Early development and metabolic rate of the sea louse Caligus rogercresseyi under different scenarios of temperature and pCO2
Introduction
Climate change, driven by the rapid release of anthropogenic CO2 into the atmosphere is causing an increase in seawater temperature, “ocean warming”, and at the same time a decrease in seawater pH, “ocean acidification” (IPCC, 2013; Duarte et al., 2014; Lee et al., 2017). Since preindustrial times ocean acidity has increased 26% and unabated CO2 emissions are predicted to cause the acidity to increase by 170% during this century (IPCC, 2013). Several economic activities, such as aquaculture, occur in the marine realm and will experience the combined effects of elevated temperature and CO2, which may influence the intensity and frequency of pathogen outbreaks (Ellis et al., 2017).
Elevated pCO2 can cause alterations in the physiological performance of organisms (Navarro et al., 2013; Almén et al., 2017; Mangan et al., 2017). Additionally, severe behavioral changes, such as in the ability to avoid predators, obtain food, mating and swimming capacity, have been recorded in both mollusks and crustaceans as consequence of high levels of pCO2 (Briffa et al., 2012; Navarro et al., 2013; Almén et al., 2017; Wang et al., 2018; Porteus et al., 2018). In copepods, high levels of pCO2 can negatively affect survival rate, respiration rate, hatching success and development (Wang et al., 2018). For example, survival rates of Oithona similis nauplii and adults were significantly decreased by 20 and 40% at 700 and 1000 μatm, respectively, compared to the control treatment (370 μatm) (Lewis et al., 2013). Similar effects have also been observed in Acartia tonsa (Cripps et al., 2014), where elevated pCO2 (1000 μatm) affected adult and nauplii survival rates. Based on previous studies, it has been suggested that the earlier developmental stages of copepods, especially the nauplii stage, are the most sensitive to ocean acidification (Wang et al., 2018). On the other hand, the effect of temperature on the physiological performance of several marine invertebrate species has been widely documented (Clarke, 1987; Thatje and Hall, 2016; Colpo and Lopez-Greco, 2017). In ectotherms, higher temperatures lead to an increased metabolism (e.g. higher respiration rate) (Thompson et al., 2019). In copepods, temperature directly affects the respiration and growth rates, accelerating them at increased temperatures and decreasing/delaying them with decreasing temperatures (Escribano et al., 1997; Montory et al., 2018; Heine et al., 2019; Hamre et al., 2019; Scheffler et al., 2019). Elevated temperatures shortened the developmental time and life cycle of the salmonid ectoparasite, Lepeophtheirus salmonis in the northern hemisphere (Groner et al., 2016; Hamre et al., 2019). For this ectoparasite, temperature has a particularly marked effect on the duration of the non-infective stages (nauplius I and II), varying from 50.0 h at 15 °C to 223.3 h at 5 °C, (Tully, 1992). Similar results with different temperature treatments have also been recorded for the copepod ectoparasite Caligus rogercresseyi (González and Carvajal, 2003; Montory et al., 2018), a response that could drastically affect the epidemiology of this ectoparasite.
Growing evidence shows that environmental drivers act synergistically, affecting many of the physiological processes of marine organisms (Gooding et al., 2009; Duarte et al., 2014). This highlights the importance of evaluating the combined effects of multiple environmental stressors (Darling and Cote, 2008; Pankhurst and Munday, 2011; Todgham and Stillman, 2013). Recent studies have shown that the effects of increased CO2 could be modified by a rise in temperature (Gooding et al., 2009; Findlay et al., 2010; Navarro et al., 2016). It has been reported that elevated seawater CO2 narrows the thermal tolerance window of an organism (Pörtner, 2008; Pörtner and Farrel, 2008). In this sense, Metzger et al. (2007) found that at elevated seawater CO2 concentrations, the upper thermal tolerance limits were reduced by several degrees Celsius in crustaceans. Calcified and non-calcified species exposed to high pCO2 are vulnerable to hypercapnia and acidosis (Melzner et al., 2009), demanding the reallocation of energy from fitness related traits (development, growth and reproduction) to acid-base regulatory processes in order to maintain homeostasis. These responses can also be exacerbated by an increase in the environmental temperature (Wang et al., 2018).
Sea lice are ectoparasitic copepods of the family Caligidae, have become one of the main problems for salmon farming worldwide, threatening the productivity of both salmon and trout farming (Burridge et al., 2014). In the future, this situation may be even more critical, with some authors suggesting that one of the impacts of climate change on aquaculture will be an increase in the incidence of diseases and parasites (Ruby and Ahilan, 2018). This ectoparasitic copepod attaches to the skin of its host to feed on mucus, generating wounds and therefore exposing fish to secondary infections, even leading to death at high infestation levels (Pike and Wadsworth, 1999; Costello, 2009; Valdés-Donoso et al., 2013; Oelckers et al., 2014). This in turn, increases production costs by extending the period to harvest and the handling time involved in the application of antiparasitic treatments (Bravo, 2003; Johnson et al., 2004; Costello, 2009; Agusti et al., 2016; Urbina et al., 2019), in addition to the treatment cost itself. In Chile, the main sea louse species is C. rogercresseyi (Boxshall and Bravo, 2000). The life cycle of this parasite involves eight stages, three non-feeding (lecithotrophic) free-living larval stages (2 nauplii and 1 copepodid) followed by 5 parasitic stages (4 chalimus and 1 adult) (González and Carvajal, 2003).
The present study aims to evaluate the combined effects of different pCO2 levels and temperatures on hatching time, duration of the pelagic development, survival, size and respiration for the free-living larval stages of C. rogercresseyi (nauplii and copepodid stages). We hypothesize that increases in temperature and acidification of seawater will negatively impact the early pelagic stages of the ectoparasite C. rogercresseyi.
Section snippets
Obtaining and maintenance of egg strings
Adults of C. rogercresseyi were collected from a salmon farm in southern Chile (Puerto Montt, Seno Reloncaví, 41.5–43° S), and transported to the Universidad Austral de Chile (Puerto Montt, Chile). Once in the laboratory, adults were allowed to infest Atlantic salmon, Salmo salar, under controlled environmental conditions (32 psu filtered seawater at 12 °C). We used the second batch of egg strings generated by females of C. rogercresseyi after their acclimation to the laboratory conditions (±45
Hatching time
Hatching time was affected by temperature (χ2 = 8.192; P = 0.016, Fig. 1), but not by pCO2 (χ2 = 2.015; P = 0.155) nor by the interaction between pCO2 and temperature (χ2 = 2.249; P = 0.324). Hatching time was longer at 10 °C (60.7 ± 20.7 h; test a posteriori, P < 0.05) than at 20 °C, with a mean hatching time of 47.9 ± 12.8 h at both pCO2 levels (Fig. 1). Larvae hatched at 15 °C presented an intermediate hatching time (50.7 ± 17.2 h).
Survival of free-living stages (nauplius I and II)
There were no significant effects of pCO2 (χ2 = 0.04; P
Discussion
Although pCO2 and temperature effects have been studied before, little is known about the stage-specific responses to these stressors during the life cycle of ectoparasitic copepods (Kurihara and Ishimatsu, 2008; Kita et al., 2013; Hildebrandt et al., 2014; Wang et al., 2018). It is known that the early developmental stages of many marine species display the greatest sensitivity to pCO2 and temperature stress as isolated stressors (Dupont and Thorndyke, 2009; Kroeker et al., 2010; Montory et
CRediT authorship contribution statement
Jaime A. Montory: Project administration, Conceptualization, Methodology, Formal analysis, Data curation, Writing - original draft. Juan P. Cumillaf: Investigation, Writing - review & editing. Paulina Gebauer: Conceptualization, Formal analysis, Writing - review & editing. Mauricio Urbina: Investigation, Data curation, Formal analysis, Writing - review & editing, Supervision. Víctor M. Cubillos: Investigation, Formal analysis, Writing - review & editing. Jorge M. Navarro: Formal analysis,
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.
Acknowledgments
This research was supported by a PAI project N° 79150046 to J.A.M. and P.G., M.U received financial support from a CONICYT-FONDECYT grant 11160019, J.M.N. from CONICYT-FONDECYT grant 1161420 and J.A.M. from CONICYT-FONDECYT grant 11190720. The authors thank Dr. M. Lee for his help reviewing English.
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