Research Article |
Corresponding author: Francisco Alexandre Costa Sampaio ( francisco.sampaio@ifbaiano.edu.br ) Academic editor: Oana Teodora Moldovan
© 2020 Francisco Alexandre Costa Sampaio, Marina Silva Rufino, Paulo Santos Pompeu, Hersília de Andrade е Santos, Rodrigo Lopes Ferreira.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Sampaio FAC, Rufino MS, Pompeu PS, Santos HA, Ferreira RL (2020) Hydraulic flow resistance of epigean and hypogean fish of the family Trichomycteridae (Ostariophysi, Siluriformes). Subterranean Biology 35: 97-110. https://doi.org/10.3897/subtbiol.35.55064
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Critical swimming speeds of four trichomycterid fish species from epigean and hypogean environments were analyzed and compared: Trichomycterus itacarambiensis and Ituglanis passensis, both troglobitic from underground rivers; Trichomycterus brasiliensis, from epigean rivers; and Ituglanis sp., an undescribed troglophilic species from an underground stream. Swimming tests were conducted with a non-volitional apparatus in which fish swim against a progressive incremental water velocity until they longer resist the flow. Total length was significantly related to critical speed for only T. itacarambiensis. The critical speed obtained by each species, in decreasing order, with values in lengths per second (lengths/s), were: I. passensis (3.61), T. itacarambiensis (3.49), T. brasiliensis (3.11) and Ituglanis sp. (1.89). Swimming performance differed between the congeners T. itacarambiensis and T. brasiliensis, but did not differed between I. passensis and Ituglanis sp. The greater speed for the troglobitic species compared to that of the troglophilic and epigean species is probably related to seasonal flooding pulses that can be extremely severe in caves. Furthermore, during the tests, fish were observed using their mouth and/or barbels to fasten themselves to the substrate to avoid high flows.
Caves, critical speed, subterranean rivers, swimming performance, troglobitic fishes
Fish belonging to the order Siluriformes Cuvier, 1817, usually possess broad geographical distributions, with different species occurring in both freshwater, marine and brackish environments (
Trichomycterus Valenciennes, 1833, is one of the richest genera within the family Trichomycteridae, with more than 240 described species (
The genus Ituglanis Costa & Bockmann, 1993, also of the family Trichomycteridae, is considered the sister group of Trichomycterus (Costa & Bockmann, 1993). Species of the former are distributed throughout South America in epigean and hypogean watercourses (
Many catfish species, but especially trichomycterids, are mainly found in basin-level streams and vadose tributaries, sometimes also occurring in subterranean aquatic environments, as previously mentioned. However, subterranean environments present particular hydraulic conditions with fast changes in water flow, which varies sharply according to the intensity and frequency of rainfall (
Studies of swimming capacity in Neotropical fish species are rare (
Four catfish species of the family Trichomycteridae that occur in Brazil were analyzed: two troglobitic, one troglophilic and one epigean. Twenty-four individuals (N=24) of the species Trichomycterus brasiliensis Lütken, 1874, which occurs in superficial streams, were caught with a trawl in the city of Luminárias (21°30'52"S, 44°52'29"W), in the state of Minas Gerais (MG). Seventeen individuals (N=17) of the troglophilic species Ituglanis sp., which occurs in both superficial and subterranean streams, were collected inside the cave Loca d’Água (20°25'23"S, 45°41'32"W) in the city of Pains, MG. Ten individuals (N=10) of Trichomycterus itacarambiensis Trajano & de Pinna, 1996, a troglobitic fish which lives only in subterranean environments, were collected in the cave Olhos d’Água (15°07'00"S, 44°10'00"W), in the city of Itacarambi, MG. Ten individuals (N=10) of the troglobitic Ituglanis passensis Fernández & Bichuette, 2002, were collected inside the cave Passa Três (13°45'00"S, 46°22'00"W), which is located in the São Domingos karst area of the state of Goiás. Cave fish were collected using PVC traps containing chicken liver as bait, from May to July 2008. Authorization for collecting fish was granted by Brazilian Institute of the Environment and Renewable Natural Resources (IBAMA; numbers 13295-1 and 10327-1).
Collected specimens were sedated and transported in a plastic box with aeration for approximately seven hours, after which they were transferred to climate-controlled aquariums at the laboratory. Testing started 48 hours after the arrival of the fish at the laboratory. Adult individuals of different size class were selected and tested in order to analyze fish swimming behavior and critical speed for as wide a size range of fish as possible (Fig.
After testing, the specimens were sedated with eugenol, measured and kept in the aquariums. Individuals that died from natural causes were fixed in formalin and preserved in 70% ethanol. Voucher specimens were properly deposited in the fish collection of Coleção Ictiológica da Universidade Federal de Lavras, Minas Gerais State, Brazil (
The experimental apparatus (Fig.
Experimental apparatus for testing fish swimming capacity and resistance to flow: A centrifugal pump which creates the water flow B central testing section C connection for fish entrance to and removal from the central testing section D screens to keep fish in the central testing section E flow rate gauge F frequency converter which was used to change pump rotation and, consequently, the flow velocity in the central testing section G water tank and H water cooler.
During the first 5 minutes (time interval), the mean water velocity in the testing section was maintained at 0.05 m/s and the fish was inserted. The flow velocity was then increased incrementally by 0.05 m/s at a time intervals of 5 minutes. The test finished when the fish experienced complete fatigue, which was assumed with the absence of swimming movements and confinement at the downstream screen. All swimming behaviors were monitored and noted during the tests.
Temperature and dissolved oxygen of the water were monitored once before, during and after the tests (Fig.
Absolute critical velocity for each specimen was calculated by the Brett equation (1):
(1)
where Vmax is the maximum velocity obtained by the fish specimen (m/s), tmax is the maximum swimming time before complete fatigue (s), Δt is the time interval (300 s) and ∆U is the velocity increment (0.05 m/s).
After this calculation, the swimming velocity must be corrected (Vcorrected) due to fish obstruction of the effective area for water movement. Equations 2 and 3, which were proposed by
(2)
(3)
where Vmeasured is specimen critical velocity (m/s), K3 is a coefficient that depends on the ratio between fish width (e in cm) and fish total length (L in cm) and may be obtained following
Linear regression provided the relationships between critical speed and other variables for each species: fish total length, fish standard length, water temperature and dissolved oxygen. Factorial Analyses of Variance (ANOVA) compared critical speed among the studied species, for which relative critical speed (body length/s) was utilized (i.e., critical velocity corrected by fish standard length). This speed relativization allows comparisons of swimming speed to be made between different specimens and species and is based on the influence of fish body size on swimming capability. Relative critical speed was also compared for pairs of species of the same genus using the Levene test. The significance level was 0.05 (p-value) for all tests and the statistical analyses were conducted using Statistica 7.0.
Tests starting with a water velocity of 0.05 m/s and with progressive increments of 0.05 m/s every 5 minutes revealed that at velocities under 0.5 m/s all fish remained active, swimming normally and sometimes remaining still over the acrylic surface (Fig.
T. brasiliensis | T. itacarambiensis | Ituglanis sp | I. passensis | |
---|---|---|---|---|
Species habit | Epigean | Troglobitic | Troglophilic | Troglobitic |
Number of tested individuals | 24 | 10 | 17 | 8 |
Attaching behavior (number of individuals) | 3 | 0 | 3 | 2 |
Maximum water velocity endured by attaching (length/s) | 9.94 | – | 4.62 | 9.20 |
No significant relationships (p > 0.05) were observed between critical speed and water temperature and dissolved oxygen for any of the tested species. Only for T. itacarambiensis was critical speed related to total and standard lengths, the latter with greater explanatory power (Fig.
Despite not being significantly related to critical speed, temperature and dissolved oxygen values were maintained as close as possible to the respective environments of origin of the fish during the tests (Table
Species | Temperature (°C) | Dissolved oxygen (mg/L) | ||||||
Mean | Min. | Max. | SD | Mean | Min. | Max. | SD | |
T. itacarambiensis | 18.4 | 18.0 | 19.3 | 0.44 | 8.4 | 8.2 | 8.6 | 0.15 |
T. brasiliensis | 23.2 | 22.0 | 24.0 | 0.97 | 8.3 | 8.2 | 8.6 | 0.16 |
I. passensis | 19.7 | 19.0 | 21.3 | 0.93 | 8.2 | – | – | – |
Ituglanis sp | 19.7 | 18.5 | 20.6 | 0.70 | 8.2 | – | – | – |
Absolute critical speed differed among the tested species (F = 7.72; p <0.01), with Ituglanis sp. having the lowest swimming capacity (Table
Relative and absolute critical speeds for the tested species considering specimens that swam in at least one time interval.
Species | Relative Critical Speed (Lenght/s) | Absolute Critical Speed (m/s) | ||||||
Mean | Min. | Max. | SD | Mean | Min. | Max. | SD | |
T. itacarambiensis | 3.496 | 2.208 | 5.213 | 0.980 | 0.240 | 0.211 | 0.288 | 0.023 |
T. brasiliensis | 3.115 | 1.872 | 5.486 | 0.947 | 0.228 | 0.132 | 0.324 | 0.045 |
I. passensis | 3.615 | 2.583 | 5.532 | 1.275 | 0.233 | 0.176 | 0.343 | 0.071 |
Ituglanis sp | 1.896 | 0.739 | 3.387 | 0.838 | 0.137 | 0.063 | 0.236 | 0.056 |
When comparing pairs of congeneric species, Ituglanis sp. had lower speeds (p <0.01) and smaller variance in its relative speed (F = 2.87; p = 0.002) than did Ituglanis passensis. For the species of Trichomycterus, T. itacarambiensis had higher absolute speeds and lower variation (F = 4.65; p = 0.03) than did T. brasiliensis (Figs
The behavioral capability to resist flow without active swimming, as observed in this experiment for three of the four evaluated species, can be considered an important pre-adaptation to subterranean environments. This ability has already been described for a number of groups of fish, including Cryptotora thamicola (Kottelat, 1988), a cave species that can climb waterfalls in its habitat through a distinct type of locomotion and a modified pelvic girdle (
The ability to adhere to the substrate, as observed for three of the studied species, may represent a pre-adaptation to the cave environment. Some similar behaviors that also support this idea have been verified in troglobitic fish that dig and bury themselves in the substrate (
Trichomycterus itacarambiensis was the only species that did not resist flow using the mouth or the operculum in the experiments of the present study. Even so,
Trichomycterus itacarambiensis was the only species to show a significant relationship between critical speed and total and standard length. Total length is considered a variable of strong explanatory power for the swimming capacity of fish (
On the other hand, the higher speeds observed for the troglobitic species, in comparison to their epigean relatives, may be directly related to selection exercised by the hydraulic cave environment where they live. It is important to note, however, that underground habitats do not always exercise the same type of hydraulic selection. As an example, the troglobitic species S. typhlops presented a lower critical swimming speed than the other related epigean species tested, Piabina argentea Reinhardt, 1867, Piabarchus stramineus (Eigenmann, 1908) and Hemigrammus marginatus Ellis, 1911 (
In addition to extreme events arising from large flow pulses (
Selection favoring specimens with higher swimming capability would also explain the less variation in this ability observed in cave species. Such a pattern would fit the definition of directional selection, when fitness consistently increases (or decreases) with the value of the characteristic, reducing the variation in a population (
In contrast, less variation in the swimming capability of cave species could also be explained by stabilizing selection, in which the average values of a give trait in the population (in this case, swimming capability) have greater aptitudes than the extremes, which are negatively selected (
The type of swimming performed by a species has direct implications on its habitat use (
We are grateful to: FAPEMIG – Minas Gerais State Agency for Research and Development, financial support for the project; CAPES – Coordination of Superior Level Staff Improvement, for financial support of part of the study – Finance Code 001; FACS for the master’s scholarship granted; CNPq – National Council for Scientific and Technological Development, for the productivity scholarship provided to RLF (308334/2018-3) and to PSP (303548/2017-7); ancient IBAMA – Brazilian Institute of the Environment and Renewable Natural Resources, for the licenses granted (13295-1, 10327-1); Regina and Arnor, the managers of the Terra Ronca National Park – Goiás State; Míriam A. de Castro for helping in the experiments; to everyone who collaborated in the field and to reviewers for comments on the manuscript.