Chronic exposure to increased water temperature reveals few impacts on stress physiology and growth responses in juvenile Atlantic salmon
Introduction
Atlantic salmon (Salmo salar) aquaculture is an established industry in several countries, including Norway, Scotland, Ireland, the Faroe Islands, Canada, USA, Chile and Australia (Tasmania) (“Aquaculture topics and activities. Aquaculture resources. In: FAO Fisheries and Aquaculture Department,”, 2015). The majority of the production areas are within latitudes 40–70° in the Northern Hemisphere, and 40–50° in the Southern Hemisphere (“Aquaculture topics and activities. Aquaculture resources. In: FAO Fisheries and Aquaculture Department,”, 2015). When reared in freshwater or seawater phases, Atlantic salmon, can be restricted in their movement, and therefore, be exposed to several environmental stressors, including seasonal or abrupt changes in water temperature.
It has been demonstrated that Juvenile Atlantic salmon are tolerant to a wide range of temperatures, where incipient (50% survival after 7 days) and ultimate lethal tolerance (survival for 10 min) range from 0 to 28 °C and −0.8–33 °C respectively (Elliott and Elliott, 2010). However, reports concerning the optimal temperature for growth in juvenile Atlantic salmon when maintained under a static regime are conflicting. In their review, Elliott and Elliott (2010) suggested that 16–20 °C provided maximum growth efficiency in juvenile Atlantic salmon. Similarly, Jensen et al. (2015) demonstrated improved growth in juvenile Atlantic salmon maintained in saltwater for four weeks at 16 °C compared to 4 °C and 10 °C, respectively. In contrast, Handeland et al. (2008) reported that the optimal temperature for growth in post-smolt juvenile Atlantic salmon was 12.8 °C when 70–150 g, and 14 °C when 150–300 g.
The temperature range for which the onset of chronic thermal stress occurs in juvenile Atlantic salmon is not well understood. Under commercial aquaculture conditions, Atlantic salmon are confined to particular areas of the water column, and therefore, can be unwillingly subjected to abrupt or seasonal changes in water temperature. It is well known that metabolism in fish is influenced by water temperature, and to some extent also health, stress response, growth and survival (Afonso et al., 2008; Dominguez et al., 2004; Pérez-Casanova et al., 2008a, Pérez-Casanova et al., 2008b; Tromp et al., 2016). Therefore, chronic thermal stress could have deleterious consequences on the overall fitness of fish. Most studies concerned with the metabolic effects of high water temperatures in Atlantic salmon were conducted for relatively short periods of time (Elliott and Elliott, 2010 (7 days); Hevrøy et al., 2012 (56 days); Olsvik et al., 2013 (45 days)), and therefore, information regarding the effects of chronic exposure to high water temperatures is poorly known in this species.
Chronic effects of high water temperature are better known in other species (Pérez-Casanova et al., 2008b; Tromp et al., 2016). Acute exposure to stressors reveal that the immediate response to stress (increased plasma cortisol and glucose levels) helps the animal to cope with the stressor (Iwama et al., 2005). Information on the effects of chronic exposure to high temperatures on cortisol are important for understanding physiological processes, given its many effects on fish performance and production (Mommsen et al., 1999). For example, a chronic regime of increasing temperature led to elevated plasma cortisol, mortality, and expression of immune-related genes in Atlantic cod (Gadus morhua) when the temperature reached 16 °C, but this was only evident approximately 30 days after the beginning of the experiment (Pérez-Casanova et al., 2008b). On the other hand, in Atlantic salmon, constant exposure to 19 °C for 56 days led to reduced growth, but no significant change in plasma cortisol (Hevrøy et al., 2012). Similarly, culture of hapuku (Polyprion oxygeneios) at 22 °C for 98 days suppressed their gain in body mass, reduced their condition factor and specific growth rate, but did not significantly change plasma cortisol levels (Tromp et al., 2016). One explanation for the incidence of elevated cortisol in some studies where fish were subjected to chronic exposure to high water temperatures, yet not in others, may be an ability of some fish to acclimate to chronic stress, and thereby reduce elevated plasma cortisol levels back to a pre-stressed state (Barton and Schreck, 1987; Pickering and Pottinger, 1987).
In addition to a lack of studies on the effects long-term exposure to thermal stress on plasma cortisol levels, there is limited information about cholesterol levels in fish during stress. Cholesterol plays a central role in steroid hormone biosynthesis (Mommsen et al., 1999; Tokarz et al., 2015), including cortisol. The only study on plasma cholesterol levels in salmonids during exposure to high temperatures (from 10 °C to 20 °C) have shown decline in cholesterol values (Wedemeyer, 1973). In humans, low plasma cholesterol levels are described as hypocholesterolaemia, and affect immune and inflammation functions (Vyroubal et al., 2008). Obtaining information about cholesterol and cortisol levels during chronic exposure to high temperatures is important considering that cortisol is the principal corticosteroid in fish and exerts significant physiological roles in metabolic regulation, osmoregulation, growth and reproduction (Mommsen et al., 1999).
Throughout the last 30 years there has been considerable interest in studying the development of bimodal growth in juvenile Atlantic salmon during the freshwater phase. Most of these studies have been carried out in hatchery and laboratory-raised fish, and they have demonstrated that in their first year of growth, Atlantic salmon can be separated into two classes based on their length: upper mode (UM) and lower mode (LM) (Heggenes and Metcalfe, 1991; Kristinsson et al., 1985; Nicieza et al., 1994; Simpson and Thorpe, 1976; Zydlewski et al., 2014) The larger fish (UM) have the potential to become smolts earlier than the LM fish. Most of these studies have examined the development of bimodal growth under normal or ambient temperatures for growth (Imsland et al., 2016; Kristinsson et al., 1985; Metcalfe et al., 1988; Shrimpton et al., 2000; Shrimpton and McCormick, 1998). There are no studies that have investigated the effects of long-term exposure to elevated temperature on the bimodal growth. In addition a few studies have examined differences in physiological indicators between these two classes. For example, it has been shown that under normal hatchery conditions fish in the UM showed increased levels of classical indicators of smoltification (plasma cortisol, growth hormone, and gill Na+, K+-ATPase) well in advance than fish in the LM (Shrimpton et al., 2000; Shrimpton and McCormick, 1998).
Recently there have been few studies that investigate the development of rapid, non-invasive and reliable techniques for determining stress. The measurement of eye sclera colour changes, termed eye darkening (ED) has shown the potential to be used as an non-invasive indicator for stress in fish (Freitas et al., 2014; Suter and Huntingford, 2002; Vera Cruz and Brown, 2007; Volpato et al., 2003). The physiological processes that induce ED in fish are not well understood (Nilsson Sköld et al., 2013). However, there is evidence in sand goby (Pomatoschistus minutes) via an in vitro study that ED may be controlled by changes in the dispersal of eye chromophores due to melanin concentrating hormone (MCH) and the adrenocorticotrophic hormone (ACTH) (Sköld et al., 2015). Given the role of ACTH in cortisol production (Barton and Iwama, 1991), these findings suggest that ED may be controlled by hormones involved in the generalised stress response in fish.
Considering the paucity of studies investigating the long-term exposure of juvenile Atlantic salmon to elevated temperatures, we examined the effects of a chronic increase in water temperature for 99 days on this species stress response and growth. The chronic physiological responses were studied temporally by measuring total plasma cortisol, glucose, and cholesterol levels and eye darkening at the last sampling time. As we were able, at the end of the study, to identify bimodal growth, and therefore separate fish by size into upper and lower modes, we also measured the physiological and growth indicators in these groups. Investigation of the effects of long-term exposure to high temperature, including in fish categorised as fast or slow growers, may lead to a better understanding of their physiology, and identification of phenotypes that are better prepared to deal with elevated temperatures.
Section snippets
Animal husbandry
Fish were held in three identical indoor recirculating aquaculture systems at the Deakin Aquaculture Futures Facility, and treated through physical, biological and UV sterilisation (Norambuena et al., 2016). Each system controlled for temperature at 12 °C and photoperiod (12 L:12D) prior to fish delivery. Juvenile Atlantic salmon (~70 g) were sourced from Mountain Fresh Trout and Salmon Farm, Victoria, Australia. Upon arrival, fish were distributed into two 2000 L circular polyethylene tanks,
Bimodal growth
At the end of the study, a bimodal distribution was observed in all treatments groups (Fig. 2). Fork length was used for assessing bimodal growth, as previously it has been used as the standard method to categorise juvenile Atlantic salmon (Simpson and Thorpe, 1976; Thorpe et al., 1980). From plotting the distribution for all length measurements at all temperatures, it was determined that at a fork length of 240 mm, there was a clear visual separation between the two distributions, resulting in
Discussion
In this study we reported the effects of chronic thermal stress on growth and stress physiology responses of Atlantic salmon. This study expanded on the current knowledge of growth profiles and cortisol, glucose and cholesterol levels in fish after exposure (99 days) to increased water temperature, and further investigated the temporal change within this period. We demonstrated that juvenile Atlantic salmon maintained at 16 °C over a period of 99 days had increased plasma cortisol levels at day
Acknowledgements
The authors would like to thank the tireless effort of Anthony Tumbarello, Chris Henaghan and all the other volunteers that donated their time. In addition we are grateful for the technical assistance provided by Bob Collins and Amber Chen at Deakin's Aquaculture Futures Facility. This study was supported by grants from Tassal Group Limited.
Author contributions
Name Contribution Jared J. Tromp Experimental design, conducted the sampling, implemented eye darkening (ED) measurements and analysis, statistical analysis, interpreted the analysis and wrote the manuscript. Paul L. Jones Experimental design, conducted sampling and comments on the manuscript. Morgan S. Brown Conducted sampling, implemented eye darkening (ED) measurements and analysis, comments on the manuscript. John A. Donald Comments on the manuscript. Peter A. Biro Statistical
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