Abstract
Understanding how growth trajectories of calcifying invertebrates are affected by changing climate requires acclimation experiments that follow development across life-history transitions. In a long-term acclimation study, the effects of increased acidification and temperature on survival and growth of the tropical sea urchin Tripneustes gratilla from the early juvenile (5 mm test diameter—TD) through the developmental transition to the mature adult (60 mm TD) were investigated. Juveniles were reared in a combination of three temperature and three pH/pCO2 treatments, including treatments commensurate with global change projections. Elevated temperature and pCO2/pH both affected growth, but there was no interaction between these factors. The urchins grew more slowly at pH 7.6, but not at pH 7.8. Slow growth may be influenced by the inability to compensate coelomic fluid acid–base balance at pH 7.6. Growth was faster at +3 and +6°C compared to that in ambient temperature. Acidification and warming had strong and interactive effects on reproductive potential. Warming increased the gonad index, but acidification decreased it. At pH 7.6 there were virtually no gonads in any urchins regardless of temperature. The T. gratilla were larger at maturity under combined near-future warming and acidification scenarios (+3°C/pH 7.8). Although the juveniles grew and survived in near-future warming and acidification conditions, chronic exposure to these stressors from an early stage altered allocation to somatic and gonad growth. In the absence of phenotypic adjustment, the interactive effects of warming and acidification on the benthic life phases of sea urchins may compromise reproductive fitness and population maintenance as global climatic change unfolds.
Keywords: climate change, sea urchin, ocean warming, life-history transition
1. Introduction
Marine species are experiencing coasts and oceans that are simultaneously warming and decreasing in pH with the magnitude of change differing among world regions [1]. Climate warming is driving marked responses in many marine ectotherms including shifts in species distributions, as seen in the poleward range extension of species as they follow their thermal niche [2]; changes in phenology, as seen in the altered timing of spawning and plankton blooms [3]; and declining body size [4]. Ocean acidification is accompanied by covarying stressors; increasing pCO2 causes organism hypercapnia and can result in metabolic suppression and energetic stress, while the accompanying decrease in calcium carbonate mineral saturation impairs calcification and growth, and hence decreasing body size, and a ‘dwarfing effect’ is reported and/or expected [5–7]. Where the synergy between warming and acidification has been investigated the outcomes for marine ectotherms can be complex, with some species being more vulnerable than others [6,8,9].
Marine calcifiers represent a vast diversity of species, and several meta-analyses show their high vulnerability to acidification, with reports of impaired growth of larval, juvenile and adult stages in studies involving single life stages of taxa that calcify in their larval and benthic life phases [6,9,10]. It is important to understand how warming and acidification will interact to affect survival, growth, size at maturity, reproductive output and other proxies of fitness. Temperature and pCO2/pH can interact, as seen in the positive buffering effect of increased temperature on growth and calcification in near-future acidification in long-term (months) studies, or can act synergistically in a negative way when tolerance thresholds are breached [9,11–14]. Understanding how growth trajectories are affected by changing ocean conditions and prospects for population persistence requires acclimation experiments that follow the response to these factors across life-history transitions such as reaching reproductive maturity.
It is not known if it will be possible for marine species to acclimate to changing ocean conditions to maintain growth levels into the future. We used the fast-growing tropical sea urchin, Tripneustes gratilla as a model species to investigate the effects of acidification and warming on the life-stage transition from the post-metamorphic juvenile to the mature adult in a long-term acclimation study. The urchins were reared from the very early juvenile (5 mm test diameter, TD) through the gonad development stage (approx. 600 mm TD). This species is also an important fishery and aquaculture species, the latter due to its fast growth [15,16]. In T. gratilla the decrease in the thickness of the test and its crushing resistance following long-term rearing at pH 7.8 is mitigated by near-future warming, but not at greater acidification [17]. For the juveniles of calcifying species the interaction between increased acidification and temperature on skeleton formation is positive for some species [18–20], but not others [11,21]. For adult sea urchins, exposure to anthropogenic (CO2 dosing experiments) and biogenic (respiratory CO2) acidification can have a negative effect on body and gonad growth [16,22], although the negative effects of acidification on reproduction can be reduced in longer-term incubations [23,24]. Maintenance of organism acid–base balance is crucial for physiological function and is a significant energetic cost that affects energy partitioning between fitness traits such as growth and reproduction [25]. Several studies have shown that sea urchins can maintain their acid–base balance at near-future levels of acidification, but this is likely to be energetically costly [26,27], especially in combination with warming [28].
There are no studies that have reared post-metamorphic benthic calcifiers to reproductive maturity under ocean warming and acidification conditions to assess how chronic long-term exposure to these stressors interact to impact on body and gonad growth, as proxies of fitness. This knowledge gap is addressed here with T. gratilla reared to reproductive maturity in a factorial combination of three temperature and three pH/pCO2 treatments, commensurate with projections for southeast Australia [29,30]. Survival, growth, internal pH and gonad production as a proxy of both nutritive condition and reproductive potential were determined. Given the negative effect of acidification on calcification and growth of echinoids on one hand, especially juveniles [31], and the positive effect of warming on the other [32], we expected to see a complex interplay between these factors with respect to the growth trajectories of T. gratilla. We predicted that impaired growth due to acidification would be ameliorated by near-future warming, as seen for T. gratilla larvae (e.g. [33]). However, if greater warming breached thermal tolerance limits, or if there is a negative effect of temperature on size even below thermal maxima such that the ‘temperature–size’ rule (TSR) applies for this species, we expect growth would be impaired [4,34]. The stunting effect of warming was expected to be exacerbated by acidification. As the gonad functions as the major nutrient storage organ in sea urchins [35], we predicted that energetic constraints imposed by acidification and warming would have a negative effect on its development. We also predicted that T. gratilla would be able to maintain its coelomic acid–base balance at moderate, but not more extreme acidification and warming.
2. Material and methods
(a). Larval and juvenile rearing
Tripneustes gratilla were collected from South Solitary Island, New South Wales (30° 12′ S, 153° 16′ E). Fertilization was conducted using pooled gametes from three males and three females induced to spawn by injection of 2–3 ml of 1M KCl. The embryos were cultured in 300 l larval rearing containers and the larvae were fed Proteomonas sulcata [36]. Competent larvae were settled in 60 l tanks containing aerated seawater and preconditioned with naturally derived biofilms, which provide a settlement cue and post-larval food. Flow-through seawater was introduced to the tanks after 48 h. The juveniles were weaned onto a diet of fresh Sargassum sp. They were used in the experiment at roughly 8 weeks post-settlement (mean 5.17 mm test diameter—TD, s.e. = 0.2, n = 42) and provided food in excess until the end of the experiment on day 147 (approx. 5 months).
(b). Experimental set-up
The juveniles were placed in individual rearing containers in flow-through treatments of three temperature (control = 22°C, +3°C = 25°C, +6°C = 28°C) and three pHNIST treatments (control = 8.1, −0.3 pH units = 7.8, −0.5 pH units = 7.6) crossed in all combinations (see electronic supplementary material, table S1), with seven replicates for each treatment combination. The treatment levels were based on near-future (2070–2100) and far-future (2300) projections for changes in local surface seawater based on the reduced (RCP 4.5) and business-as-usual (RCP 8.5) emissions scenarios [1]. However, the 3°C level of warming occurs during El Niño years in the region for protracted periods [37], indicating that near-future sea temperatures could occasionally approach +6°C.
The pCO2/pH of experimental water was manipulated in 60 l header tanks supplied with flow-through seawater maintained at a constant volume using float valves. Seawater pCO2/pH was lowered in two of the header tanks (pH 7.8 and 7.6) by injection of pure CO2 dissolved using a vortex mixer (Red Sea). Acidification conditions were controlled by a pH probe connected to a pH controller, solenoid valve, regulator (Tunze 7070/20) and CO2 cylinder. A third 60 l header tank was not injected with CO2 and tracked ambient pCO2/pH. Air was bubbled into all headers to aid mixing, and maintain dissolved oxygen levels greater than 95%. Seawater from each header tank flowed to three separate 12 l subtanks where temperature was manipulated. Temperature was controlled using 200 W thermostatically controlled aquarium heaters (Jager). Water in the subtanks was supplied to rearing container through agricultural irrigation dripper taps (Antelco). Temperature and pH were measured daily in the rearing containers and the water supply adjusted to maintain target levels.
Water conditions (pH, temperature, salinity) were monitored and measured in approximately 5 haphazardly selected rearing containers per treatment per day with a WTW Multimeter (MultiLine P4) (electronic supplementary material, table S1). Samples for total alkalinity (TA) were collected regularly and were filtered (0.2 µm) and fixed with saturated HgCl. TA was measured by potentiometric titration and the results were checked against standard reference material [38]. Experimental pCO2 was determined from TA, pHNIST and salinity data using CO2SYS [39] using the dissociation constants of Mehrbach [40] as refitted by Dickson & Millero [41] (electronic supplementary material, table S1).
Individual juveniles (seven replicates per treatment) were placed in rearing containers that consisted of 100 ml sample jars with a window that acted as an overflow that maintained the water volume at 30 ml. The rearing containers were supplied with a constant flow of seawater with a turnover rate of greater than 100 container volumes per day. As the urchins grew, they were transferred to 200 ml and then 500 ml containers. Flow rates were increased with size of the container to maintain a water turnover rate of greater than 100 volumes per day. The urchins were fed fresh Sargassum sp. in excess. Rearing containers were cleaned of faeces and uneaten seaweed daily or as needed.
(c). Growth
At approximately weekly intervals each urchin was photographed with a scale and the average of three radial diameters measured using ImageJ (NIH). Their wet weight was measured to the nearest mg after they were placed on absorbent paper towelling for 15 s to remove excess water. This was only done four times throughout the experiment to minimize stress on the animals.
(d). Gonad index and coelomic fluid pH
At the end of the experiment TD and wet weights were recorded before the urchins were dissected to obtain coelomic fluid for immediate measurement of pH using the WTW Multimeter and to remove the gonads. The gonad index was calculated as gonad wet weight, as a percentage of the wet weight of the whole sea urchin.
(e). Statistical analysis
Growth, cumulative increase in diameter and weight date were analysed by permutational analysis of covariance (PERMANCOVA), with initial diameter and weight used as covariates, and temperature and pH as fixed factors. Data for parameters measured at the end of the experiment, weight, gonad index and coelomic fluid pH, were analysed using permutational analysis of variance (PERMANOVA). Post hoc pairwise comparisons were used to determine differences between treatments. All analyses were done using the statistical package Primer + PERMANOVA.
3. Results
(a). Survival and growth
There were six mortalities, but no more than a single mortality in each treatment. The juveniles grew from a mean of 5.17 mm (±0.2 mm s.e., n = 42) to a mean of 562 mm (±23 mm s.e., n = 36) TD by day 147 (figures 1 and 2). Elevated temperature and pCO2/pH both affected growth (change in diameter/initial diameter), but there was no interaction between these factors (figures 1 and 2; PERMANCOVA with initial size as a covariate; temperature, F2,48 = 57, p < 0.0001; pH, F2,48 = 7.9, p < 0.0001; temperature × pH, F4,48 = 07, p = 0.6; electronic supplementary material, table S1). When compared with ambient pH 8.15, T. gratilla grew more slowly in diameter at pH 7.6, but not at pH 7.8 (post hoc pairwise test; figures 1 and 2). At the end of the experiment the urchins were larger at the higher temperatures than the ambient, with no difference between the two highest temperatures (post hoc pairwise test; figures 1 and 2; electronic supplementary material, table S1). Wet weight followed a similar pattern as diameter (figure 3a). Increased growth in the warm treatments offset the negative effects of acidification (figures 1–3a). Tripneustes gratilla were 50% lighter when reared at pH 7.6 and ambient temperature, compared with ambient pH and temperature, but were 166% heavier when reared under acidification (pH 7.6) and moderate warming (+3°C) (figure 3a; electronic supplementary material, table S1).
Figure 1.
Photo taken on the last day of the experiment (day 146) showing the indicative effect of pH and temperature on the growth of Tripneustes gratilla. Sea urchins started at approximately the same initial size (5.02 mm test diameter ±0.08 s.e.). Sea urchins aligned horizontally were from the same pH treatment, and those aligned vertically were from the same temperature treatment. (Online version in colour.)
Figure 2.
Effect of (a) pH and (b) temperature on the mean cumulative growth in diameter of Tripneustes gratilla. The data are presented pooled with respect to pH and temperature treatments to aid interpretation as both factors had independent significant effects on growth when analysed at the end of the experiment. Lines next to the figure legend represent significant difference (post hoc pairwise test p > 0.05). Data are means ± s.e., n = 12–14.
Figure 3.
Effect of pH and temperature on Tripneustes gratilla after 146 days in culture as (a) wet weight, (b) gonad index and (c) coelomic fluid pH. The symbols (=, >) or letters indicate significant difference in post hoc pairwise tests—see results. Data are means ± s.e., n = 6–7.
(b). Reproductive potential
Acidification and warming had a strong and interactive effect on nutritive condition and reproductive potential as measured by the gonad index (PERMANOVA; temperature, F2,48 = 13.5, p = 0.0002; pH, F2,48 = 12.7, p = 0.0001; temperature × pH F4,48 = 2.9, p < 0.03; electronic supplementary material, table S1; figure 3b). Warming increased the gonad index, but acidification decreased it (figure 3b). At pH 7.6 there were virtually no gonads in any urchins regardless of temperature (figure 3b). At the end of the experiment fewer sea urchins had gonads in the ambient-temperature treatment (14%) than the high-temperature treatments (79%, 83%, respectively, and 100% if the pH 7.6 treatments are excluded).
(c). Internal pH
Coelomic fluid pH was affected by acidification and warming with no interaction between these factors (PERMANOVA; temperature, F2,48 = 6.8, p = 0.003; pH, F2,48 = 7.4, p = 0.002; temperature × pH F4,48 = 1.5, p = 0.22; electronic supplementary material, table S1; figure 3c). The urchins were able to compensate internal pH in moderate (pH 7.8), but not at greater acidification (pH 7.6) (figure 3c). Coelomic fluid pH was lower in the higher-temperature treatments.
4. Discussion
As warming and acidification of marine habitats continues to unfold, it is not known how these combined stressors will interact to affect survival, growth, size at maturity and other proxies of fitness of marine ectotherms. In this first study to examine how these stressors interact to affect the juvenile to adult life-stage transition of a benthic calcifier, we show the utility of the multifactorial approach and the importance of considering the interplay between fitness traits in predicting species' responses to changing climate. In parallel with the trend seen for many calcifiers, near-future acidification reduced body size in T. gratilla, while near-future warming mitigated this effect. However, this mitigation was not as effective with respect to gonad growth, and not at all with respect to acid–base balance. Although the juveniles grew and survived in near-future warming and acidification conditions, chronic exposure to these stressors from an early age altered allocation to somatic and gonad growth in a positive or negative way, depending on the stressor combination.
Temperature alone had a positive effect on growth. Tripneustes gratilla in the 25°C and 28°C treatments were larger and heavier, and also had a more robust test, due to the increased skeletal growth and, as shown previously, potentially due to altered mineralogy (increased MgCO3) [17]. As more tropical populations of this species experience these temperature levels, these outcomes might be expected. Our results contrast with those found for bivalves, where moderate warming reduced shell growth and strength [42]. Moderate warming had a positive effect on gonad growth in T. gratilla, while the warmest treatment showed evidence of reduced growth of this organ. Thus, while warming had a positive effect on body size, there was a limit to thermal facilitation of gonad production. Similarly, adult urchins in long-term warming (approx. +3°C) experiments (Paracentrotus lividus, 3 months; Echinometra sp., 2.5 months; Evechinus chloroticus 3 months) exhibit impaired gonad development [22,43,44]. Increasing temperatures are a major physiological stress for T. gratilla and other sea urchins with increased susceptibility to disease and mortality as the ocean warms [45,46].
Acidification alone, especially at pH 7.6, had a negative effect on body and gonad growth in T. gratilla, as also seen for calcification in this and other sea urchin species [17,22,25,31,47]. Moderate acidification (pH 7.8) was not so stressful, perhaps because this level approaches the conditions occasionally experienced in nature. Acidification was particularly deleterious to gonad growth. Along with reduced body size, this indicates an altered nutritive state and energy partitioning to development of this important storage organ.
The impacts of combined warming and acidification on body and gonad growth in T. gratilla were complex. Amelioration of the negative effect of acidification on growth in size and weight and calcification in T. gratilla [17] was limited to the near-future scenario (+3°C/pH 7.8). The negative effects of acidification on gonad growth were not mitigated by this level of warming. At higher stress levels T. gratilla were smaller and had poorly developed or no gonads, as seen for other sea urchins [25,44,47]. Despite being provided with excess food, it seems that T. gratilla was not able to maintain its growth and reproductive potential at high acidification and warming. This is counter to the observation that the deleterious effects of acidification can be compensated by high food conditions [48]. At pH 7.6, regardless of temperature, gonad development was reduced and in some individuals inhibited.
The T. gratilla were able to compensate their acid–base balance in moderate acidification but less so in the lowest pH treatment, as reported for other sea urchin species [22,25,27,49]. Increased temperature caused acidification of the coelomic fluid, probably due to increased respiratory acidosis of the coelom. The inability of T. gratilla reared to adulthood in warm–low pH conditions to compensate for internal acidosis is likely to have contributed to their reduced performance. Key functions such as growth and reproduction are negatively impacted by these stressors due direct impacts on metabolism and the energetic demands to maintain body acid–base balance for functions such as calcification and enzyme activity [25,26,31]. Increased temperature and acidification have an additive effect in increasing respiration in sea urchins [22,28]. It will be important to understand the metabolic responses of T. gratilla and other sea urchins reared to the adult stage in changing ocean conditions to determine if phenotypic adjustment over time is possible to maintain growth and production at present-day levels.
The duration of marine climate change experiments can influence outcomes as short-term incubations may overestimate effects when organisms do not have time to physiologically acclimatize to changing conditions [25]. For instance, acidification has a negative effect on gonad growth in sea urchins at 4-month but not 16-month exposure [23], although this would be influenced by the gametogenic state of the gonad at the onset of incubation. Adult urchins are able to adjust their reproductive output to control levels following long-term acclimation (years) to acidification and warming [24]. In both of these studies the experimental subjects were fully grown adult urchins with differentiated gonads. As shown here, the outcome is likely to differ when experiments involve juvenile urchins from first gonad development. We do not know if the urchins reared at pH 7.6 would eventually develop viable gonads with longer rearing. Given more time the controls would have developed larger gonads.
Reduced reproductive output of T. gratilla in response to warming and acidification have negative consequences for population persistence. This concern is compounded given the sensitivity of T. gratilla and other sea urchins to climate change stressors during their larval phase [10,33]. Given the sensitivity of invertebrate calcifiers to acidification and warming as larvae, decreased reproductive output by adults combined with poor larval survival may pose a serious bottleneck for survival of many benthic species in the future [9].
It is predicted that ocean acidification and warming will combine to exacerbate body size reductions in marine ectotherms as a universal impact of global change [4]. The ‘temperature–size’ rule (TSR) posits that ectotherms are smaller as adults when they develop through their life at elevated temperatures [50], as seen in the reduced body size of aquatic ectotherms due to contemporary warming [51]. Our results with T. gratilla do not support this and highlight that the TSR does not hold for all species [52], and may be context-dependent. Increasing temperatures have a nonlinear effect on ectotherms, initially elevating metabolic rates and facilitating growth with moderate warming up to thermal limits when growth decreases [4]. The expectation is that decreased body size will also be attributed to the impact of acidification where the energetic constraints to produce a skeleton under hypercapnic and lower carbonate mineral saturation conditions impair calcification and growth [4,6,7,10,31]. This is evident at CO2 vent sites where calcifiers are smaller than in non-vent sites [52]. Our data for T. gratilla indicate that while warming can mitigate the stunting effects of acidification, there is a limit to this. Indeed, temperatures above the levels used here (29°C) impair growth of this species.
A major caveat of our results and much of current marine climate change research is that we tested how present-day genotypes respond to future stressors. It is likely that increased environmental stress will result in genetic change and possible adaptation [53]. A major challenge will be to understand how organisms might adapt to future multiple environmental stressors [54]. In addition, T. gratilla is a very widely distributed species with a large metapopulation across the tropics. Our juveniles were the progeny of high-latitude/range-edge parents with a comparatively ‘cool’ environmental history. It will be important to understand the tolerance of more tropical populations to increased temperature and acidification. However, in the absence of phenotypic adjustment, the interactive effects of warming and acidification on the benthic life phases of T. gratilla and other benthic calcifiers may compromise reproductive fitness and population maintenance as global climatic change unfolds.
Supplementary Material
Supplementary Material
Acknowledgements
Thanks are expressed to Benjamin Mos and Sam West for assistance.
Ethics
Under local guidelines no ethics approvals were needed to conduct this research.
Data accessibility
The datasets supporting this article are available in electronic supplementary material and from the Dryad Digital Repository (doi:10.5061/dryad.qc3m7) [55].
Authors' contributions
S.A.D. and M.B. conceived and designed the experiments, analysed the data and wrote the manuscript. S.A.D. preformed and managed the experiments.
Competing interests
We declare we have no competing interests.
Funding
This work was supported by grants from the New South Wales Environmental Research Trust and the Australian Research Council to S.A.D. and M.B.
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Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Data Citations
- Dworjanyn SA, Byrne M. 2018. Data from: Impacts of ocean acidification on sea urchin growth across the juvenile to mature adult life-stage transition is mitigated by warming Dryad Digital Repository. ( 10.5061/dryad.qc3m7) [DOI] [PMC free article] [PubMed]
Supplementary Materials
Data Availability Statement
The datasets supporting this article are available in electronic supplementary material and from the Dryad Digital Repository (doi:10.5061/dryad.qc3m7) [55].



