Cleaning interactions are textbook examples of mutualisms. On coral reefs, most fishes engage in cooperative interactions with cleaners fishes, where they benefit from ectoparasite reduction and ultimately stress relief. Furthermore, such interactions elicit beneficial effects on clients’ ecophysiology. However, the potential effects of future ocean warming (OW) and acidification (OA) on these charismatic associations are unknown. Here we show that a 45-day acclimation period to OW (+3 °C) and OA (980 μatm pCO2) decreased interactions between cleaner wrasses (Labroides dimidiatus) and clients (Naso elegans). Cleaners also invested more in the interactions by providing tactile stimulation under OA. Although this form of investment is typically used by cleaners to prolong interactions and reconcile after cheating, interaction time and client jolt rate (a correlate of dishonesty) were not affected by any stressor. In both partners, the dopaminergic (in all brain regions) and serotoninergic (forebrain) systems were significantly altered by these stressors. On the other hand, in cleaners, the interaction with warming ameliorated dopaminergic and serotonergic responses to OA. Dopamine and serotonin correlated positively with motivation to interact and cleaners interaction investment (tactile stimulation). We advocate that such neurobiological changes associated with cleaning behaviour may affect the maintenance of community structures on coral reefs.
Mutualisms are ecological interactions that benefit two or more species1. Cleaning behaviour is one of the most important mutualistic interactions between fishes in coral reefs2,3,4. Cleanin g directly affects communities structure and health, as the removal of cleaners in small patch reefs decreased fish diversity, recruitment and abundance of both site-attached resident fishes and visitor client fishes2,3,4. While interacting with client fish, some cleaners (e.g. wrasse Labroides dimidiatus) can either cooperate (eating parasites, i.e. cleaning) or cheat (eating mucus from clients) which they prefer5. Whenever cleaners choose to be dishonest, a conflict arises, typically resulting in an observable “jolt” of the client, in response to the cleaner’s bite6. Cleaners can reduce conflict and invest in the quality of the interaction by providing tactile stimulation to their clients (physical contact with client bodies) using their pelvic fins7. Additionally, cleaners can increase inspection quality and duration, which enhances the odds of future interactions8.
To optimize the output of cooperative interactions, fishes need to adjust their social behaviour according to the available social information (i.e. social competence)9. The ability to regulate their social behaviour relies on mechanisms that allow fast and transient behavioural changes, which depend on socially-driven biochemical switching of existing neural networks (e.g. neuromodulators). Monoamines are one major class of neuromodulators and their action in social behaviour as well as their sensitivity to environmental factors, have been extensively documented10. They are thought to be involved in control and integration of behaviour and physiological stress response in fish11. For instance, cleaner wrasses’ social behaviour is known to be modulated by different monoamines, namely serotonin and dopamine, which affect motivation to interact and interaction quality, respectively12,13.
Ocean warming and acidification, caused by the rising concentration of carbon dioxide (CO2) in the atmosphere, are predicted to impact fish behaviour and physiology14. Sensitivity to ocean acidification acclimation can lead to learning impairments15, increased anxiety in rockfish (Sebastes diploproa)16, disrupted lateralization17 and loss of auditory in mulloway larvae (Argyrosomus japonicus)18 and olfactory responses of orange clown fish (Amphiprion percula)19. Several of those impairments are assumed to be linked to changes in Cl− ion exchange in γ-aminobutyric acid type A (GABAA) receptors, as the administration of gabazine (GABAA antagonist) restored those effects16,20. Likewise, ocean warming can impact fish behaviour by increasing activity levels21, sensory responsiveness22 and prey-predator interactions23. In fact, the changes in these climate-change related drivers can unbalance mutualisms towards more exploitative outcomes, where a once-beneficial interaction can become less beneficial or even detrimental1.
Although a recent study showed the deleterious impact of extreme environmental perturbations, namely cyclones and bleaching, to cleaner fish abundance and sophistication24, there is no knowledge regarding the combined effect of ocean warming and acidification on cleaning mutualisms and how these might affect the respective neuromodulators. Here, we evaluated how simulated end-of-century elevated CO2 (~960 µatm, high CO2) and warming (+3 °C) scenarios25 may affect cooperative cleaning interactions between the cleaner wrasse (L. dimidiatus) and a client surgeonfish (Naso elegans). To analyse the behaviour component of cleaning interactions we measured cleaner fish and client motivation to interact (e.g. number of interactions, the proportion of interactions initiated by cleaners and ratio of client “posing” displays) and interaction quality (e.g. mean interaction duration, number of client jolts and proportion of interactions with tactile stimulation). To study the molecular mechanisms behind such changes in the cleaning interactions, we quantified monoamine levels and metabolites (as a proxy of activity) in three major regions of the fish brain that are normally analysed in social behaviour studies – e.g. forebrain, midbrain and hindbrain26,27,28. Moreover, we investigated how serotoninergic and dopaminergic systems were associated with motivation to engage in cooperation and interaction quality.
After 45 days of acclimation, the number of cleaning interactions was significantly decreased under warming (−93%), acidification (−85%) and the interaction of these two stressors (−73%, df = 30, p < 0.001; Fig. 1a, Supplementary Table S2). On average, the proportion of interactions initiated by the cleaners declined under elevated CO2 (−66%, df = 26, p < 0.001; Fig. 1b, Supplementary Table S2), but there was no significant effect of warming, or the interaction between stressors. By contrast, the client posing displays ratio significantly increased under high CO2 (+84%, df = 30, p < 0.05; Fig. 1c, Supplementary Table S2). While the proportion of cleaning interactions with tactile stimulation significantly increased under high CO2 (+15%, df = 26, p < 0.01; Fig. 1d, Supplementary Table S2), cleaners’ dishonesty (proportion of interactions with client jolts) and interaction duration were not affected significantly by either warming or high CO2 (df = 26, p > 0.05; Fig. 1e–f, Supplementary Table S2).
In cleaner fish, although dopamine concentration was overall higher in midbrain and hindbrain, a significant interaction of stressors was observed (independently of the brain region), high CO2 significantly decreased dopamine only under lower temperatures (−67% in FB, −65% in MB, −48% in HB; df = 23, p < 0.01; Fig. 2a, Supplementary Table S3). On the other hand, DOPAC concentration did not change among treatments (df = 23, p > 0.05, Fig. 2b Supplementary Table S3). Serotonin (5-HT) concentration significantly decreased in the forebrain under high CO2 (−19%, df = 23, p < 0.05; Fig. 2c, Supplementary Table S3), while regarding 5-HIAA concentration, there was a significant interaction of stressors in the hindbrain, as high CO2 significantly increased 5-HIAA under lower temperature (−91%, df = 23, p < 0.05; Fig. 2d, Supplementary Table S3).
In clients, dopamine concentration (overall higher in the forebrain) was significantly decreased under high CO2 in the forebrain (−57%) and hindbrain (−32%), and increased in the midbrain (+77%; df = 23, p < 0.05; Fig. 3a, Supplementary Table S4). Contrarily, DOPAC (df = 23, p > 0.05, Fig. 3a Supplementary Table S4) and serotonin (df = 23, p > 0.05, Fig. 3a Supplementary Table S4) concentrations did not change among treatments. While 5-HIAA concentration significantly decreased in the forebrain under high CO2 (−8%, df = 23, p < 0.05; Fig. 2d, Supplementary Table S3).
Correlation between behaviour and neurotransmitters
The canonical correlation analysis (CCA) between the neurobiological (N) and behaviour (B) sets of variables showed that, in cleaners, 51.9% of the behavioural variability was explained by neurobiological variables. CCA cross-loadings (Supplementary Figs S1-S2) revealed that the first canonical variable (CV1) has a strong negative correlation with proportion of interactions with tactile stimulation (rNCV1 × Tactile stimulation = −0.85) and positive with client jolts (rNCV1 × client jolts = 0.63) and a moderate negative correlation with midbrain 5-HIAA (rBCV1 × MB-5-HIAA = −0.45), and hindbrain serotonin and dopamine concentrations (rBCV1 × HB-5-HT = −0.44, rBCV1 × HB-DA = −0.3). The CCA also showed that CV2 correlates negatively with the proportion of interactions initiated by cleaners (rNCV2 × interactions initiated by cleaners = −0.84) and number of interactions (rNCV2 × interactions = −0.79) and with midbrain dopamine, DOPAC (rBCV2 × MB-DA = −0.6; rBCV2 × MB-DOPAC = −0.36), and hindbrain 5-HIAA concentrations (rBCV2 × HB-5-HIAA = −0.38).
For the client fish, CCA between neurobiological and behavioural variables showed that, on average, 15.7% of the behavioural variability was explained by neurotransmitters concentration. CCA cross-loadings (Supplementary Figs S3-S4) revealed that CV1 has positive correlation with client posing ratio (rNCV1 × Client posing = 0.67) and negative correlation with the midbrain serotonin and 5-HIAA concentrations (rBCV1 × MB-5-HT = −0.29). On the other hand, CV2 correlates negatively with the proportion of interactions with jolts (rNCV2 × client jolts = 0.57), number of interactions (rNCV2 × interactions = −0.51) and with midbrain dopamine (rBCV2 × MB-DA = 0.57).
Fish behaviour and physiology is known to be affected by ocean warming and acidification but their effects on cleaning mutualisms are poorly known1,14. Here, we show that both these stressors affect the cooperative cleaning interactions (both at behavioural and neurobiological scales) between the cleaner wrasse L. dimidiatus and the client fish N. elegans. The motivation to interact dropped and interaction quality changed under such conditions. Concomitantly, the dopaminergic (in all brain regions) and serotonergic (in the forebrain) systems were significantly altered by these stressors in both partners.
Impaired cleaning interactions can indirectly lead to cascading effects on local fish community structure and abundance. Previous studies suggest that the presence of cleaner wrasses can affect local communities as the experimental removal of cleaners in small patch reefs decreased fish diversity, recruitment and abundance of both site-attached resident fishes and visitor client fishes2. Cleaner fish presence is known to affect parasitic gnathiid isopod loads on individuals3, and just a single gnathiid ectoparasite can significantly impact fish survival (especially small recruits) as it decreases their swimming performance and metabolic rates and increases mortality rates29. Thus, a disruption of cleaning interactions under warming and ocean acidification could indirectly, by a putative increase in clients’ ectoparasite load, affect client fish physiology and, ultimately, survival. The local and individual effects of losing this mutualism could eventually scale up to a community level (i.e. cascading trophic effects1).
The motivation to engage in cooperative interactions (number of interactions) was significantly lower under ocean acidification, warming and the combined stressors. Crucially, the cleaners’ motivation to clean declined with acidification, with the proportion of interactions started by cleaners dropping from >75% to <10%. This change in cleaner behaviour was associated with an increase in client posing displays, suggesting that the clients’ motivation to be cleaned had increased.
Clients that experience quality interactions return to the same cleaning station where they were previously inspected, and nearby bystanders choose stations where good quality interactions occur30. Thus, investment in the quality of interactions is crucial for cleaners to increase food availability, as they depend solely on cleaning interactions for food5,30). Here, cleaner dishonesty (measure as client jolts) and interaction duration were not affected by any stressor. Dishonesty usually increases when cleaners are interacting with resident clients that cannot choose among different cleaning stations31. As cleaners were deprived of clients during the whole exposure period, the clients could have been perceived as visitors, leading to the low number of interactions with jolts. Another possible explanation is related with the low number of interactions observed under the different stressors, as cleaners might have lacked the opportunity or motivation to cheat during the behavioural trial. The opposite occurred under acidification, as tactile stimulation events increased under high CO2. Cleaners use tactile stimulation to negotiate when the outcome of an interaction is not certain or to prolong interactions after a cheating event. Contrary to predictions, the cleaners’ dishonesty levels remained unaffected by ocean acidification conditions. As tactile stimulation is incompatible with foraging, and it is a costly form of negotiation32, ocean acidification might be modulating cleaner wrasse anticipation/perception regarding predicted rewards and cost in an interaction, as if the client was more likely to terminate the interaction. The observed effects of ocean warming and acidification on motivation to engage in cleaning interactions and interaction quality could lead to mutualism loss by: (i) reduction of interactions, ceasing the exchange of rewards between partners; and (ii) loss of negotiation, leading to unfruitful interactions for at least one partner (cleaner)1,33.
Here we also showed that ocean warming and acidification altered monoamine concentrations in the different brain regions. So far social behaviour in fishes, including the present species pair, was described to be modulated by different monoaminergic concentrations in different brain regions26,27,28. As expected, these stressors had distinct interspecific effects and differences among the studied brain region. Under ocean acidification, cleaners’ dopamine concentration was overall lower, and no changes were observed in its metabolite DOPAC concentration. Interestingly, hindbrain dopamine concentration was correlated with tactile stimulation. These findings are aligned with a previous study where dopamine disruption was shown to affect directly tactile stimulation without affecting cleaner honesty13. In such study, the authors described that blocking dopamine receptors induces cleaners to initiate more interactions with clients, contrarily, we observed less interactions and less motivation to interact together with a decrease in dopamine concentration under high CO2. Moreover midbrain dopamine concentration was correlated number of interactions and cleaners’ motivation to interact. Here, since we observed the effect after the lack of interactions, it was logical to expect low levels of dopamine related with lower rewards or decreased likelihood to obtain food13,34. Since dopamine is responsible for modulating cleaners’ perception of rewards and risks, influencing their capacity to manipulate clients within an interaction, our findings suggest a potential mechanistic effect of high CO2 on the dopaminergic system with consequences on reward and risk perception.
In clients, dopamine concentration also decreased overall under high CO2 and, in midbrain, was correlated with the number of interactions which, as with cleaners, could be related with lower rewards due to the lack of interactions26. Since dopaminergic activation can be: (i) driven by the perception of the interactions, and (ii) related to species-specific social behaviours across vertebrates (as aggression and courtship), we argue that ocean acidification may lead to dopamine-induced impairment of clients’ perception of rewards, as a visual stimulus (cleaner’s presence) is perceived without achieving an interaction (reward). Together, the across species effect on the dopaminergic system suggests dopamine as a potential neurobiological system by which high CO2 impairs behaviour although further pharmacological studies are needed to confirm this. Dopamine was not affected by CO2 when cleaners were exposed to higher temperatures this could suggest an antagonistic interaction of both stressors and the presence of a cross-tolerance mechanism35.
In the serotonergic system, we observed decrease in cleaners’ forebrain serotonergic concentration and overall 5-HIAA increase along with a lower motivation to interact under ocean acidification. The serotonin blockade is known to disrupt motivation for cleaning interactions12 and forebrain serotonergic activity can regulate and be regulated by social interactions26. Therefore, we suggest that CO2 could affect serotonin function disrupting the motivation to interact. In clients serotonin concentration was not affected by any stressor, and 5-HIAA decreased in the forebrain under high CO2. A previous study12 had already shown that serotonin may not affect clients’ direct interactions with cleaners, and thus motivation to interact is not equally modulated in cleaners and clients. It is worth noting that contrary to a recent study in cod, which found a higher serotonergic activity under ocean warming36, the serotoninergic system was not affected by warming alone in both fishes. We argue that both mutualistic partners live in a relatively more stable temperature environment than temperate and sub-arctic cod species, and therefore they may lack the ability of serotonergic modulation of respiration observed in cod, but further investigation is needed to test this hypothesis. The metabolite 5-HIAA was also not affect by CO2 when cleaners were exposed to higher temperatures again suggesting an antagonistic interactions of stressors an cross-tolerance mechanisms35.
It is worth noting that GABAergic neurotransmission is the major system known to be affected by ocean acidification and one cannot discard its effects and possible GABAergic interactions with dopamine and serotonin16,20,37. Under elevated CO2, the equilibrium potential for Cl− is disrupted due to a decrease in plasma Cl− concentration to maintain charge balance (due to H+ excretion to counteract acidosis). When GABA binds to the normally inhibitory GABAA receptor channel opening leads to net Cl− movement out of the neuron, causing membrane depolarization and increasing excitation of neural pathways38. This process was described in both fish and invertebrates – e.g. mollusks39,40. The GABAergic system is known to be linked with both dopaminergic and serotonergic systems, as GABAA receptor activation in GABAergic interneurons can reduce serotonergic response41 and dopamine neurons can exert a strong inhibitory influence through activation of GABAA receptors42. Therefore, the described effect of CO2 in GABAergic receptors, and their relation with serotonin and dopamine can play a role in the potential mechanism of high CO2 disruption of cooperative cleaning behaviour.
In conclusion, we show that cooperative cleaning interactions, a key mutualism in coral reefs, are disrupted by ocean warming and acidification conditions. This disruption could potential lead to mutualism breakdown if: (1) this mutualism shift to antagonism, (2) one of the partner switches to novel partners or (3) both partners abandon the mutualistic interaction1,33. Mutualism integrity is affected mainly by a lower motivation to engage in interactions and lack of proper perception of interaction quality by cleaners, by disrupting their ability to negotiate (under elevated CO2). We suggest that CO2 could interact (directly or indirectly) with: (i) dopamine, a new potential neurobiological system of CO2 behaviour impairment, damaging cleaners’ and clients’ perception and ability to negotiate and (ii) serotonin modulating motivation for interaction, although further pharmacological studies are required to support this hypothesis. Unravelling the interspecific behavioural effect of ocean warming and acidification with neurobiological links is a priority for future research, as it would provide the opportunity to better understand possible behavioural impairments at the community level. Thus, we propose that a climate change induced neurobiological and behavioural disruption of cleaning mutualisms will significantly affect the structure of local communities of coral reefs.
We used cleaner wrasses Labroides dimidiatus (n = 32; size 5.4 ± 0.6 cm) and surgeon fish Naso elegans (n = 32, size 6.9 ± 1.1 cm), a frequent client of cleaner wrasses known to be easily adapted to laboratory conditions43. These species have been used in behavioural and neurobiological studies and exhibit fully their cooperative cleaning interactions in aquaria even without the presence of parasites. Both were collected by local fishermen, using hand nets and barrier nets, between November and December 2014 in the Maldives and transported by TMC Iberia to the aquatic facilities of Laboratório Marítimo da Guia (Cascais, Portugal). To avoid possible interactions between parasitation levels, parasite-fish interaction and parasite responses to ocean warming and acidification treatments fish were deparasitized with a five-minute freshwater bath on arrival44. Fish were also laboratory acclimated for 5 days at seawater conditions similar to the collection site: salinity = 35 ± 0.5, temperature 29 °C (Maldives 2013–2014 average SST, NOAA45), pH 8.1 and pCO2 ~400 ppm (2014 BOBOA Ocean Acidification mooring, NOAA46). Each fish was exposed for 45 days (to one of the four following experimental treatments) in separated individual tanks (i.e. 8 L. dimidiatus and 8 N. elegans per treatment, 32 L. dimidiatus and 32 N. elegans in total; a total of 64 tanks): (1) present day scenario (control) (29 °C, pH 8.1, pCO2 ~ 400 ppm), (2) warming scenario (32 °C, pH 8.1, pCO2 ~400 ppm), (3) high CO2 – acidification (29 °C, pH 7.7, pCO2 ~960 ppm) and (4) high CO2 + warming (32 °C, pH 7.7, pCO2 ~960 ppm), following IPCC’s RCP scenario 8.525 (see Table S1 for water chemistry summary). During the exposure period one fish from each species died in the warming scenario.
In each treatment, we used flow-through aquatic systems to maintain correct levels of total alkalinity, dissolved inorganic carbon and pH. Natural seawater (NSW) was pumped from the sea into a 5 m3 seawater storage tank. From the storage tank, NSW was filtered (0.35 μm) and UV-irradiated (Vecton 300, TMC Iberia, Portugal) before being supplied to mixing and experimental tanks. Experimental tanks were kept under a photoperiod of 12 h/12 h (light/dark cycle). Ammonia and nitrate levels were daily checked using colorimetric tests (Salifert Profi Test, Holland). Levels of pH were monitored and automatically adjusted every 2 seconds (Profilux 3.1 N, GLH, Germany), downregulated by direct injection of certified CO2 gas (Air Liquide, Portugal) and upregulated through aeration with CO2 filtered atmospheric air (soda lime, Sigma-Aldrich) in mixing tanks. Seawater temperature was regulated using chillers (Frimar, Fernando Ribeiro Lda, Portugal) and submerged heaters (300 W, TMC-Iberia, Portugal). We used additional handheld equipment to complement the automatic systems with a manual daily monitoring of seawater temperature (TFX 430 thermometer, WTW GmbH, Germany), salinity (V2 refractometer, TMC Iberia, Portugal) and pH (826 pH mobile, Metrohm, Germany). We quantified pH using a pH meter connected to a glass electrode (Schott IoLine, Si analytics, ±0.001), calibrated with TRIS-HCl (TRIS) and 2-aminopyridine-HCl (AMP) seawater buffers. Seawater carbonate system speciation was calculated twice a week from total alkalinity (spectrophotometrically at 595 nm) and pH measurements40. Bicarbonate and pCO2 values were calculated using CO2SYS software. Seawater parameters of different experimental setups are summarized in Supplementary Table S5.
Following 45 days of acclimation, both cleaners and clients were fasted for 24 hours. After fasting, pairs composed of one cleaner L. dimidiatus and one client N. elegans interacted for 30 minutes (between 08:00–12:00) in observation tanks (3 isolated aquaria: 30 cm × 40 cm × 40 cm) with the same water parameters as the experimental treatments. Fish were acclimatized to the observation tank for 15 minutes prior to the experiment separated by an opaque acrylic partition. During the observation period, the experimenter raised the partition, left the room, and the behavioural trial was recorded for 30 minutes by a video camera (Canon Legria HFR56) positioned frontally to the observation tank wall. Before each trial water was renovated and the tank was cleaned to avoid possible chemical cues. To characterize cleaner and client motivation to interact, we measured the number of interactions, the proportion of interactions initiated by cleaners and ratio of client “posing” displays (i.e. client “posing displays/time of no interaction; “posing” displays are conspicuous signals used by clients seeking cleaning interactions from cleaners47). Cleaning interaction quality was determined using mean interaction duration, number of client jolts (jolt is a conspicuous signal that indicates cheating48) and proportion of interactions with tactile stimulation (cleaners use tactile stimulation of clients with their pectoral fins to manipulate them as this behaviour has been shown to reduce stress levels and can prolong interaction duration4,7). All data were analysed per trial (30 minute observation).
Brain sampling and quantification of brain monoamines and metabolites
To avoid monoamine degradation during the brain macro-dissection and to keep the time of sampling after the interactions as homogeneous, cleaner and client fishes were sacrificed immediately after an overdose of tricaine solution (MS222, Pharmaq; 250 mg/L) and the spinal cord sectioned. The brain was macrodissected under a stereoscope (Leica S6D) into three regions: forebrain (olfactory bulbs + telencephalon + diencephalon, FB), midbrain (optic tectum, MB), and hindbrain (cerebellum + brainstem, HB). Immediately after collection brain tissue was placed on dry ice and stored at −80 °C until analysis.
Frozen brain regions from 24 interacting pairs (48 fish, 12 per treatment) were homogenized in 4% (w/v) ice-cold perchloric acid containing 100 ng/ml 3,4-dihydroxybenzylamine (DHBA, the internal standard) using a Sonifier cell disruptor B-30 (Branson Ultrasonics, Danbury, CT, USA) and were immediately placed on dry ice. Subsequently, the homogenized samples were thawed and centrifuged at 21,000 × g for 10 min at 4 °C. The supernatant was used for high-performance liquid chromatography with electrochemical detection (HPLC-EC), analyzing the monoamines dopamine (DA) and serotonin (5-HT, 5-hydroxytryptamine), the DA metabolite DOPAC (3,4-dihydroxyphenylacetic acid), and the 5-HT metabolite 5-HIAA (5-hydroxy indole acetic acid), as described by Teles et al.26. In brief, the HPLC–EC system consisted of a solvent delivery as system model 582 (ESA, Bedford, MA, USA), an auto injector Midas type 830 (Spark Holland, Emmen, the Netherlands), a reverse phase column (Reprosil-Pur C18-AQ 3 μm, 100 mm × 4 mm column, Dr. Maisch HPLC GmbH, Ammerbuch-Entringen, Germany) kept at 40 °C and an ESA 5200 Coulochem II EC detector (ESA, Bedford, MA, USA) with two electrodes at reducing and oxidizing potentials of −40 mV and +320 mV. A guarding electrode with a potential of +450 mV was employed before the analytical electrodes to oxidize any contaminants. The mobile phase consisted of 75 mM sodium phosphate, 1.4 mM sodium octyl sulphate and 10 μM EDTA in deionized water containing 7% acetonitrile brought to pH 3.1 with phosphoric acid. Samples were quantified by comparison with standard solutions of known concentrations. To correct for recovery DHBA was used as an internal standard using HPLC software ClarityTM (DataApex Ltd., Prague, Czech Republic).
Data exploration was performed according to Zuur et al.49, which promotes a protocol for data exploration. Behavioural data was analysed using Generalized Linear Models (GLM) using pCO2 and temperature as covariates, according to Zuur and Ieno50. In these models, Gaussian distribution was used for continuous data (interaction duration and client posing ratio); negative binomial distribution for count data (number of interactions, since we observed overdispersion of Pearson residuals using Poisson distribution) and binomial distribution for proportions (proportion of interactions started by cleaners, proportion of interactions with tactile stimulation and proportion of interactions with client jolts). For neurobiological data analysis, we used a Generalized Linear Mixed Model framework with individual identity as a random effect, pCO2, temperature and brain region as covariates and Gamma distribution. Selection for best model was made using Akaike Information Criterion (AIC). Model assumptions, namely independence and absence of residual patterns, were verified by plotting residuals against fitted values and each covariate in the model. A canonical correlation analysis was performed to explore the correlation between two paired variable sets, behaviour variables and neurobiological variables for each species. Statistical analysis was performed in R51 and data exploration and model validation used the HighstatLibV10 R library from Highland Statistics52.
Research was conducted under approval of Faculdade de Ciências da Universidade de Lisboa animal welfare body (ORBEA – Statement 01/2017) and Direção-Geral de Alimentação e Veterinária (DGAV – Permit 2018-05-23-010275) in accordance with the requirements imposed by the Directive 2010/63/EU of the European Parliament and of the Council of 22 September 2010 on the protection of animals used for scientific purposes.
Data supporting this article is available in the repository figshare https://doi.org/10.6084/m9.figshare.7235192.
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The authors acknowledge Laboratório Marítimo da Guia members and volunteers that helped in fish and aquatic systems maintenance throughout the experiment and Catarina Santos for the drawings. This study was funded by Portuguese national funds through FCT – Fundação para a Ciência e Tecnologia, I.P., within the project MUTUALCHANGE - PTDC/MAR-EST/5880/2014, ASCEND - PTDC/BIA-BMA/28609/2017 and the strategic project UID/MAR/04292/2013 granted to MARE. FCT also supported this study through a PhD scholarship to JRP (SFRH/BD/111153/2015), Programa Investigador FCT to RR (IF/01373/2013) and a postdoctoral fellowship to TR (SFRH/BPD/94523/2013). The Swedish Research Council (VR) supported SW. This study was co-funded by Programa Operacional Regional de Lisboa, Portugal 2020 and the European Union within the project LISBOA-01-0145-FEDER-028609.
The authors declare no competing interests.
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