DOI: 10.5061/dryad.jsxksn05r
title: Functional consequences of phenotypic variation between locally adapted populations: swimming performance and ventilation in extremophile fish

description: Natural selection drives the evolution of traits to optimize organismal
 performance, but optimization of one aspect of performance can often
 influence other aspects of performance. Here, we asked how phenotypic
 variation between locally adapted fish populations affects locomotion and
 ventilation, testing for functional trade-offs and trait-performance
 correlations. Specifically, we investigated two populations of livebearing
 fish (Poecilia mexicana) that inhabit distinct habitat types
 (hydrogen-sulfide-rich springs and adjacent nonsulfidic streams). For each
 individual, we quantified different metrics of burst swimming during
 simulated predator attacks, steady swimming, as well as gill ventilation.
 Coinciding with predictions, we documented significant population
 differences in all aspects of performance, with fish from sulfidic
 habitats exhibiting higher steady swimming performance and higher
 ventilation capacity, but slower burst swimming. There was a significant
 functional trade-off between steady and burst swimming, but not between
 different aspects of locomotion and ventilation. While our findings about
 population differences in locomotion performance largely parallel the
 results from previous studies, we provide novel insights about how
 morphological variation might impact ventilation and ultimately oxygen
 acquisition. Overall, our analyses provided insights into the functional
 consequences of previously documented phenotypic variation, which will
 help to disentangle the effects of different sources of selection that may
 coincide along complex environmental gradients.
description: <i>Study organisms and general experimental design</i> Several sulfide springs inhabited by <i>P. mexicana </i>occur in the states of Tabasco and Chiapas, Mexico (Palacios, et al. 2016). For the present study, we collected young adult fish (standard length: 28-38 mm) from a sulfidic (El Azufre I: N 17.442°/W 92.775°) and a nonsulfidic population (Río Tacotalpa: N 17.275°/W 92.462°) near Tapijulapa, Tabasco, and transported them to Kansas State University (KSU), where they were housed in 80-liter tanks and given two months to acclimate to standardized laboratory conditions, irrespective of their habitat of origin. Fish were kept at under nonsulfidic and normoxic conditions, a constant temperature of 25° C, and a 12:12 hr light:dark photoperiod. Fish were fed <i>ad libitum </i>and had access to flake food and frozen brine shrimp twice daily. We chose to acclimate all individuals to one standardized environment, because maintaining stable H<sub>2</sub>S-rich water is difficult in the laboratory. In addition, the toxic effects of H<sub>2</sub>S lead to high mortality of fish from nonsulfidic populations, preventing factorial experimental designs where the performance of fish from different habitats is measured under multiple environmental conditions. Consequently, our experiments only quantify the functional repercussions of traits that vary between sulfidic and nonsulfidic populations, and we cannot capture potential trait-environment interactions that might impact performance of fish in their natural habitats. After acclimation, fish were separated into groups of 3-4 individuals and housed in 40-liter tanks, facilitating the tracking individual fish across different portions of the experiment. For each fish, we quantified three aspects of performance: 1) burst swimming upon a simulated predator attack, 2) steady swimming, and 3) gill ventilation. The order of performance trials was randomized across individuals, and individuals were allowed to recover for at least one week in between trials. Fish were fasted for 24 hours prior to each performance trial to ensure they were in a post-absorptive state (Niimi and Beamish 1974; Kieffer 2000). After the completion of all performance trials, individuals were euthanized using MS-222 (500 mg/l buffered to pH 7.5 with sodium bicarbonate) for morphological analyses. A total of <i>N</i>=71 fish were tested.   <i>Burst swimming performance</i> We quantified burst swimming performance of fish during their reflexive escape response (c-start) to simulated predator attacks (Weihs 1973; Howland 1974; Eaton, et al. 1977; Harper and Blake 1990; Domenici and Blake 1997). Fish from high-predation environments have previously been documented to perform faster at c-starts than fish from low-predation environments (Walker 1997; Langerhans, et al. 2004; Langerhans, et al. 2007), and several studies have linked burst swimming performance with survival in the presence of predators (e.g., Ingley & Johnson, 2016; Walker, Ghalambor, Griset, Mckenny, & Reznick, 2005).  Methods for the quantification of fast-start responses were adapted from previous studies (Langerhans, et al. 2004; Ingley, et al. 2016). For each trial, we placed a fish into a clear acclimation cylinder (5.5 cm in diameter) within a larger test arena (circular tank with a 40-cm diameter). To minimize vertical displacement and approximate two-dimensional escape responses, the water level was maintained at a depth of ~3 cm. After a 10-min acclimation period, the cylinder was removed, and we struck the arena with a probe (6 mm in diameter and 90 cm long) within ~1 body length of the fish’s caudal region to evoke an escape response. After the first trial, fish were placed back into the cylinder, given the same acclimation period, and tested twice more with the same procedures, yielding three burst swimming performance trials per fish. Each trial was filmed from above with a Sony NXCAM NEX-FS700 high-speed camera (Sony Corporation, Tokyo, Japan) at 120 frames per second (fps).  Videos were analyzed frame by frame using the DLTdv6 tracking software (Hedrick 2008) in MATLAB 2016a (Mathworks Inc., Natick, MA, USA) to quantify four metrics of burst swimming performance (Walker, et al. 2005) following methods established by Langerhans (2009): (1) total distance traveled (d<sub>net</sub> [cm]) is the net distance a fish traveled within 1/12 of a second after bending into the c-shape; (2) rotational velocity (w<sub>S</sub> [°/s]) is the average rotational velocity of the head from the moment the fish begins bending into the c-shape until it has completely bent (rotational angle of bend divided by duration); (3) maximum velocity (v<sub>max</sub> [cm/s]) is the greatest change in distance between two consecutive frames (1/120 of a second); (4) maximum acceleration (a<sub>max</sub> [cm/s<sup>2</sup>]) is the greatest positive change in velocity between two consecutive frames.For each individual, we calculated the average of each metric across the three trials.   <i>Steady swimming performance</i> We quantified metrics for steady swimming performance, an energy-efficient mode of locomotion that fish use during place-holding against water flow, foraging, and mate searching (Domenici 2003b; Blake 2004; Langerhans 2008). To quantify steady swimming performance, we measured the critical swimming speed as well as swimming kinematics at different swimming speeds for each individual. Critical swimming speed is defined as the maximum speed at which a fish can maintain steady swimming (Plaut 2001; Domenici 2003a; Blake 2004) and can be quantified by incrementally increasing the swimming speed until an individual fatigues (Brett 1964). Critical swimming speed can then be calculated as <i>U</i><sub>crit</sub> =<i> U</i><sub>f</sub><i> + U</i><sub>s</sub> × (<i>t</i><sub>f</sub>/<i>t</i><sub>s</sub>), where <i>U</i><sub>f</sub> is the highest flow velocity maintained for a full time-interval, <i>U</i><sub>s</sub> is the velocity increment, <i>t</i><sub>f</sub> is the time to fatigue at the last flow speed, and <i>t</i><sub>s</sub> is the time interval at which increases in speed occur (Brett 1964). To quantify <i>U</i><sub>crit</sub>, individual fish were placed in a 5-L swim tunnel (Loligo Systems ApS, Viborg, Denmark), in which they were exposed to laminar flow with adjustable speed (Ellerby and Herskin 2013){Ellerby, 2013 #83;Ellerby, 2013 #83}. Trials started with a 20-min acclimation period, including 10 min without flow and 10 min at a flow speed of one body length per second (BLs<sup>-1</sup>). After acclimation, fish were incrementally exposed to higher flow speeds (<i>U</i><sub>s</sub> = 1 BLs<sup>-1</sup>) every 10 min (<i>t</i><sub>s</sub> = 600 s). Acclimation times and speed increments were adopted from previous studies (Hammill, et al. 2004; Oufiero and Garland 2009; Sfakianakis, et al. 2011). Trials were immediately terminated once a fish reached fatigue. During each steady swimming trial, fish were filmed at 120 (fps) using a high-speed camera twice during each interval (once immediately after the speed was increased and a second time halfway into a time interval). Four videos were selected at speeds ~25%, 50%, 75%, and 100% of each individual fish’s <i>U</i><sub>crit</sub> (Oufiero and Garland 2009). At each speed, we quantified five kinematic variables relevant for the hydrodynamics of steady swimming (see Langerhans, 2009; McHenry, Pell, & Long, 1995): (1) tail-beat frequency (<i>f</i> [Hz]) was measured as the inverse average period of ten complete tail-beat cycles; (2) rostral amplitude (<i>R</i> [mm]) was measured as half the distance between right and left excursions of the anterior tip of the rostrum; (3) tail-beat amplitude (<i>H</i> [mm]) was measured as half the distance between right and left excursions of the caudal fin; (4) propulsive wavelength (<i>λ</i> [mm]) was quantified as double the posterior half-wavelength; and (5) propulsive wave speed (<i>c</i>[mm/s]) was calculated by multiplying the propulsive wavelength with the tail-beat frequency (<i>c</i>= <i>λ</i> *<i>f</i>). For <i>R</i>, <i>H</i>, and <i>λ</i>, measurements were taken by averaging the values of each across three complete tail beats.   <i>Gill Ventilation Capacity</i> Gill ventilation in teleost fishes has been described as a two-pump system, in which water is taken through the mouth into the buccal cavity, pumped into opercular cavity, and out through the opercular openings, resulting in a unidirectional flow across the respiratory surfaces (Hughes 1958). The rate at which water is pumped over the gills is consequently limited by the capacity of the first pump (i.e., the frequency of ventilation and the buccal volume). We quantified these variables for each individual to estimate the maximum gill ventilation capacity. To measure the maximum ventilation frequency, fish were driven to maximum aerobic performance using chase trials (see Brennan, et al. 2016). Fish were placed in a circular arena (28 cm in diameter), given a 10-min acclimation period, and then chased along the edge of the arena for 6 min. After chasing, individuals were immediately transferred into a photo tank (18´10.5´10 cm) with aerated water and filmed at 60 fps. Fish were recorded eight times for 3 s each, 15 s apart. We counted the number of respiratory cycles for each 3-second interval (in pumps s<sup>-1</sup>), retaining the highest value for subsequent analyses. To estimate the volume of the buccal cavity for each fish, we performed a sagittal cut from the center of the body toward the mouth and a second cut in a planar fashion just behind the opercula, yielding in two separate halves of the head. Digital images were than taken of each sagittal plane using a Canon Rebel T5i camera (Canon USA Inc., Lake Successes, NY, USA), allowing for the measurement of the length of the buccal cavity. Additional images were taken of the planar planes at the anterior and posterior edge of the buccal cavity, allowing for the measurement of the corresponding radii of the buccal cavity. Measurements on the two halves were averaged. To approximate the buccal volume, we treated the shape of the cavity as a circular truncated cone, for which the volume can be calculated as <i>V</i><sub>b</sub>=(1/3)*<i>h</i>*π*(<i>r</i><sub>1</sub><sup>2</sup>+<i>r</i><sub>1</sub><i>r</i><sub>2</sub>+<i>r</i><sub>2</sub><sup>2</sup>), where <i>h</i> is the length of the buccal cavity, and <i>r</i><sub>1</sub> and <i>r</i><sub>2</sub> are the radii of the anterior and posterior ends, respectively.   <i>Body shape</i> To relate variation in performance to variation in morphology, we quantified the body shape based on lateral photographs of each individual using geometric morphometrics. We digitized 11 landmarks using the software program tpsDig version 2.10 (Rohlf 2006): (1) tip of the upper jaw; (2) anterior and (3) posterior insertions of the dorsal fin; the (4) dorsal and (5) ventral insertions of the caudal fin; (6) the anterior junction of the anal fin; (7) the bottom of the head where the operculum breaks away from the body outlin; (8) the dorsal endpoint of the opercular bone; (9) the dorsal and (10) ventral insertions of the pectoral fin; and (11) the center of the orbit.   <b>References</b> Blake RW. 2004. Fish functional design and swimming performance. Journal of Fish Biology 65:1193-1222. Brennan RS, Hwang R, Tse M, Fangue NA, Whitehead A. 2016. Local adaptation to osmotic environment in killifish, Fundulus heteroclitus, is supported by divergence in swimming performance but not by differences in excess post-exercise oxygen consumption or aerobic scope. Comparative Biochemistry and Physiology A - Molecular and Integrative Physiology 196:11-19. 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