bioRxiv preprint doi: https://doi.org/10.1101/2021.04.27.441509; this version posted April 29, 2021. The copyright holder for this preprint (which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
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4 Antarctic Teleosts With and Without Haemoglobin Behaviourally Mitigate
5 Deleterious Effects of Acute Environmental Warming
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9 Iskander I. Ismailov1,*, Jordan B. Scharping2, 3, Iraida E. Andreeva1, Michael J. Friedlander1*
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11 1Fralin Biomedical Research Institute at Virginia Tech Carilion, Roanoke, VA
12 2Virginia Tech Carilion School of Medicine, Roanoke, VA
13 3Current address: Northwestern Memorial Hospital, Chicago, IL
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16 *
17 *Co-corresponding authors:
18 Iskander I. Ismailov, Fralin Biomedical Research Institute at VTC, 2 Riverside Cir, Roanoke, VA 19 24016. e-mail: [email protected]; Tel.: +1 (205) 746-5395.
20 Michael J. Friedlander, Fralin Biomedical Research Institute at VTC, 2 Riverside Cir, Roanoke, 21 VA 24016. e-mail: [email protected]; Tel: +1 (540) 526-2013
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23 Word count: 7694
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bioRxiv preprint doi: https://doi.org/10.1101/2021.04.27.441509; this version posted April 29, 2021. The copyright holder for this preprint (which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
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27 Recent studies forecast that many ectothermic animals, especially aquatic stenotherms, may
28 not be able to thrive or even survive predicted climate change. These projections, however,
29 generally do not call much attention to the role of behaviour, an essential thermoregulatory
30 mechanism of many ectotherms. Here we characterize species-specific locomotor and
31 respiratory responses to acute ambient warming in two highly stenothermic Antarctic
32 Notothenioid fishes, one of which (Chaenocephalus aceratus) lacks haemoglobin and appears
33 to be less tolerant to thermal stress as compared to the other (Notothenia coriiceps), which
34 expresses haemoglobin. At the onset of ambient warming, both species perform distinct
35 locomotor manoeuvres that appear to include avoidance reactions. In response to unavoidable
36 progressive hyperthermia, fishes demonstrate a range of species-specific manoeuvres, all of
37 which appear to provide some mitigation of the deleterious effects of obligatory
38 thermoconformation and to compensate for increasing metabolic demand by enhancing the
39 efficacy of branchial respiration. As temperature continues to rise, Chaenocephalus aceratus
40 supplements these behaviours with intensive pectoral fin fanning which may facilitate cutaneous
41 respiration through its scaleless integument, and Notothenia coriiceps manifests respiratory-
42 locomotor coupling during repetitive startle-like manoeuvres which may further augment gill
43 ventilation. The latter behaviours, found only in Notothenia coriiceps, have highly stereotyped
44 appearance resembling Fixed Action Pattern sequences. Altogether, this behavioural flexibility
45 could contribute to the reduction of the detrimental effects of acute thermal stress within a
46 limited thermal range. In an ecologically relevant setting, this may enable efficient
47 thermoregulation of fishes by habitat selection, thus facilitating their resilience in persistent
48 environmental change.
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bioRxiv preprint doi: https://doi.org/10.1101/2021.04.27.441509; this version posted April 29, 2021. The copyright holder for this preprint (which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission.
49 Keywords: Antarctic Notothenioids, behavioural thermoregulation, fanning, fixed action pattern,
50 lateralization, respiratory behaviour, respiratory-locomotor coupling, startle-like behaviour
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51 There is increasing concern about the fitness of life forms on Earth in the face of rising
52 environmental temperatures (Thomas et al., 2004; Pacifici et al., 2015). As part of that
53 awareness, the potential vulnerability of high latitude marine ecosystems, such as the Antarctic
54 shelf, has drawn particular attention (Clarke et al., 2012; Constable et al., 2014), as they are
55 likely facing some of the most rapid environmental changes on the planet (Vaughan et al., 2003;
56 Cheng et al., 2019; see, however, Turner et al., 2016). Furthermore, isolated from the rest of the
57 world by the Antarctic Circumpolar Current, inhabitants of this ecosystem have evolved under
58 extremely cold conditions which remained thermally stable for millions of years (Barker and
59 Thomas, 2004). In effect, they are thought to have specialized for such a milieu by developing
60 stenothermy, i.e., traded-off the ability to adjust to even small variations in temperature
61 (Wohlschlag, 1964; Somero and DeVries, 1967).
62 Based on the results of experimental studies in a variety of aquatic organisms subjected to
63 acute warming, one perspective on the physiological mechanisms that limit adaptive capacity
64 and thermal tolerance of ectotherms is that cardiac collapse is ultimately responsible for
65 organismal failure at extreme temperatures (see Eliason and Anttila, 2017 for a Review).
66 Deriving rationale from the relationship between thermal tolerance of fishes to their aerobic
67 metabolic rates (Fry and Hart, 1948), these studies provide the basis for an ‘oxygen- and
68 capacity-limited thermal tolerance’ theory (Pörtner, 2001) and attribute this collapse to a
69 mismatch between the aerobic demand of the heart during thermally induced tachycardia and
70 maximal ability to supply oxygen to the heart. Presented initially as an integrative concept
71 comparing the effects of temperature on different organisms, this theory has lately generated
72 discussion (Pörtner et al, 2017; Jutfelt et al., 2018) as a possible overreach attempting to merge
73 environmentally meaningful thermal limits observed in natural habitats with acute sub-lethal
74 warming experiments at miniscule timescales having little ecological relevance. Furthermore,
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75 experimental studies in instrumented, often sedated or restrained animals, or in perfused in vitro
76 and in situ preparations, generally do not encompass a critical thermoregulatory mechanism of
77 ectotherms – behaviour (Crawshaw, 1979).
78 In this study, we examine behavioural responses elicited by ambient warming in two highly
79 stenothermal Antarctic teleosts, Notothenia coriiceps (N. coriiceps, Richardson 1844) and
80 Chaenocephalus aceratus (C. aceratus, Lönnberg 1906), swimming unrestricted in a tank.
81 These fishes belong to the related families Nototheniidae and Channichthyidae, respectively,
82 but differ in that the blood of C. aceratus (also called icefish) is devoid of the oxygen transport
83 protein haemoglobin (Ruud, 1954; Cocca et al., 1995). Consequently, haemoglobinless (Hb-)
84 icefishes supply tissues with oxygen dissolved directly in plasma, with an estimated oxygen-
85 carrying capacity 90% lower than the blood of haemoglobin expressing (Hb+) Antarctic fishes
86 (Holeton, 1970). Large volumes of plasma, big hearts and elaborate vasculature (Hemmingsen,
87 1991) are thought to offset the Hb- state in icefishes, affording their successful habitation in the
88 oxygen-rich Southern Ocean. Yet, compared to their Hb+ relatives, icefishes appear to be less
89 tolerant to acute warming (Beers and Sidell, 2011), putatively due to inferior capacity to adjust
90 cardiac performance at elevated temperatures (O'Brien et al.,2018; see, however, Joyce et al.,
91 2018a). Hence, icefishes have been predicted to be particularly vulnerable to expected global
92 climate change, unless behavioural thermoregulation and/or other physiological plasticity
93 mechanisms alleviate (Huey, et al., 2012) the effects of this detriment.
94 Otherwise, while being considered extremely stenothermal, negatively buoyant bottom dwellers
95 N. coriiceps and C. aceratus are both in fact eurybathic (Eastman, 2017). That is, occasionally
96 found at depths as far down as 500 and 700 metres, respectively, both fishes prefer bathymetric
97 ranges closer to the surface. Namely, N. coriiceps are most commonly found at depths less than
98 100 m, while C. aceratus are typically observed at depths between 100 and 300 m (Hureau,
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99 1985), conceivably both performing frequent routine migrations in the water column. In all
100 locations inhabited by both fishes from as far North as South Georgia and Bouvetøya islands
101 (both at ~54°S) to the Antarctic Peninsula (~65.5°S) (Hureau, 1985), on the other hand, these
102 depths correspond to a prominent thermo- and oxycline (most significant between 50 and 300
103 m, Fig. S1), encompassing a range of temperatures from -1.8°C to +2°C and a dissolved
-1 -1 104 oxygen (DO2) gradient from ~10 mg·L to ~6 mg·L . Then, the fishes must possess certain
105 adaptive capacities that allow them to function equally well in such diverse environments.
106 Behavioural strategies of the Hb+ and Hb- animals responding to ambient warming, however,
107 may be different. Testing this possibility constituted the main goal of this study.
108 We report that both Hb+ and Hb- Antarctic fishes respond to acute ambient warming with an
109 extensive repertoire of behaviours. Restricted in the ability to perform essential
110 thermoregulatory behaviour such as habitat selection in the uniformly heated tank, fishes
111 respond to progressive hyperthermia with an elaborate range of manoeuvres - relative
112 quiescence, startle-like behaviours, aquatic surface respiration, pectoral fin fanning and pectoral
113 fin splay, accompanied with continuous changes in ventilation. While manifestations of these
114 behaviours are species-specific in terms of intensity, duration, thermal dependence and
115 stereotypy, most of them are observed in both fishes. To compensate for increasing respiratory
116 demand at the temperatures above +8°C, both fishes enhance the efficacy of their respiratory
117 pumps. In addition, sedentary Hb- fish supplement increased ventilatory effort with intense
118 fanning which may facilitate cutaneous respiration, whereas more agile Hb+ fish augment it with
119 respiratory-locomotor coupling during repetitive startle-like manoeuvres. Altogether, these
120 behavioural responses appear to constitute complementary adaptive actions to physiologically
121 mitigate deleterious effects of obligatory thermoconformation, resulting in concerted optimization
122 of multiple vital functions within a limited thermal range.
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123 MATERIALS AND METHODS
124 Animals
125 Animals were collected during the austral fall of 2015 (April-June) off the Southwestern shore of
126 Low Island (63°30 S, 62°42 W) and of Brabant Island in Dallmann Bay near Astrolabe Needle
127 (64°08 S, 62°40 W). Otter trawls were used to capture both C. aceratus and N. coriiceps, and
128 baited benthic traps - for N. coriiceps only, all deployed from the Antarctic Research and Supply
129 Vessel Laurence M. Gould (LMG). On board of the LMG, captured animals were held
130 segregated by the species up to 4 days in insulated 900 litre tanks (XacticsTM, ON, Canada)
131 supplied with running ambient ocean water and superfluous aeration at a rate of 17 litres per
132 minute provided by two submersed glass-bonded silica air diffusers (Sweetwater® model AS5L,
133 Pentair Aquatic Eco-Systems, FL, USA) and two diaphragm air pumps (24 litres per minute at 1
134 psi output, Sweetwater® model SL24, Pentair Aquatic Eco-Systems, FL, USA) per tank. After
135 transfer to aquaria at the United States Antarctic Program research station, Palmer Station,
136 fishes were kept segregated by the species in 9,000 litre tanks flowing fresh sand-filtered ocean
137 water pumped from the Arthur Harbour at ambient temperature (-1.7°C to +1°C) for a minimum
138 period of 72 h and up to 3 weeks prior to experiments. N. coriiceps were fed fish muscle blocks
139 once every 2-3 days. Icefish do not feed in captivity (O’Brien et al., 2018), so these animals
140 were used within two weeks of capture. All animal procedures were approved by the University
141 of Alaska, Fairbanks Institutional Animal Care Committee (570217-9).
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143 Temperature ramp experiments
144 Behavioural experiments were performed in a custom-built 500-litre (93 cm (W) x 93 cm (L) x 74
145 cm (H)) flow-through experimental acrylic tank placed in a climate controlled room (with air
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146 temperature maintained between +2 °C and +4°C) and filled with 300 litres of seawater. All
147 surfaces of the tank were additionally covered with 3.175 mm thick transparent red (#2423)
148 acrylic (Professional Plastics, Inc., CA, USA). The rationale for the latter was based on the
149 finding that Notothenioids lack long-wave sensitive opsin gene (Pointer et al., 2005). Therefore,
150 used photic conditions mimic light environment corresponding to the austral mid-winter
151 darkness in the natural habitat of the fishes, visually shield them from the experimenters, and
152 should help to minimize stress.
153 Before the experiment, each specimen was allowed to acclimate overnight in the experimental
154 tank continuously flowing with fresh ocean water (at a rate of 11-15 litres per minute) pumped
155 from the Arthur Harbour at ambient temperature. This ensured relative consistency of thermal
156 environment of fishes from capture to the beginning of the experiment. Baseline behaviours
157 were recorded during this period (for at least 60 minutes just prior to warming ramp). Warming
158 rate of ~3.2°C per hour was achieved by re-circulating tank water through the coil of a custom-
159 made glass heat exchanger with a jacket plumbed to a heating bath-pump (AD28R-30, VWR,
160 PA, USA) running in an external closed loop mode. During the temperature ramp, before
161 entering the heat exchanger, re-circulated water was aerated at a rate of 17 litres per minute
162 using two submersed glass-bonded silica air diffusers (Sweetwater® model AS5L, Pentair
163 Aquatic Eco-Systems, FL, USA) and a diaphragm air pump (24 litres per minute at 1 psi output,
164 Sweetwater® model SL24, Pentair Aquatic Eco-Systems, FL, USA).
165 Digital video images were acquired with Ethovision XT10 tracking software (Noldus Information
166 Technologies, Inc., Netherlands) at a standard frame rate of 30 Hz using a Basler acA 1300-
167 60gm area scan GigE camera (Basler AG, Germany) equipped with a Computar H2Z0414C-MP
168 CCTV lens (CBC Group, NC, USA). The tank contained no gravel or any other substrate, and
169 imaging was performed in a transparency mode (ventral view), in a 34″x34″ acrylic mirror
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170 (Professional Plastics, Inc., CA, USA) placed at a shallow angle (to minimize distortions) 75 cm
171 below the tank. Illumination was achieved with four 12″x12″ heat- and flicker-free (200W HMI
172 light output) LED flood light panels (model 1x1LS Litepanels, Vitec Group, UK) positioned 50 cm
173 above the tank and waterproofed by lamination from both sides 36% transmission value
174 diffusion filter (# 216, LEE Filters, UK) placed directly over the tank. Water temperature and DO2
175 were recorded synchronously using an Orion Versa Star meter and DO2 probe (Thermo
176 Scientific, MA, USA). Warming and video recordings continued until loss of equilibrium (LOE)
177 was observed. All experiments were terminal, and each animal was used in a single behavioural
178 experiment without repetition.
179
180 Analyses of locomotor activity
181 Locomotion was analysed post hoc in video recordings acquired in the field using an automated
182 tracking algorithm of EthoVision XT software. Instantaneous velocities (expressed in body
183 lengths per second, BL·s-1) were calculated by the program from instantaneous (i.e., measured
184 between every two consecutive frames taken 33 ms apart) displacement of the centre of the
185 mass of the fish (determined using a proprietary algorithm of the EthoVision software). The
186 average body lengths were 36.91 ± 1.26 cm and 47.36 ± 3.22 cm, for five N. coriiceps and five
187 C. aceratus, respectively (mean ± SEM). Elongation ratios of fishes used in our experiments
188 were determined as the ratio of length over width (Ward and Azizi, 2004), and constituted 8.38 ±
189 0.24 (mean ± SEM; n = 5) for C. aceratus and 4.73 ± 0.11 (mean ± SEM; n = 5) for N. coriiceps.
190
191 Analyses of respiratory behaviours
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192 Opercular movements were analysed post hoc by manual frame-by-frame measurements of fish
193 head width in Adobe Premiere Pro v.5.5.2 (Adobe Inc., CA, USA) projecting field video
194 recordings on the screen of a Dell U2410 monitor (1920 x 1200 resolution) at 3.2x
195 magnification. All metrics were determined unremitted throughout entire experiment, except the
196 moments when high linear or angular velocity of fish movement precluded reliable
197 measurements. Ventilation frequencies were determined by tallying of opercular movement
198 cycles per minute, and compared for consistency with records of counts taken at 10-15 minute
199 time intervals during actual field experiments at Palmer Station. Opercula opening amplitude
200 (OA), a direct proxy metric of ventilatory stroke volume, was measured as the difference in width
201 of fish head with opercula maximally open and maximally closed, using an Apollo VCG7070
202 transparency film (Acco Brands, IL, USA) with a 1 mm grid. Accuracy of head width change
203 measurements was arbitrarily set at 0.5 mm. Opercula opening time (OT), an inverse proxy
204 metric of branchial pump suction, was calculated from the number of frames taken during
205 transition of opercula from closed to maximally open state. Opercula opening velocity (OV)
206 calculated as OV = OA/OT. This ratio is considered as “unidimensional” proxy metric of
207 branchial pump velocity to characterize the efficacy of ventilation. Due to suboptimal contrast in
208 some recordings, reliable characterization of respiration metrics was possible only in three
209 specimens of each species. Numbers and durations of surfacing events were manually tallied
210 post hoc on the frame-by-frame basis in Adobe Premiere Pro.
211
212 Kinematics of startle-like behaviours
213 Spontaneous startle-like behaviours were analysed post hoc manually in Adobe Premiere Pro,
214 on a frame-by-frame basis, using conventions comparable to those described above for
215 analyses of respiratory behaviours and Apollo VCG7070 transparency film (without a grid) 10
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216 placed directly on a Dell U2410 monitor projecting field video recordings. Angular velocities
217 were determined by measuring with a transparent protractor angles between vectors drawn
218 from the centre of mass (vertex of the angle, determined using a proprietary algorithm of the
219 EthoVision software) of the fishes to the snout at appropriate temporal resolution. For fast S-
220 bend startle-like manoeuvres of N. coriiceps, a 33 ms-1 frame rate may result in underestimation
221 of angular velocity.
222 Analyses of axial movements during thermally induced startle-like responses were done using
223 manual sketches of the body shapes of the fishes made on transparency film on a frame-by-
224 frame basis. For presentation purposes, ventral outlines of the turning fish were made over
225 scanned and imported into CorelDraw (Corel Corporation, ON, Canada) images.
226
227 Lateralization of C-bend manoeuvres in response to ambient warming
228 For laterality analyses, quantities and directions of C-bend manoeuvres were tallied for every
229 0.5oC increment of the temperature ramp in each of five experiments with Hb+ and Hb- fishes.
230 Since tank walls can affect lateralization (Eaton and Emberly, 1991), turns that occurred near
231 the walls were not tallied. Relative Lateralization indices (LR, %, Bisazza et al., 1998) were
232 calculated using following equation: