Abstract
Predicting the response of populations to climate change requires knowledge of thermal performance. Genetic differentiation and phenotypic plasticity affect thermal performance, but the effects of sex and developmental temperatures often go uncharacterized. We used common garden experiments to test for effects of local adaptation, developmental phenotypic plasticity, and individual sex on thermal performance of the ubiquitous copepod, Acartia tonsa. Females had higher thermal tolerance than males in both populations, while the Florida population had higher thermal tolerance compared to the Connecticut population. An effect of developmental phenotypic plasticity on thermal tolerance was observed only in the Connecticut population. Ignoring sex-specific differences may result in a severe underestimation of population-level impacts of warming (i.e. - population decline due to sperm limitation). Further, despite having a higher thermal tolerance, southern populations may be more vulnerable to warming as they lack the ability to respond to increases in temperature through phenotypic plasticity.
Introduction
Temperature has a profound effect on organismal performance [1,2]. Rapid climate warming represents a significant challenge for organisms, increasing average environmental temperatures [3] and the frequency of extreme climatic events (i.e. - heat waves) [4]. Predicting organismal responses to these changes depends on our understanding of the factors affecting thermal tolerance. Acute thermal tolerance is known to be affected by phenotypic plasticity [5] and genetic differentiation [6], as well as diet, behavior and individual sex [7,8,9]. Spatial variation in the thermal environment should generate adaptive differences in thermal performance between populations from different environments [2]. The Climate Variability Hypothesis (CVH) [10,11] states that increased thermal tolerance should correspond with increased mean environmental temperature, while plasticity should evolve in response to variability in the thermal environment. This is supported in terrestrial and freshwater aquatic systems [12, 13], but there have been fewer tests in marine systems [14,15,16], yielding only limited support. Additionally, no tests of the CVH have examined how individual sex factors into observed variation in thermal performance.
Here we examine the effects of genetic differentiation, developmental phenotypic plasticity, and individual sex on thermal tolerance in the widespread copepod Acartia tonsa. This species dominates coastal and estuarine systems around the globe. With a geographic range covering a large latitudinal thermal gradient, this is a good model system to explore the contributions of various adaptive mechanisms to thermal adaptation [15]. Our results show that complex interactions between these variables strongly affect our ability to predict organismal responses to climate change.
Methods
Plankton samples were collected from surface tows at field sites in Groton, Connecticut, and Punta Gorda, Florida (Table 1) during July and August of 2017 using a 250 um mesh plankton net. Temperature data for both sites was obtained from the AQUA-MODIS satellite database [17]. Initial laboratory populations, comprised of >1500 mature adults to minimize the effects of genetic drift, were established from collected animals. Cultures were maintained under common garden conditions (30 psu, 12:12 light:dark, 18°C) for several generations, and fed a diet of the microalgae Tetraselmis sp., Rhodomonas sp., and Thalassiosira weissflogii. Eggs were collected from the 18°C culture and moved to 22°C to develop. All other factors were held constant. Once mature, individuals from both developmental conditions (18 and 22°C) were exposed to a 24-hour acute heat stress. Individuals were carefully transferred to a microcentrifuge tube with 1.5 mL of filtered seawater, then transferred to heat blocks set to a constant temperature (18-38°C at degree intervals). Each individual experienced a single temperature. Individual survivorship was measured after 24 hours as binary data (1 = survival, 0 = mortality).
All analyses were performed using R version 3.5.1 [18]. 1717 individuals were used throughout the experiments. Initially, an ANOVA was run for all data (Survivorship ~ Stress Temperature + Sex + Developmental Temperature + Population, and all two-way interactions). Three-way and four-way interaction were excluded from the ANOVA. ANOVAs were also run for each population separately (Survivorship ~ Stress Temperature ∗ Sex ∗ Developmental Temperature). Thermal performance curves were estimated using logistic regressions. Because of the common garden design, differences in the performance curves between developmental conditions within a population can be attributed to developmental phenotypic plasticity, whereas differences between populations should reflect the effects of genetic differentiation. LD50 (the temperature with 50% mortality) was calculated for each performance curve. The change in LD50 between the two developmental conditions (ΔLD50) was used as a measure of the magnitude of the plastic response.
Results
Statistical analyses – In the full ANOVA, significant effects of stress temperature, sex, developmental temperature and population, as well as significant stress temperature x population and developmental temperature x population interaction terms were evident (Table 2). Sex, stress temperature and developmental temperatures were significant in the Connecticut population, with no significant interaction terms. By contrast, only stress temperature and sex and their interaction were significant in the Florida population.
Thermal performance curves - Males showed lower survival than females in both populations (Fig. 1, red versus blue lines). Developmental temperature had a strong effect on survival in the Connecticut population, but not in the Florida population.
Reaction norms –
Thermal tolerance (LD50) reaction norms show clear sex-dependent differences in thermal tolerance (Fig. 2), with females being always more tolerant than males. Higher developmental temperature increased thermal tolerance in the Connecticut population, but not in the Florida population. However, there were no sex-dependent differences in the plastic response between males and females (no difference in slopes), regardless of population.
Discussion
The two populations of Acartia tonsa used in this study were collected from strongly differing thermal environments - a cool, variable environment (Connecticut), and a warmer, more stable environment (Florida). We observed lower thermal tolerance, but stronger plasticity in the Connecticut population relative to the Florida population, consistent with expectations of the CVH [10,11]. However, we find that individual sex had the largest effect on thermal tolerance. The demographic implications of these results are crucial to consider in predictions of future population dynamics.
In both populations, females always had a higher thermal tolerance than males. Sex-specific differences in thermal tolerance are observed across diverse systems [8, 19-21]. Within copepods, the few studies that have examined sex-specific thermal tolerance have also found females to be more thermally tolerant than males [9, 22-24], but ours is the first to examine these differences in more than one adaptive mechanism (thermal tolerance and phenotypic plasticity), and in multiple populations. Interestingly, Acartia tonsa females have also been found to be more tolerant to toxic dinoflagellates and to starvation [25, 26]. While there are strong differences in male and female thermal tolerance in this study, neither population exhibits significant differences between male and female plastic capacity (ΔLD50). No previous studies have examined differences in male and female developmental phenotypic plasticity, but higher acclimatory capacity was observed in females in a different copepod species [9]. This difference in sex-dependence of the different adaptive mechanisms suggests that their physiological basis is different.
Multiple factors affect acute thermal stress tolerance. Understanding these factors, and how they vary among populations, has critical implications for predictions of future population dynamics. Lower male thermal tolerance creates an asymmetrical vulnerability to climate change, which could lead to population declines under less intense warming due to sperm-limitation [27]. Our results also suggest that, despite having a higher thermal tolerance, southern populations may be more vulnerable to predicted warming. The southern population exists near their thermal limit under present conditions. As they are also unable to respond to increased temperatures through developmental phenotypic plasticity, any further increase in temperature is likely to have significant negative effects on population survival. Furthermore, males have a significantly lower thermal tolerance, lowering the temperature threshold that would bring the onset of temperature-driven population dynamic changes. Both sexes in the Connecticut population, however, have thermal tolerance values well above the current temperature maximum, and have a robust plastic capacity to increase thermal tolerance, potentially decreasing deleterious effects of warming on this population. Without examining multiple adaptive mechanisms and factors affecting thermal tolerance in several different populations, the complex variation in vulnerability to warming cannot be predicted.
Author Contributions
M.S. collected and cultured all copepods. H.G.D. and M.S. designed the study. K.R. and S.H. performed the experiments. M.S. analyzed the data. M.S. and H.G. Dam drafted the manuscript.
Data Accessibility
All data is accessible on Dryad (doi:10.5061/dryad.v5g6r80)
Funding
Supported by NSF grants 1559180 and 1658663, a Research Council grant, and graduate research fellowships from the University of Connecticut.
Competing Interests
We have no competing interests.
Ethics Statement
Permits to collect individuals were not required. Standard protocols were used for copepod culturing and thermal tolerance assays. Ethics committee approval was not required.
Acknowledgments
S.H. and K.R. were UCONN-Mystic Aquarium REU Program participants. We’d like to thank Drs. Tracy Romano and Michael Finiguerra for organizing this program.