemiller KO: Tube-snouted gymnotiform and mormyriform fishes: convergence of a specialized foraging mode in teleosts. Environ Biol Fishes. 1993, 38: 299-309. 10.1007/BF00007523.
Wilson SK, Bellwood DR, Choat JH, Furnas MJ: Detritus in the epilithic algal matrix and its use by coral reef fishes. Oceanography and Marine Biology: an Annual Review. Edited by: Gibson RN, Atkinson RJA. 2003, New York: Taylor & Francis, 279-309.
Putz R, Junk WJ: Phytoplankton and periphyton. The Central Amazon Floodplain: Ecology of a Pulsing System. Edited by: Junk WJ. 1997, New York: Springer, 207-222.
Hamilton SK, Sippel SJ, Bunn SE: Separation of algae from detritus for stable isotope or ecological stoichiometry studies using density fractionation in colloidal silica. Limnology and Oceanography: Methods. 2005, 3: 149-157.
Budge SM, Springer AM, Iverson SJ, Sheffield G: Fatty acid biomarkers reveal niche separation in an Arctic benthic food web. Mar Ecol Prog Ser. 2007, 336: 305-309.
Arrington DA, Winemiller KO: Preservation effects on stable isotope analysis of fish muscle. Trans Am Fish Soc. 2002, 131: 337-342. 10.1577/1548-8659(2002)131<0337:PEOSIA>2.0.CO;2.
Armbruster JW: The species of the Hypostomus cochliodon group (Siluriformes: Loricariidae). Zootaxa. 2003, 249: 1-60.
Maddison DR, Maddison WP: MacClade 4: Analysis of phylogeny and character evolution. Version 4.08a. 2005, http://macclade.org." More information can be found here on the MacClade homepage: http://macclade.org/macclade.html
Armbruster JW: The genus Peckoltia with the description of two new species and a reanalysis of the phylogeny of the genera of the Hypostominae (Siluriformes: Loricariidae). Zootaxa. 2008, 1822: 1-76.
Rapp Py-Daniel L, Cox Fernandes C: Dimorfismo sexual em Siluriformes e Gymnotiformes (Ostariophysi) da Amazônia. Acta Amazonica. 2005, 35: 91-110.
We gratefully acknowledge D. German, C. Layman, H. López-Fernández, E. Oneal, K. Roach, and anonymous reviewers for comments on previous versions of this manuscript; T. Maddox for conducting mass spectrometric isotope analyses; A. Arrington for early discussions of this concept; D. Taphorn, H. Ortega, and J. Birindelli for assistance with collecting permits; D. Werneke, M. Sabaj Pérez, O. Leon Mata, L. de Souza, D. German, K. Capps, A. Flecker, L. Sousa, and A. Netto Ferreira for assistance with specimen collection and management; and J. Humphries and K. Luckenbill for assistance with CT scans and CT data manipulation. This project represents part of Planetary Biodiversity Inventory: All Catfish Species (Siluriformes; NSF DEB-0315963), NSF grant OISE-1064578 to NKL, and NSF grant DEB-0107751 to JWA; with additional funding from the estate of George and Carolyn Kelso via the International Sportfish Fund.
NKL conceptualized the study and conducted field and laboratory work. NKL, KOW, and JWA wrote the paper. JWA developed and conducted the phylogenetic analyses. All authors read and approved the final manuscript.
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Lujan, N.K., Winemiller, K.O. & Armbruster, J.W. Trophic diversity in the evolution and community assembly of loricariid catfishes. BMC Evol Biol 12, 124 (2012). https://doi.org/10.1186/1471-2148-12-124
- Particulate Organic Carbon
- Trophic Niche
- Trophic Ecology
- Local Assemblage
- Dietary Protein Content