Love thy neighbor: Social buffering following exposure to an acute thermal stressor in a gregarious fish, the lake sturgeon (Acipenser fulvescens)
Graphical abstract
Introduction
Animal social structures, which involve a wide range of behavioral and physiological responses, are linked to how animals may respond to stressful events (Hennessy et al., 2002; LeBlanc et al., 2011; van der Kooij et al., 2018; Culbert et al., 2019). This idea was first illustrated in mammals where, depending on the nature of the social interactions, the presence of conspecifics influenced how an individual responded to stressful situations (Hennessy et al., 2002; Kiyokawa et al., 2013). In mice and primates, aggressive interactions between conspecifics may cause social stress, impairing an individual's ability to tolerate other forms of stress (DeVries et al., 2003; van der Kooij et al., 2018). Conversely, positive or pro-social interactions may improve recovery from stressful encounters, a phenomenon known as social buffering (Bartolomucci et al., 2003; Weiss et al., 2004; Hennessy et al., 2009). Social buffering was first observed in primates with individuals in stable social structures having reduced glucocorticoid responses to stress (Virgin and Sapolsky, 1997; DeVries, 2002; DeVries et al., 2003; Sanchez et al., 2015). The term social buffering was popularized by research on guinea pigs (Cavia porcellus) where the presence of an agonistic conspecific supressed the stress response of individuals (Hennessy et al., 2002). Social buffering has since been observed in multiple mammal species, including humans (Hennessy et al., 2002; DeVries et al., 2003; Kiyokawa et al., 2013). Outside of mammals, social buffering has been observed in the domestic hen (Gallus Gallus domesticus) (Edgar et al., 2015) and recently in two species of fish, the three-spined stickleback (Gasterosteus aculeatus) (Mommer and Bell, 2013; Fürtbauer and Heistermann, 2016) and the daffodil cichlid (Neolamprologus pulcher) (Culbert et al., 2019). In the stickleback, fish exposed to simulated predation in groups showed a reduced cortisol response compared to those in isolation (Mommer and Bell, 2013). Furthermore, pairs of stickleback placed in a stressful environment displayed a positive correlation between each partner's cortisol levels, providing indirect evidence for social buffering (Fürtbauer and Heistermann, 2016). In the daffodil cichlid, air-exposed individuals had lower cortisol concentrations and reduced expression of genes regulating the stress response in the brain when recovering with a familiar social group compared to fish that recovered in isolation (Culbert et al., 2019). Conversely, studies in other social fishes including zebrafish (Danio rerio) and rainbow trout (Oncorhynchus mykiss) did not demonstrate evidence supporting social buffering, indicating that social buffering may be variable in fishes and dependent on their social structures (LeBlanc et al., 2011; Giacomini et al., 2015).
Research examining the relationship between stress and sociality in fishes have largely focused on salmonids and cichlids, both of which are known to establish a dominance hierarchy in their social structures (Alonso et al., 2012; Carpenter et al., 2014; Culbert et al., 2018, Culbert et al., 2019). Dominant individuals in such social constructs may benefit from greater access to resources, increased growth (Sloman et al., 2000a; Gilmour et al., 2005), additional breeding opportunities (Fitzpatrick et al., 2008) and reduced stress (Sloman et al., 2000a; Alonso et al., 2012). While subordinate fish may display the negative effects of social stress, including reduced access to resources (Sloman et al., 2000a), reduced growth (Sloman et al., 2000b), chronically elevated cortisol levels (Gilmour et al., 2005) and increased heat shock protein (HSP) expression (Currie et al., 2010). However, not all social fishes form dominance hierarchies; in gregarious fishes all members of the social group presumably benefit from interaction (Stirling, 1977; Tanaka et al., 2018). These benefits include increased foraging success, reduced predation, and group vigilance (Stirling, 1977; Godin et al., 1988; Tanaka et al., 2018), some social fishes, such as the cichlid, Cichlasoma paranaense, may be adversely affected by isolation, responding with impaired cognition and learning (Brandão et al., 2015). Thus, it is important to understand the role of social context in mediating how fish may respond to stressors.
Thermal tolerance is an important aspect of physiology and can be highly variable in fishes. Differences in acclimation temperature, body size, genotype (Martin et al., 1976), temperature fluctuation (Feminella and Matthews, 1984), and the rate of temperature increase (Becker and Genoway, 1979) have all been shown to influence thermal tolerance. The critical thermal maximum (CTmax), as an estimate of acute thermal tolerance, is a valuable measure of physiological performance that is comparable across species. An animal's CTmax is defined as the temperature at which movement becomes disoriented and the animal loses its ability to maintain physical equilibrium (Cox, 1974; Becker and Genoway, 1979; Beitinger et al., 2000). In fishes, CTmax has typically been assessed using individual fish; however, social context may also influence thermal tolerance. For example, socially subordinate rainbow trout have a lower CTmax compared to their dominant counterparts (LeBlanc et al., 2011). While in the aggressive mangrove rivulus (Kryptolebias marmoratus), social stimulation from a mirror reflection did not affect CTmax but did delay their escape response making them more vulnerable to thermal stress (Currie and Tattersall, 2018). Currently the influence of social structure in gregarious fishes that do no display dominance hierarchies is unknown.
Lake sturgeon (Acipenser fulvescens) are a freshwater acipenseriform fish native to North America. In the wild, juvenile lake sturgeon are known to aggregate in large groups (Barth et al., 2009, Barth et al., 2011) and laboratory studies report no evidence of dominance hierarchies or aggressive behavior between conspecifics (Allen et al., 2009). Indeed, it has been proposed that long-lived species such as the lake sturgeon may be more likely to develop less aggressive social structures as continued repeat encounters between individuals may encourage reciprocal altruism or local dominance (Ridley et al., 2004). To our knowledge lake sturgeon to not defend territory, therefore, we assume that lake sturgeon sociality is based around reciprocal altruism (Ridley et al., 2004). Previous studies examining the influence of social context on the endocrine stress response in two-year-old lake sturgeon have shown that isolation resulted in a prolonged cortisol stress response following air exposure (Allen et al., 2009; Hare et al., 2015). This suggests that the presence of conspecifics may have improved the ability of juvenile lake sturgeon to recover from a stressful event pointing to possible social buffering.
Here, we tested the hypothesis that lake sturgeon will display social buffering when exposed to a stressful thermal event in the presence of conspecifics. The goal of our study was to examine the effects of social buffering in lake sturgeon following recovery from thermal stress, therefore, we selected two time points at 1 h and 20 h post-CTmax for stress measurement. The lake sturgeon endocrine and cellular responses post CTmax were measured by assessing whole body concentrations of cortisol, and mRNA expression of steroidogenic acute regulatory protein (StAR) and the cellular chaperone proteins hsp90a, hsp90b, and hsp70. We selected StAR due to its role as a rate limiting step in steroid synthesis and positive relationship with cortisol concentration in juvenile lake sturgeon (Geslin and Auperin, 2004; Castillo et al., 2008; Earhart, 2018). The selected hsp genes were chosen because of their differing responses to thermal stress in fishes. HSP90a is an inducible protein that is often strongly expressed after heat shock to serve as a cellular chaperone (Krone and Sass, 1994). The isoform hsp90b serves a similar role as hsp90b but is thought to be constitutively expressed and is more weakly affected by heat shock (Krone and Sass, 1994; Taherian et al., 2008). Finally, hsp70, another cellular chaperone is strongly expressed following heat shock in teleosts (Fowler et al., 2009; Clark et al., 2008), but weakly expressed in shortnose sturgeon (A. brevirostrum) (Zhang et al., 2017). We predicted that isolated juvenile lake sturgeon would be less thermally tolerant than those in groups and have concomitant heightened endocrine and cellular stress responses during the recovery period. Furthermore, we predicted that the effect of social buffering would increase with a larger group size and thus tested multiple group sizes alongside the isolated fish.
Section snippets
Animal maintenance
Lake sturgeon gametes were obtained in May 2018 from wild-caught adults downstream of the Pointe du Bois generating station on the Winnipeg River (50°17′52 N, 95°32′51 W), Manitoba, Canada. Eggs were fertilized at the University of Manitoba Animal Holding Facility and the hatched fish were reared in a 11 L flow-through aquarium at 15 °C on a 12 h:12 h day:night cycle. All fish used in the experiment were raised in the same aquarium with approximately 200 conspecifics, the population was
CTmax
Our results indicate that group size had no effect on the CTmax of the age-0 lake sturgeon as all three social groups had similar mean CTmax values; isolated fish (mean ± S.E.; 32.9 °C ± 0.15), 3 fish (33 °C ± 0.1), and 6 fish (32.9 °C ± 0.05) (p > .1, Fig. 2, Table 2).
Whole body cortisol
The cortisol concentration of lake sturgeon was significantly affected by both group size and recovery time (p < .001, Table 2). At 1 h post-CTmax cortisol concentrations in isolated fish were 3.3 and 3.6 fold higher than the
Discussion
Social buffering is a phenomenon where the presence of conspecifics reduces the stress experienced by their neighbours (Hennessy et al., 2002; DeVries et al., 2003). Previous research with lake sturgeon provided an indication of social buffering following air exposure (Allen et al., 2009; Hare et al., 2015) and the present study confirms the presence of this phenomenon in the gregarious lake sturgeon during recovery from acute thermal stress. Contrary to our predictions, both the isolated and
Conclusion
In summary, the presence of conspecifics during and after the CTmax test did not influence acute thermal tolerance but did significantly influence the endocrine and cellular stress response during recovery. The isolated fish showed significantly higher endocrine and cellular stress responses 1 h post-CTmax, while 20 h post-CTmax the isolated fish only showed a higher endocrine stress response. Lake sturgeon are known to be gregarious (Barth et al., 2009, Barth et al., 2011) and may benefit from
Funding
This work was supported by a Faculty of Science University of Manitoba summer studentship award awarded to M.E.Y and the research was supported by an NSERC/Manitoba Hydro Industrial Research Chair awarded to W.G.A and NSERC Discovery Grants awarded to KMJ (05479), SC (061770) and WGA (05348).
Declaration of Competing Interest
The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.
Acknowledgements
The authors thank the University of Manitoba Animal Holding staff for their assistance in caring for the lake sturgeon and conducting this experiment.
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