The pre-conditioning of adult marine invertebrates to altered conditions, such as low pH, can significantly impact offspring outcomes, a process which is often referred to as transgenerational plasticity (TGP). This study describes for the first time, the gene expression profiles associated with TGP in the green sea urchin Psammechinus miliaris and evaluates the transcriptional contribution to larval resilience. RNA-Seq was used to determine how the expression profiles of larvae spawned into low pH from pre-acclimated adults differed to those of larvae produced from adults cultured under ambient pH. The main findings demonstrated that adult conditioning to low pH critically pre-loads the embryonic transcriptional pool with antioxidants to prepare the larvae for the “new” conditions. In addition, the classic cellular stress response, measured via the production of heat shock proteins (the heat shock response (HSR)), was separately evaluated. None of the early stage larvae either spawned in low pH (produced from both ambient and pre-acclimated adults) or subjected to a separate heat shock experiment were able to activate the full HSR as measured in adults, but the capacity to mount an HSR increased as development proceeded. This compromised ability clearly contributes to the vulnerability of early stage larvae to acute environmental challenge.
To make accurate predictions about the resilience of biodiversity in the future, it is essential to understand the cellular mechanisms that underpin species’ responses to change. Evaluations at the molecular level provide a priori clues as to how these responses vary between species and suggest who will be the winners and losers under changing conditions1. In the marine field, much of the early work manipulating pH and CO2 in marine systems, popularly known as Ocean Acidification (OA), has concentrated on early developmental stages (embryos and larvae), as these are potentially the most vulnerable part of the life cycle and key to continued population success2. However, many of these early experiments used adults from the wild and spawned them in present day pH sea water. The resulting larvae were then directly decanted into lowered pH sea water and their development monitored. Whilst these types of experimental manipulation mimic the effect of seasonal, episodic high pCO2 upwelling, such as that observed along the US western coast3,4, they do not mirror the real-time trajectory of climate change. These experiments exclude examination of the abilities of organisms to respond via phenotypic plasticity, developmental plasticity and transgenerational plasticity (TGP)1,5,6.
An increasing number of studies, many of them in sea urchin species, now show that adult acclimation to low pH prior to spawning can significantly impact larval success7,8,9,10. This is often called TGP, if both male and female parents are pre-acclimated and maternal conditioning or maternal provisioning if pre-acclimation is restricted to females only5,6. In a recent review of TGP in echinoderms and molluscs, the majority of studies reported beneficial effects, although neutral and negative effects were also recorded, with the authors acknowledging that such responses are complex to predict and often time-scale, taxa or species-specific5. For example, pre-acclimation of adult sea urchins to low pH, had deleterious effects on the reproductive success of the tropical Echinometra mathaei11. No effects were observed on the larvae of Echinometra species living on venting coral reefs from Papua New Guinea12. Mixed effects were discovered in the temperate Strongylocentrotus droebachiensis, which showed positive effects on egg size, no effect on female fecundity after prolonged pre-acclimation, but negative effects on F1 recruitment and juvenile survival7. In both the temperate Psammechinus miliaris and Antarctic Sterechinus neumayeri positive effects were observed on larval survival at low pH, especially if the whole reproductive cycle was included9,10. In a further study on sea urchins and pollution, maternal pre-conditioning of the temperate Evechinus chloroticus preloaded the resulting larvae with antioxidants to help mitigate against pollution-induced oxidative damage13. To emphasize the complexities of TGP responses, mortality was 100% before the blastula stage in embryos produced from low pH pre-acclimated adults of the cold water sea cucumber (Cucumaria frondosa) in the only study to date on lecithotrophic larvae14. The picture is even more complicated from a multi-stressor perspective, for example experiments (temperature and low pH) in the bivalves Mercenaria mercenaria and Agropecten irradians showed negative effects with pre-acclimated adults producing more vulnerable offspring15. Similarly studies using the Sydney rock oyster Saccostrea glomerata showed positive effects when low pH alone was investigated, but maladaptive responses to multiple stressors16. Additionally, the stage at which the embryos or larvae are introduced into low pH is also critical. Sea urchin larvae that were spawned and cultured up to the 4-arm stage in control conditions and then introduced to low pH were more robust than cleaving embryos introduced directly to low pH17,18,19. Thus predicting the outcomes from the experimental manipulation of environmental parameters in marine species is complex, with both parental conditioning and the stage at which the larvae are exposed to the new conditions both critical factors6.
In summary, most of the studies on TGP have described the morphological and developmental responses of the F1 generation. For cellular mechanisms underpinning these physiological responses, the number of examples is limited. Recent data on larvae spawned from adult populations of Strongylocentrotus purpuratus from across a latitudinal pH gradient and also populations pre-acclimated in the laboratory to low pH have demonstrated the upregulation of metabolic pathways redirecting ATP production towards enhancing acid-base homeostasis and ion regulatory capacity, but with potential cellular trade-offs20,21. Hence, there is still a significant knowledge gap of not only the differential gene expression underpinning TGP, but also larval robustness through development to altered conditions5.
In this study we analysed the gene expression profiles of early stage larvae from the green sea urchin Psammechinus miliaris raised under low pH (~1000 µatm). These larvae were produced from either adults raised under ambient conditions (~400 µatm) or pre-acclimated to low pH in IPCC year 2100 conditions (~1000 µatm) to evaluate the cellular level effect of parental conditioning. There was an expectation that larvae produced from adults cultured under ambient conditions and spawned directly into low pH would exhibit the classical stress response to new conditions, namely the heat shock response (HSR). This virtually ubiquitous cellular reaction involves the up-regulation of chaperone proteins, specifically members of the 70 kDa and 90k Da heat shock protein families (Hsp70 and Hsp90). These are highly conserved proteins that deal with the stress-induced denaturation of other cellular proteins22. The lack of such a response in the gene expression data was surprising. Therefore the ability of early stage larvae to mount an HSR was further investigated in a separate experiment where both adults and larvae were subjected to an acute heat shock and the resulting expression levels of nine hsp70 and hsp90 genes were evaluated by Q-PCR.
Gene network analyses in low pH
Expression profiles were produced from cohorts of larvae at 2, 3 and 4 dpf (days post fertilisation) raised in low pH (~1000 µatm). One set of these larvae were produced from adults cultured at ambient pH (~400 µatm) to mimic rapid pH transfer experiments, whilst a second set was produced from low pH acclimated adults to study the effect of parental acclimation. In each case the expression profiles were compared to larvae raised under ambient conditions and produced from adults kept under ambient conditions (controls at ~400 µatm). The number of annotated transcripts which were up-regulated in the treated samples was highly variable (Table 1), but in general, more transcripts at each time point were up-regulated in the samples where both the adults and the larvae were raised in low pH conditions. When these data were entered into the STRING program increasingly complex gene networks were produced over the time course (Supplementary Tables S1–S6).
Expression profiles for 2dpf larvae
Evaluation of the transcripts up-regulated in 2 dpf larvae produced from ambient adults and raised in low pH showed a small network centred on tubulin with connections to other genes involved in microtubule formation and cell division (coded yellow in Supplementary Table S1), indicating that the embryonic cells were actively dividing. A similar network centred on tubulin was produced for the genes up-regulated in larvae raised in low pH, produced from adults acclimated at low pH (coded green in Supplemental Table S2). An additional network was also present containing genes involved in glutathione metabolism (gpx7 and ggt1) and inflammation (mep1B and clec4A) (coded yellow in Supplemental Table S2) indicating the possession of a defence response.
Expression profiles for 3dpf larvae
At this stage larvae in low pH produced from ambient adults produced two networks, one centred on the notch gene involving other signalling molecules (Fig. 1a) (coded yellow in Supplementary Table S3) and the second related to RNA processing (coded green in Supplementary Table S3). Three larger inter-connected networks were present among the up-regulated transcripts from the low pH larvae produced from low pH adults. One gene network included the notch gene which was connected to other transcriptional activators such as spdef and forkhead (Fig. 1b) and several members of the antioxidant glutathione-s-transferase family and CypP450 protein family, which is involved in detoxification processes (Fig. 1b) (coded yellow in Supplementary Table S4). A second network (coded green in Supplementary Table S4) was largely concerned with transcriptional regulation, whilst a third (coded blue in Supplementary Table S4) involved metabolic genes. One heat shock protein transcript (contig 7997) with sequence similarity to hsp701A was shown as up-regulated (Supplementary Table S4), but was not present in the networks or in the nine hsp genes evaluated by Q-PCR.
Expression profiles for 4dpf larvae
In this stage, the gene networks in both treatments were far more interconnected and much larger compared to 2 and 3 dpf larvae. In the network produced from up-regulated genes in low pH larvae raised from control pH adults, another important signalling transcript was present (wnt (wingless-type MMTV)) and also other transcription factors impacting cell differentiation and growth such as the map kinase mapk1 and protein kinase (prkcd) (Supplementary Table S5). Virtually all of the transcripts up-regulated in the low pH larvae raised from low pH acclimated adults were involved in one large network, in which it was impossible to define specific nodal functional groups. The latter included the signalling genes notch and wnt, but also the antioxidants; the glutathione-s-transferases, a large number of ribosomal genes and members of the heat shock protein family (contig 35016: hsp901a1b; contig 7997: hsp701a; contig 18720: hspa5; contig 37882: hspa8) (Supplementary Table S6). These were small HSP contigs and thus not included in the main HSP listing (Table 2).
Identification of heat shock protein transcripts and transcriptome profiling
Nine contigs were initially identified in the backbone transcriptome, which shared sequence similarity with heat shock proteins (as defined by Blast sequence similarity searching) and also had sufficient overlap in sequence to enable them to be identified as distinct family members (Table 2). Whilst several additional smaller contigs with sequence similarity to hsp family members were identified in the transcriptional profiles (Supplementary Tables S1–S6), these sequences were too short to enable a more comprehensive characterisation and thus the list of nine should be considered as a minimal listing of family members present in the genome. Of the nine sequences analysed in more detail, two showed highest sequence similarity to hsp90 (contig IDs 52063 and 51464) with 48.5% identity and 72.4% similarity at the amino acid level in a 263 amino acid (aa) overlapping region. The first contig (52063) contained the methionine start codon, along with five motifs characteristic of the Hsp90 family (NKEIFLRELISNSSDALDKIR (at aa position 28–48); LGTIAKSGT (aa 95–103); IGQFGVGFYSAYLVAD (aa119–134); IKLYVRRVFI (aa 346–355) and GVVDSEDLPLNISRE (aa 372–386)), but was not full-length, missing the C-terminus with the cellular localisation motif 23. The second contig (51464) was shorter and only encompassed the central portion of the gene, containing only the last two motifs listed above. The remaining seven transcripts were putatively identified as belonging to the hsp70 family, both on Blast sequence similarity searching and motif searches (Table 2, Supplementary Information S1). Of these it was interesting to note that two (13435, 46238) were the only ones not having a Blast sequence similarity search E value of 0.0, identifying them as more divergent members of this family. A third contig (44027) showed highest sequence similarity to mortalin, a gene which, although it has been shown to be non-inducible to heat in vertebrates, has multiple functions including the response to numerous types of environmental stress and chaperone-like activity24. The four remaining hsp70 contigs (37720, 62830, 62842 and 62178) all had the signature for non-organelle family members (comprising hsp70, hsc70 and grp78) (Supplementary Information S1). Contig 62178 showed most sequence similarity to grp78 (Glucose-regulated protein 78 kDa), whilst the remaining three contigs (37720, 62830, 62842) were particularly close in terms of sequence similarity. Analysis of the overlapping 265 amino acid region between these three sequences revealed that the more divergent member of this sub-group (37720) shared most sequence similarity to hsp70IV and 86.8–88.7% amino acid similarity to the other two contigs. Contigs 62830 and 62842 matched the same accession number (W4Y0E3: Hsp701A) sharing 84.2% amino acid identity (91.3% similarity). The level of differences between the three transcripts indicated that they were most likely separate isoforms, rather than allelic variants and these data were validated via the Q-PCR analyses.
Interrogation of the OA-generated transcriptome data revealed highly variable expression of the nine different hsp transcripts under the different treatments and time points (Table 3). In general the hsp transcripts were all poorly expressed in the treated larvae compared with controls. Most of the expression ratios were less than 1 (indicating down regulation) and all were below 2 (the cut-off used in the evaluation of the classical HSR detailed below). The only exception was transcript 37720 (hsp70IV) in the CE3 (low pH cultured larvae produced from ambient adults) samples with an expression ratio of 18. Contig 13435 coding for a putative member of the hsp70 family was not expressed above the analysis threshold in any of the treated samples.
Evaluation of the classical heat shock response via heat shock experiments in adults and larvae
In a separate P. miliaris experiment, adult and 2 dpf and 4 dpf larvae, all cultured and raised in ambient pH, were subjected to an acute heat shock of 25 °C for one hour to evaluate their HSR. All of the nine hsp70 and hsp90 gene family members identified from the larval transcriptome were successfully amplified in these samples by standard PCR and Q-PCR. 18s rRNA was a suitable reference gene as its expression was stable across all samples: Cq values were not significantly different between control and heat shock samples for 2 dpf larvae (t(3.84) = 1.87, p > 0.05), 4 dpf larvae (χ2(1) = 0.05, p > 0.05) and adults (t(17.473) = −0.010, p > 0.05). There was an increase in the number of significantly up-regulated hsp transcripts in response to heat shock through development: two transcripts were up-regulated in 2 dpf larvae, whilst five were up-regulated in 4 dpf larvae. Eight transcripts were up-regulated in adults (Fig. 2), including one transcript (contig 44027) with highest sequence similarity to mortalin, an hsp70 family member which has not been shown previously to be involved in the heat shock response. Only one transcript (Contig 46238: hsp701G) did not show significant differential expression between heat shock and control treatments. Developmental stage also had an effect on the magnitude of up-regulation: the combined log2 fold changes in gene expression across all transcripts were significantly different between stages [χ2 (2) = 9.358, p < 0.01]. The effect was most evident between 2 dpf larvae and adults (Fig. 2).
These data clearly highlight the molecular mechanisms underpinning TGP in P. miliaris, with maternal pre-loading of transcripts involved in the classical stress response, such as antioxidants and chaperone proteins. We suggest that these transcripts play a protective role in the vulnerable early stage larvae until their own transcriptional responses are fully developed. The transcriptional profiling also showed delayed expression of signalling genes, such as notch and wnt. These transcripts are key regulators of development, interacting with numerous biochemical pathways including cellular homeostasis and calcification, which may explain the morphological differences previously observed in this species, when subjected to low pH experiments9 (Supplementary Information S2). There is also a developmental delay in the capacity of P. miliaris larvae to express an HSR, the classical response to environmental change, as demonstrated by an additional heat shock experiment and Q-PCR analysis of heat shock proteins (Fig. 2).
One working hypothesis at the start of this study concerned the developmental regulation of the classical environmental stress response, often evaluated as the HSR. It was expected that larvae spawned into low pH from adults held in control conditions would exhibit more of an HSR compared with larvae spawned from adults pre-conditioned to low pH, due to the induction of an acute stress response. In fact it was the low pH larvae produced from low pH acclimated adults that showed expression of a variety of hsp transcripts along with genes involved in antioxidant and detoxification activities. These data provide a potential cellular mechanism behind TGP in this species, which results in improved larval performance with adult acclimation to low pH9. Current evidence from other species suggests that in general embryos are stable and well buffered from the environment, which is achieved by a process called maternal provisioning or maternal conditioning25. Studies, specifically on maternal effects have shown that adults raised in good nutritional conditions can increase the levels of energy sources, such as triglycerides, within the eggs, providing a boost for growth, which can last long after larval feeding has started26. Allied to this observation is the demonstration that one of the strategies to increase developmental success is the production of larger eggs27 and indeed, this effect has been demonstrated in P. miliaris when eggs are produced under altered conditions9. Such preparation of the embryo is not restricted to nutritional requirements: in fact, the maternal effect also strongly influences early transcription profiles21. The eggs are pre-loaded with maternal transcripts, which include high levels of cellular defence mechanisms, including antioxidants and immune transcripts25, the expression of which is triggered on fertilisation and provide the initial development profile of the larvae28. Parental conditioning can also influence the response of the offspring, priming them to respond more efficiently to the “new” conditions21. This maternal pre-loading of transcripts is evidenced here by the presence of transcripts putatively involved in antioxidant activity and also by the presence of some hsps in the low pH larvae produced from low pH pre-treated adults (Supplementary Tables S4 and S6). This indicates the possible protective mechanism behind maternal conditioning of gonads under altered conditions, whereby larvae raised under low pH conditions from acclimated adults can perform at least as well, if not better than larvae raised in control conditions from adults maintained in control conditions9,10,21,29,30. Such findings highlight the importance of adult pre-conditioning in a number of urchin species where critical defence mechanisms can be pre-loaded. However there are some species which do not exhibit a favourable TGP to altered conditions11,14,15 and others where the initial beneficial effects on the early stage larvae do not continue through to recruitment7,13 or diminish when multiple stressors are used16. This complexity of response clearly requires further investigation at the molecular level, not only in larvae, but also the adults under pre-acclimation.
It should be noted that even in those cases with beneficial parental acclimation, the maternal transcripts are unstable and are gradually replaced by two waves of minor and major zygotic genome activation as the embryo develops complexity and becomes fully independent28. This gradual activation of the zygotic genome is in agreement with the increasing number of transcripts represented through time in the transcriptional profiling detailed here (Table 1) and the heat shock protein Q-PCR results. The lack of any significant up-regulation of heat shock transcripts in the transcription profiles of the larvae raised in low pH (at 2, 3, and 4 dpf), particularly those produced from non-acclimated adults was intriguing. This indicated the potential inability to produce the classic HSR in response to environmental stress, but has been seen previously in other studies31,32. In a separate experiment designed to evaluate when P. miliaris larvae can mount an HSR, Q-PCR of nine heat shock protein transcripts was used in conjunction with an acute heat shock treatment of both adults and larvae. These demonstrated that the HSR was not fully present in the larvae, but the ability to produce such a response increased in the larvae from 2 dpf to 4 dpf (Fig. 2).
Despite the possession of an active immune system, gastrulation is an extremely sensitive stage of early life history development in sea urchins34,35. Previous experiments have shown that the amount of hsp70 transcript produced at early developmental stages is low and only produced post-blastula34. Even with maternal conditioning and pre-loading of transcripts, the levels of hsp mRNA are probably insufficient to overcome any cellular damage. It was suggested that this low level of measureable expression was because of the number and size of the cells in the very early embryo. Early embryos have few, large cells, with a low nucleus to cytoplasm ratio, but as the number of cells increase, the cell size decreases and the nucleus to cytoplasm ratio increases. Thus the relative amount of hsp70 produced per cell becomes increasingly effective at protecting the cell as the number of cells increase36. This may be further complicated by selected (and delayed) translational activation of maternal mRNA, as has been shown for hsp90 or post-translational regulation of hsp7032,33.
In this study although the embryo stages in this heat shock study were post-blastula, their abilities to produce sufficient hsps were still developmentally limited with only two hsp transcripts activated in 2 dpf larvae, increasing to four transcripts in 4 dpf larvae. This is much lower when compared with the adults, in which eight hsps were expressed in response to an acute heat stress. Additionally the larval transcripts were also expressed at lower levels compared with the adults (Fig. 2), as seen previously in S. franciscanus37. This may be due to any of the effects discussed above, but also potentially because over-expression of hsps can have negative effects on larval development and is thus more tightly regulated during these early stages38. The results here are also reflected in recent ocean acidification studies showing the impacts of responses to low pH to be larval stage-dependent17,18,33,39. Overall these data indicate the vulnerability of larval stages, but also the need to understand in more detail the transcriptional and translation events in these early life history stages.
In terms of investigating the effects of environmental change on early life history stages, sea urchins are ideal models, as they have a long history in scientific research for deciphering the molecular events involved in the cell cycle and development40,41. These studies have identified key regulators of development including wnt, notch and β-catenin. These genes critically initiate the developmental cascades in the urchin. The identification of such key transcripts up-regulated in all the low pH treated larvae, when compared to larvae from control conditions and their presence in enriched gene networks (Fig. 1), implies a delayed expression of these transcripts in this experiment. This may have significant down-stream implications for other biochemical processes, as evidenced by morphological differences between larvae in the different treatments9,18. The experiment described here was conducted within the scope of a Masters project (CLM, pers comm; Supplementary Information S2). In the Masters project, the developmental schedule of P. miliaris was described along with comprehensive morphometric analyses of larvae raised in ambient and low pH conditions (from ambient acclimated and low pH acclimated adults respectively). These showed altered larval morphometrics with time in the low pH treatment. The larvae raised in low pH had significantly smaller body length-width ratios (F1,174 = 8.035, p = 0.005) than counterparts reared under ambient conditions. In addition, larvae raised under low pH had an increased percentage of abnormalities (25–40%) than those raised under ambient conditions. The severity of abnormalities in low pH larvae was more pronounced with missing arms, substantial length differences in arm length, asymmetric body shape etc. compared to ambient pH raised larvae, which had only minor length differences in arm pairs and minor imbalance to body shape (Supplementary Information S2). Changes in larval morphology due to culture in low pH conditions has been documented in virtually every study to date, although there is debate as to the underlying mechanisms. Theories include hypercapnic effects, maintenance costs associated with cellular homoeostasis, reduced capacity for calcification and developmental delay21,31,42,43,44,45,46,47,48.
Previous transcriptional profiling experiments on sea urchin larvae have shown very variable results, often with considerable down-regulation (in excess of 80%) of transcripts48. The effects are often very subtle and thus can be difficult to accurately define (cf. foxq231; wnt849), particularly if there are consequential trade-off effects20. A meta-analysis involving molecular profiling of sea urchin larvae cultured under low pH suggested that shape and size changes in low pH cultured larvae were due to metabolic depression with up-regulation of genes involved in metabolism, ion transport and biomineralization48. This meta-analysis did not show over-representation of gene ontologies related to development even though genes annotated to “developmental process” were up-regulated in certain studies48. Whilst the most striking finding about the transcriptional profiles described here was the delayed expression of key signalling genes, a number of ion channels and solute carriers were also up-regulated under the different treatments (e.g. Cacna1a, kcnj18, kcnn3, solute carriers all denoted slc etc) and in general genes involved with skeletogenesis were down-regulated (Supplementary Tables S1–S6). The finding that ion channels and solute carriers were up-regulated in all larvae implies an alteration has occurred in ion homeostasis as a result of culture in low pH. A particularly interesting observation was that more ion channels and solute carriers were up-regulated in the larvae from low pH acclimated adults supporting the results of a previous study which showed that adult conditioning can impact the ion regulatory response of their F121 (Supplementary Tables S1–S6). In general genes involved in skeletogenesis were down-regulated in this study (as they were not annotated in the gene lists), the exception was the up-regulation of bmp2 and chrd in 3 dpf larvae from low pH acclimated adults. These findings, along with altered ion homeostasis may explain why P. miliaris larvae cultured in low pH are usually smaller than those cultured in ambient conditions and also the differences in morphological measurements between larvae from different adult pre-treatments9,18 (Supplementary Information S2).
Disentangling developmental delay from altered biochemical processes is complex, as the signalling molecules expressed early in development affect multiple biochemical pathways40,41. The data here show that the initial disruption to developmental signalling cascades occurs very early in development with the altered expression of the critical transcription factors (wnt, notch and β-catenin) (Fig. 1), which may result in a range of physiological outcomes for the larvae. It is possible be that subtle differences in the expression levels of these initial signalling molecules in different species and their downstream cascades determines the highly variable larval responses, seen in experiments to date. Thus discovery-led RNA-Seq approaches linked to longer and more detailed time course studies may help to dissect out the causality of such species-specific effects and the potential downstream consequences of adult acclimation on later developmental stages such as juveniles and recruitment.
In summary, investigations into larval sensitivities to environmental challenge are revealing the complex nature of the responses, particularly at the molecular level. The data here show that adult P. miliaris pre-acclimated to low pH conditions can preload the resulting larvae with protective transcripts such as antioxidants and heat shock proteins, resulting in favourable TGP with larvae better able to survive in the altered conditions. The results of both the transcriptional profiling and the Q-PCR analysis of heat shock proteins clearly show that there is a delay in the ability of larvae to mount a full HSR. This inability (or capacity) of early stage larvae to mount an effective “stress” response clearly contributes to the vulnerability of this early stage of life. Thus maternal conditioning and assessment of the vulnerability of larvae via the characterisation of particularly sensitive stages is important not only for experimental design, but also for modelling where an understanding of recruitment potential underpins future biodiversity predictions.
Animal collection and adult acclimation
Psammechinus miliaris sea urchins were collected by scuba divers at 3–10 m in February 2010 from Rubha Garbh, Loch Creran, Scotland. The urchins were transported in aerated cool boxes and transferred into flow-through aquaria at Bangor University’s School of Ocean Sciences, Anglesey. They were then acclimated to ambient (control) pH aquarium conditions (~pH 8) for two months prior to the start of the experiment. Urchins were fed to satiation (approximately 5% mean body weight) twice a week on an artificial diet largely composed of mussels (Mytilus edulis) and macroalgae (Laminaria digitata). After the two months, animals with a test diameter over 25 mm were chosen as broodstock for the OA trial as this is the size generally considered as reproductively contributing adults in this species50. These animals were randomly assigned to experimental tanks in an OA flow-through mesocosm as described previously18. Treatments used in this study were derived from the IPCC predictions using the ‘RCP8.5 business-as-usual’ scenario51 with parameters calculated and reported following OA community guidelines52. Present day control sea water, imported directly from the Menai Straits, measured ~pHNIST 8.06 and pCO2 calculated at 412 ± 6 µatm (referred to from here on as 400 µatm or ambient), with the year 2100 pH level calculated at ~pHNIST 7.72 and a pCO2 of 1013 ± 12 µatm (referred to from here on as 1000 µatm or low pH) (Table 1). Adults were cultured in either 400 µatm or 1000 µatm for a further two months prior to spawning in June of the same year (Supplementary Information S3). No data are available for the water chemistry of Loch Creran, however this experiment resulted in a total of four months culture in water from the Menai Straits prior to spawning, with associated acclimation to water chemistry and diet. This timing is at least as long as previous aquaculture studies in this species, which show full acclimation of P. miliaris to manipulation experiments53,54. The length of the acclimation period in the new conditions did not cover the whole of the reproductive cycle, as recommended in urchin studies of other species7,10. However, in this species previous data have demonstrated that two months is sufficient time to produce significantly improved outcomes for the resulting larvae9. Seawater temperatures in holding tanks during acclimation and experimental periods was according to ambient seasonal temperatures of the region (Supplementary Information S3). A 16 L: 8 D photoperiod was used throughout the experiment.
Spawning and larval culture
Following two months exposure to 400 µatm or 1000 µatm, adult P. miliaris from each treatment were induced to spawn at the beginning of July when all urchins, irrespective of treatment, were at stage IV maturity (the normal stage for the peak spawning period)9,18. Spawning of adults via injection of 0.5 M KCl and fertilisation of embryos was performed in the same conditions as the parents had been cultured in either ambient or low pH (400 µatm or 1000 µatm) as appropriate, with methodology as described previously18. Five females and two males were successfully spawned for each treatment with gametes pooled prior to fertilisation, with the production of three replicates. Embryos and larvae were either cultured under 400 µatm or 1000 µatm conditions, using 1 μm filtered and UV treated seawater obtained from the OA system. 48 hours after fertilisation larval stocking densities were adjusted to one larvae mL−1 and a daily feeding regime was started using Dunaliella tertiolecta (CCAP 19/6B) cultured in sterile conditions with a daily feeding rate of 1500 cells ml−1. 50 mls of larval culture were sampled 2, 3 and 4 days post fertilisation, at which point they were at the feeding pluteus (4 arm) stage. After brief centrifugation at 2,000 rpm to concentrate the larvae, the seawater was carefully removed and the larvae flash frozen in liquid nitrogen and stored at −80 °C until RNA extraction.
Daily measurements of temperature and pH were taken using a hand-held temperature compensated pH meter (HI98160 Hanna Instruments UK Ltd). Weekly salinity measurements were made using an ATC portable refractometer calibrated with distilled water prior to use. Total CO2 concentration (TCO2) was measured twice weekly, in triplicate using a Carbon Dioxide Analyser (Corning 965; Olympic Analytical, UK). The TCO2 analyser was blanked to zero and calibrated with Reagecon 2 g L−1 CO2 standards before each set of readings. Silicate (SiCO3) and phosphate (PO4) nutrients were determined with a Lachat 8000 two flow injection nutrient analyser in the Scottish Association of Marine Science, Oban, UK. Values for the parameters of total alkalinity (TA), and Ω were calculated with CO2SYS with refitted constants following OA community guidelines52 (Table 4).
Heat shock experiments
Heat shock experiments were conducted on both larvae and adult P. miliaris. The adults were taken from the control system (400 µatm) of the OA experiment described earlier. The control temperature used was 15.8 °C and the heat shock performed at 25 °C for one hour. This temperature was chosen as sufficiently high in relation to the normal temperature range experienced by these urchins to take them over a “stress” threshold and induce a heat shock response22. Larvae were produced from broodstock (test diameter (±SE) = 34.87 ± 0.82 mm, whole animal wet mass = 20.50 ± 1.10 g) which were reared under the control conditions described in Table 4. Gametes and subsequent embryos and larvae were maintained at control conditions of 15.8 ± 0.13 °C and salinity 35 on the practical salinity scale until used for the one-hour thermal shock experiments, but otherwise reared using the methods described above. Fertilisation success was 99% showing that gametes were healthy and viable. Heat shocks were performed on larvae cultured under control pH conditions at days two and four dpf, with three replicates for each time period. Prior to the heat shock trial, larvae were collected into a 47 µm mesh and washed directly into the control and higher temperature treatments. After the heat shock of one hour at 25 °C, larvae were centrifuged for two seconds at 7000 rpm, the seawater was removed and the larvae flash frozen in liquid nitrogen and stored at −80 °C until extraction. Two-year old adults (25.5 months) (n = 5) were used in the heat shock experiment. After the adults had been heat shocked, coelomic fluid was removed using a syringe and flash frozen in liquid nitrogen and stored at −80 °C until extraction. Control samples (non-heat shocked) were also taken for both larvae (three replicates) and adults (n = 5).
RNA extraction and RNA-Seq
RNA was extracted from three replicates of pooled larval samples using TRI reagent (Bioline) and purified on RNeasy mini-columns (Qiagen) according to manufacturer’s instructions. RNA was quantified using either a NanoDrop 1000 photometer (Labtech International, UK) or a Tape Station 2200 (Agilent Technologies). The OA experimental RNAs were subjected to RNA-Seq on an Illumina Hi-Seq (100 bp paired end reads) at The Earlham Institute, Norwich.
In total, 194,339,075 100 bp paired end Illumina reads (C2: 15,601,575; C3: 9,407,731; C4: 15,253,564; CE2: 44,586,274; CE3: 30,382,990; CE4: 14,915,868; E2: 27,799,660;E3: 24,860,228; E4: 11,531,185) were clipped and trimmed for adapter sequence and quality using EA-UTILS55,56. The raw Illumina reads were assembled using SOAP denovo (soap.genomics.org.cn) (using a kmer of 91, which produced the greatest number of longer contigs). All kmer contigs greater than 200 bp were run through CD-HIT57,58, following which the remaining contigs were run through CAP359. All contigs and singletons greater than 500 bp were then screened for contamination from various sources, including the food (Dunaliella tertiolecta) using BLAST and any reads identified as contaminants removed. The remaining sequences were used for both producing the backbone sequence database and also for mapping differential expression patterns. A proportion test was carried out for all comparisons in R60 with an adjustment made for multiple testing61 with an FDR cutoff set at 0.01. Only mappings where both paired-end reads mapped to the same contig were used to generate expression levels and calculate significance of expression with the following additional criteria for selection and designation of significant change in expression: a fold change greater than 2; an adjusted p value of <0.01; both sets of treatment reads had to have in excess of 10 reads per contig and at least one treatment had to have in excess of 50 reads per contig. Contigs were searched for sequence similarity using BLAST62 against the GenBank non-redundant database63 with a threshold score of <1e−10. Transcripts with sequence similarity to members of the 70 kDa and 90 kDa HSP family were identified from searches of the BLAST data, manually verified and the sequences manipulated, including translation into putative protein sequences, using Bio-Linux64. Sequences annotated through GenBank were further searched against the Swissprot databases of different model species. The Swissprot Homo sapiens database produced the highest number of matches below 1e−10 by at least a factor of 10 compared to the lower vertebrates and invertebrates when searched with the P. miliaris data and so it was chosen for further analyses. The Swissprot identifiers were used to input into Panther GO-Slim65 and the STRING program, a database of protein-protein interactions (http://string-db.org/), to provide an overview of putative gene networks.
HSP transcript expression analysis: RNA extraction and reverse transcription
RNA was extracted from three replicates of pooled larval samples using ReliaPrep™ RNA Miniprep Systems (Promega) according to manufacturer’s instructions. The protocol for non-fibrous tissue (tissue input ≤ 5 mg) was followed, with a centrifugation speed of 13,000 × g. RNA from the coelomic fluid of adults was extracted using RNeasy Mini Kit (Qiagen) following the protocol for animal cells, with centrifugation speed of 10,600 × g. Both protocols included a DNase digestion step. Larvae and coelomic fluid were lysed using a TissueRuptor rotor-stator homogeniser (Qiagen), and the final elution volume was 30 µL. RNA concentration and integrity were assessed using a Tape Station 2200 (Agilent Technologies). Complementary DNA (cDNA) was produced from 150 or 500 ng of RNA from adults or larvae respectively, using the QuantiTect® Reverse Transcription Kit (Qiagen) according to manufacturer’s instructions, with a further genomic DNA elimination step.
Q-PCR primer design and specificity testing
Q-PCR primers for each of the nine HSP transcripts were designed either using the Primer3plus program66 or manually in the case of the three very closely related hsp70 genes (Supplementary Table S7), with primer specificity confirmed by Sanger sequencing of PCR products (performed by Source Bioscience, UK). PCR thermal cycling conditions were as follows: 2 min at 95 °C, 35 cycles of 15 s at 95 °C, 20 s at 60 °C and 30 s at 72 °C. Reactions comprised 1x NH4 buffer, 1.6 mM MgCl2 solution dNTP mix with 213.9 µM of each dNTP, 1.07 µM of each primer, 0.027 u/µL BIOTAQ™ DNA Polymerase (Bioline) and 3.24 µM bovine serum albumin with 0.5 µL of cDNA.
Q-PCR was performed using an Eco Real-Time PCR System (PCRmax) with the following thermal cycling conditions: 3 min at 95 °C followed by 40 cycles of 5 s at 95 °C and 10 s at 60 °C. Amplification specificity was assessed through melting curve analysis, with an additional step immediately subsequent to the thermal cycling: the products were denatured for 15 s at 95 °C, allowed to re-anneal for 15 s at 55 °C and the temperature was then raised to 95 °C at a ramping rate of 0.25 °C/s. Samples were run in duplicate wells and all assays included no template controls and negative controls (nuclease free water). Amplification efficiencies for each assay were calculated by the EcoStudy software (Illumina) from a standard curve produced through serial dilutions of cDNA template pools (separate pools were prepared from adult and larval samples). The number of dilutions was ≥4 starting from undiluted or 1:2 cDNA for all assays and the dilution factor was either 4 or 10, depending on the assay-specific amplification behaviour. Each q-PCR reaction comprised 1x Brilliant III SYBR® Green master mix (Agilent), 570 nM of each primer, 721 nM bovine serum albumin and 0.5 µL cDNA (total reaction volume: 10.5 µL). Adult sample cDNA was diluted 1:10 for all transcripts except for contigs 46238 and 62830, for which a 1:4 dilution was used. Day 2 and day 4 larval cDNA samples were diluted 1:2 and 1:10 respectively. A 18 s rRNA transcript was used as the reference gene for normalisation, after confirming its expression was constant between control and heated samples.
Q-PCR Data analysis
Amplification efficiency and R2 values were obtained using the EcoStudy software (Illumina) with automatic baseline correction and threshold adjustment (Supplementary Table S7). To test for differential expression, each of the transcripts was analysed using REST 2009 Software67. The algorithm calculates efficiency corrected relative expression ratios between target and reference genes68 for each transcript, and performs a randomisation test producing a P value indicating differential expression between two treatments, with statistical significance for p < 0.0567. The default number of randomisations (2000) was used in the analysis. Stable expression of the reference gene used for normalisation (18s rRNA) was confirmed by comparing raw Cq values (Supplementary Table S8) between treatments using a Welch’s t-test for day 2 and adult samples, and by a Kruskal-Wallis test for day 4 samples as these did not meet the normality assumption. To test for a difference in the magnitude of differential expression of the HSP transcripts between early developmental stages and adult sea urchins an inter-stage comparison was carried out on the log2 fold changes in gene expression across all transcripts (n = 9, see Fig. 2) among day 2 larvae, day 4 larvae and adult sea urchins. Because the data (log2 fold changes) were not normally distributed, a Kruskal-Wallis test and a Dunn’s post-hoc test with Holm’s correction for multiple comparisons were performed. All statistical analyses were performed in R60.
All sequence data were submitted to the NCBI Short-Read Archive (SRA) with the accession number: SRP102910 with the separate run accession numbers: C2 SRR5396276; C3 SRR5396277; C4 SRR5396279; CE2 SRR5396289; CE3 SRR5396306; CE4 SRR5396328; E2 SRR5396309; E3 SRR5396331;E4 SRR5396332.
Somero, G. N. The physiology of climate change: how potentials for acclimatization and genetic adaptation will determine ‘winners’ and ‘losers’. Journal of Experimental Biology 213, 912–920, https://doi.org/10.1242/jeb.037473 (2010).
Kroeker, K. J. et al. Impacts of ocean acidification on marine organisms: quantifying sensitivities and interaction with warming. Global Change Biology 19, 1884–1896, https://doi.org/10.1111/gcb.12179 (2013).
Feely, R. A., Sabine, C. L., Hernandez-Ayon, J. M., Ianson, D. & Hales, B. Evidence for upwelling of corrosive “acidified” water onto the continental shelf. Science 320, 1490–1492, https://doi.org/10.1126/science.1155676 (2008).
Hauri, C. et al. Ocean acidification in the California current system. Oceanography 22, 60–71, https://doi.org/10.5670/oceanog.2009.97 (2009).
Ross, P. M., Parker, L. & Byrne, M. Transgenerational responses of molluscs and echinoderms to changing ocean conditions. Ices Journal of Marine Science 73, 537–549, https://doi.org/10.1093/icesjms/fsv254 (2016).
Donelson, J. M., Salinas, S., Munday, P. L. & Sharma, L. N. S. Transgenerational plasticity andclimate change: Where do we go from here? Global Change Biology 24, 13–34 (2018).
Dupont, S., Dorey, N., Stumpp, M., Melzner, F. & Thorndyke, M. Long-term and trans-life-cycle effects of exposure to ocean acidification in the green sea urchin Strongylocentrotus droebachiensis. Marine Biology 160, 1835–1843, https://doi.org/10.1007/s00227-012-1921-x (2013).
Kurihara, H., Yin, R., Nishihara, G. N., Soyano, K. & Ishimatsu, A. Effect of ocean acidification on growth, gonad development and physiology of the sea urchin Hemicentrotus pulcherrimus. Aquatic Biology 18, 281–292, https://doi.org/10.3354/ab00510 (2013).
Suckling, C. C. et al. Experimental influence of pH on the early life-stages of sea urchins II: increasing parental exposure times gives rise to different responses. Invertebrate Reproduction & Development 58, 161–175, https://doi.org/10.1080/07924259.2013.875951 (2014).
Suckling, C. C. et al. Adult acclimation to combined temperature and pH stressors significantly enhances reproductive outcomes compared to short-term exposures. Journal of Animal Ecology 84, 773–784, https://doi.org/10.1111/1365-2656.12316 (2015).
Uthicke, S., Soars, N., Foo, S. & Byrne, M. Effects of elevated pCO 2 and the effect of parent acclimation on development in the tropical Pacific sea urchin Echinometra mathaei. Marine Biology 160, 1913–1926, https://doi.org/10.1007/s00227-012-2023-5 (2013).
Lamare, M. D., Liddy, M. & Uthicke, S. In situ developmental responses of tropical sea urchin larvae to ocean acidification conditions at naturally elevated pCO 2 vent sites. Proceedings of the Royal Society B-Biological Sciences 283, https://doi.org/10.1098/rspb.2016.1506 (2016).
Lister, K. N., Lamare, M. D. & Burritt, D. J. Maternal antioxidant provisioning mitigates pollutant-induced oxidative damage in embryos of the temperate sea urchin Evechinus chloroticus. Scientific Reports 7, https://doi.org/10.1038/s41598-017-02077-5 (2017).
Verkaik, K., Hamel, J. F. & Mercier, A. Carry-over effects of ocean acidification in a cold-water lecithotrophic holothuroid. Marine Ecology Progress Series 557, 189–206, https://doi.org/10.3354/meps11868 (2016).
Griffith, A. W. & Gobler, C. J. Transgenerational exposure of North Atlantic bivalves to ocean acidification renders offspring more vulnerable to low pH and additional stressors. Scientific Reports 7, https://doi.org/10.1038/s41598-017-11442-3 (2017).
Parker, L. M. et al. Adult exposure to ocean acidification is maladaptive for larvae of the Sydney rock oyster Saccostrea glomerata in the presence of multiple stressors. Biology Letters 13, https://doi.org/10.1098/rsbl.2016.0798 (2017).
Clark, D., Lamare, M. & Barker, M. Response of sea urchin pluteus larvae (Echinodermata: Echinoidea) to reduced seawater pH: a comparison among a tropical, temperate, and a polar species. Marine Biology 156, 1125–1137, https://doi.org/10.1007/s00227-009-1155-8 (2009).
Suckling, C. C., Clark, M. S., Peck, L. S. & Cook, E. J. Experimental influence of pH on the early life-stages of sea urchins I: different rates of introduction give rise to different responses. Invertebrate Reproduction & Development 58, 148–159, https://doi.org/10.1080/07924259.2013.875950 (2014).
Brothers, C. J., Harianto, J., McClintock, J. B. & Byrne, M. Sea urchins in a high-CO2 world: the influence of acclimation on the immune response to ocean warming and acidification. Proceedings of the Royal Society B-Biological Sciences 283, https://doi.org/10.1098/rspb.2016.1501 (2016).
Evans, T. G., Pespeni, M. H., Hofmann, G. E., Palumbi, S. R. & Sanford, E. Transcriptomic responses to seawater acidification among sea urchin populations inhabiting a natural pH mosaic. Molecular Ecology 26, 2257–2275, https://doi.org/10.1111/mec.14038 (2017).
Wong, J. M., Johnson, K. M., Kelly, M. W. & Hofmann, G. E. Transcriptomics reveal transgenerational effects in purple sea urchin embryos: Adult acclimation to upwelling conditions alters the response of their progeny to differential pCO 2 levels. Molecular Ecology 72, 1120–1137, https://doi.org/10.1111/mec.14503 (2018).
Feder, M. E. & Hofmann, G. E. Heat-shock proteins, molecular chaperones, and the stress response: Evolutionary and ecological physiology. Annual Review of Physiology 61, 243–282, https://doi.org/10.1146/annurev.physiol.61.1.243 (1999).
Gupta, R. S. Phylogenetic analysis of the 90 kD heat shock family of protein sequences and an examination of the relationship among animals, plants and fungi species. Molecular Biology and Evolution 12, 1063–1073 (1995).
Kaul, S. C., Deocaris, C. C. & Wadhwa, R. Three faces of mortalin: A housekeeper, guardian and killer. Experimental Gerontology 42, 263–274, https://doi.org/10.1016/j.exger.2006.10.020 (2007).
Hamdoun, A. & Epel, D. Embryo stability and vulnerability in an always changing world. Proceedings of the National Academy of Sciences of the United States of America 104, 1745–1750, https://doi.org/10.1073/pnas.0610108104 (2007).
Byrne, M. et al. Maternal provisioning for larvae and larval provisioning for juveniles in the toxopneustid sea urchin Tripneustes gratilla. Marine Biology 155, 473–482, https://doi.org/10.1007/s00227-008-1045-5 (2008).
Llodra, E. R. Fecundity and life-history strategies in marine invertebrates. Advances in Marine Biology, Vol 43 43, 87–170 (2002).
Tadros, W. & Lipshitz, H. D. The maternal-to-zygotic transition: a play in two acts. Development 136, 3033–3042, https://doi.org/10.1242/dev.033183 (2009).
Delorme, N. J. & Sewell, M. A. Temperature limits to early development of the New Zealand sea urchin Evechinus chloroticus (Valenciennes, 1846). Journal of Thermal Biology 38, 218–224, https://doi.org/10.1016/j.jtherbio.2013.02.007 (2013).
Kelly, M. W., Padilla-Gamino, J. L. & Hofmann, G. E. Natural variation and the capacity to adapt to ocean acidification in the keystone sea urchin Strongylocentrotus purpuratus. Global Change Biology 19, 2536–2546, https://doi.org/10.1111/gcb.12251 (2013).
Todgham, A. E. & Hofmann, G. E. Transcriptomic response of sea urchin larvae Strongylocentrotus purpuratus to CO2-driven seawater acidification. Journal of Experimental Biology 212, 2579–2594, https://doi.org/10.1242/jeb.032540 (2009).
Bédard, P. A. & Brandhorst, B. P. Translational activation of maternal messenger RNA encoding the heat shock protein HSP90 during sea urchin embryogenesis. Developmental Biology 117, 286–293, https://doi.org/10.1016/0012-1606(86)90371-4 (1986).
Bonaventura, R., Poma, V., Russo, R., Zito, F. & Matranga, V. Effects of UV-B radiation on development and hsp70 expression in sea urchin cleavage embryos. Marine Biology 149, 79–86, https://doi.org/10.1007/s00227-005-0213-0 (2006).
Giudice, G., Sconzo, G. & Roccheri, M. C. Studies on heat shock proteins in sea urchin development. Development Growth & Differentiation 41, 375–380 (1999).
Smith, L.C. et al. The sea urchin immune system. Invertebrate Survival Journal 3, 25–39, http://www.isj.unimo.it/articoli/isj114.pdf (2006).
Sconzo, G. et al. Activation by heat shock of HSP70 gene transcription in sea urchin embryos. Biochemical and Biophysical Research Communications 217, 1032–1038, https://doi.org/10.1006/bbrc.1995.2873 (1995).
O’Donnell, M., Hammond, L. & Hofmann, G. Predicted impact of ocean acidification on a marine invertebrate: elevated CO2 alters response to thermal stress in sea urchin larvae. Marine Biology 156, 439–446, https://doi.org/10.1007/s00227-008-1097-6 (2009).
Krebs, R. A. & Feder, M. E. Hsp70 and larval thermotolerance in Drosophila melanogaster: how much is enough and when is more too much? Journal of Insect Physiology 44, 1091–1101, https://doi.org/10.1016/s0022-1910(98)00059-6 (1998).
Foo, S. A., Dworjanyn, S. A., Poore, A. G. B., Harianto, J. & Byrne, M. Adaptive capacity of the sea urchin Heliocidaris erythrogramma to ocean change stressors: responses from gamete performance to the juvenile. Marine Ecology Progress Series 556, 161–172, https://doi.org/10.3354/meps11841 (2016).
Zhu, X. D. et al. A large-scale analysis of mRNAs expressed by primary mesenchyme cells of the sea urchin embryo. Development 128, 2615–2627 (2001).
Ransick, A., Rast, J. P., Minokawa, T., Calestani, C. & Davidson, E. H. New early zygotic regulators expressed in endomesoderm of sea urchin embryos discovered by differential array hybridization. Developmental Biology 246, 132–147, https://doi.org/10.1006/dbio.2002.0607 (2002).
O’Donnell, M. J. et al. Ocean acidification alters skeletogenesis and gene expression in larval sea urchins. Marine Ecology Progress Series 398, 157–171, https://doi.org/10.3354/meps08346 (2010).
Stumpp, M., Wren, J., Melzner, F., Thorndyke, M. C. & Dupont, S. T. CO2 induced seawater acidification impacts sea urchin larval development I: Elevated metabolic rates decrease scope for growth and induce developmental delay. Comparative Biochemistry and Physiology a-Molecular & Integrative Physiology 160, 331–340, https://doi.org/10.1016/j.cbpa.2011.06.022 (2011).
Stumpp, M., Dupont, S., Thorndyke, M. C. & Melzner, F. CO2 induced seawater acidification impacts sea urchin larval development II: Gene expression patterns in pluteus larvae. Comparative Biochemistry and Physiology a-Molecular & Integrative Physiology 160, 320–330, https://doi.org/10.1016/j.cbpa.2011.06.023 (2011).
Yu, P. C. et al. Growth attenuation with developmental schedule progression in embryos and early larvae of Sterechinus neumayeri raised under elevated CO2. Plos One 8, https://doi.org/10.1371/journal.pone.0052448 (2013).
Stumpp, M. et al. Acidified seawater impacts sea urchin larvae pH regulatory systems relevant for calcification. Proceedings of the National Academy of Sciences of the United States of America 109, 18192–18197, https://doi.org/10.1073/pnas.1209174109 (2012).
Byrne, M., Lamare, M., Winter, D., Dworjanyn, S. A. & Uthicke, S. The stunting effect of a high CO2 ocean on calcification and development in sea urchin larvae, a synthesis from the tropics to the poles. Philosophical Transactions of the Royal Society B-Biological Sciences 368, https://doi.org/10.1098/rstb.2012.0439 (2013).
Evans, T. G. & Watson-Wynn, P. Effects of Seawater Acidification on Gene Expression: Resolving Broader-Scale Trends in Sea Urchins. Biological Bulletin 226, 237–254, https://doi.org/10.1086/BBLv226n3p237 (2014).
Hammond, L. M. & Hofmann, G. E. Early developmental gene regulation in Strongylocentrotus purpuratus embryos in response to elevated CO2 seawater conditions. Journal of Experimental Biology 215, 2445–2454, https://doi.org/10.1242/jeb.058008 (2012).
Kelly, M. S., Hughes, A. D. & Cook, E. J. Chapter 22: Psammechinus miliaris. Developments in Aquaculture and Fisheries Science 38, 329–336, https://doi.org/10.1016/B978-0-12-396491-5.00022-8 (2013).
IPCC Climate change 2013: the physical science basis. Summary for policymakers. Working Group I contribution to the IPCC Fifth Assessment Report [cited 2013 Nov 9]. Available from, http://www.ipcc.ch (2013)
Barry, J.P., Tyrrell, T., Hansson, L., Plattner, G. & Gattuso, J. P. Atmospheric CO2 targets for ocean acidification pertubation experiments. Guide to best practices for Ocean Acidification research and data reporting (eds Riebesell, U., Fabry, V. F., Hansson, L. & Gattuso, J. P.), pp. 53–66. Publications Office of the European Union, Luxembourg (2011).
Cook, E. J. & Kelly, M. S. Effect of variation in the protein value of the red macroalga Palmaria palmata on the feeding, growth and gonad composition of the sea urchins Psammechinus miliaris and Paracentrotus lividus (Echinodermata). Aquaculture 270, 207–217, https://doi.org/10.1016/j.aquaculture.2007.01.026 (2007).
Suckling, C. C., Symonds, R. C., Kelly, M. S. & Young, A. J. The effect of artificial diets on gonad colour and biomass in the edible sea urchin Psammechinus miliaris. Aquaculture 318, 335–342, https://doi.org/10.1016/j.aquaculture.2011.05.042 (2011).
Aronesty, E. ea-utils: Command-line tools for processing biological sequencing data, https://github.com/ExpressionAnalysis/ea-utils (2011).
Aronesty, E. TOBioiJ: Comparison of Sequencing Utility Programs, https://doi.org/10.2174/1875036201307010001 (2013).
Li, W. Z. & Godzik, A. Cd-hit: a fast program for clustering and comparing large sets of protein or nucleotide sequences. Bioinformatics 22, 1658–1659, https://doi.org/10.1093/bioinformatics/btl158 (2006).
Fu, L. M., Niu, B. F., Zhu, Z. W., Wu, S. T. & Li, W. Z. CD-HIT: accelerated for clustering the next-generation sequencing data. Bioinformatics 28, 3150–3152, https://doi.org/10.1093/bioinformatics/bts565 (2012).
Huang, X. Q. & Madan, A. CAP3: A DNA sequence assembly program. Genome Research 9, 868–877, https://doi.org/10.1101/gr.9.9.868 (1999).
R Core Team. A language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria, https://www.R-project.org/ (2011).
Benjamini, Y. & Hochberg, Y. Controlling the false discovery rate – A practical and powerful approach to multiple testing. Journal of the Royal Statistical Society Series B-Methodological 57, 289–300 (1995).
Altschul, S. F. et al. Gapped BLAST and PSI-BLAST: a new generation of protein database search programs. Nucleic Acids Research 25, 3389–3402, https://doi.org/10.1093/nar/25.17.3389 (1997).
Benson, D. A., Karsch-Mizrachi, I., Lipman, D. J., Ostell, J. & Wheeler, D. L. GenBank. Nucleic Acids Research 35, D21–D25, https://doi.org/10.1093/nar/gkl986 (2007).
Field, D. et al. Open software for biologists: from famine to feast. Nature Biotechnology 24, 801–803, https://doi.org/10.1038/nbt0706-801 (2006).
Mi, H. Y. et al. PANTHER version 11: expanded annotation data from Gene Ontology and Reactome pathways, and data analysis tool enhancements. Nucleic Acids Research 45, D183–D189, https://doi.org/10.1093/nar/gkw1138 (2017).
Untergasser, A. et al. Primer3Plus, an enhanced web interface to Primer3. Nucleic Acids Research 35, W71–W74, https://doi.org/10.1093/nar/gkm306 (2007).
Pfaffl, M. W., Horgan, G. W. & Dempfle, L. Relative expression software tool (REST (c)) for group-wise comparison and statistical analysis of relative expression results in real-time PCR. Nucleic Acids Research 30, https://doi.org/10.1093/nar/30.9.e36 (2002).
Pfaffl, M. W. A new mathematical model for relative quantification in real-time RT-PCR. Nucleic Acids Research 29, https://doi.org/10.1093/nar/29.9.e45 (2001).
Livak, K. J. & Schmittgen, T. D. Analysis of relative gene expression data using real-time quantitative PCR and the 2(T)(-Delta Delta C) method. Methods 25, 402–408, https://doi.org/10.1006/meth.2001.1262 (2001).
CCS was financed by a NERC (natural Environment Research Council) algorithm studentship (NE/G523539/1) and partly by a Scottish Association of Marine Sciences (SAMS) research bursary. MSC, AC, MAST and LSP were financed by NERC core funds to the British Antarctic Survey. The authors would like to thank Tim Brand of the Scottish Association of Marine Science, Oban, UK for nutrient analyses, Elisha Slater for assistance in some of the spawning work and Nick Dunn for initial Q-PCR trials.
The authors declare no competing interests.
Publisher’s note: Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
About this article
Cite this article
Clark, M.S., Suckling, C.C., Cavallo, A. et al. Molecular mechanisms underpinning transgenerational plasticity in the green sea urchin Psammechinus miliaris. Sci Rep 9, 952 (2019). https://doi.org/10.1038/s41598-018-37255-6
Gene Expression Changes after Parental Exposure to Metals in the Sea Urchin Affect Timing of Genetic Programme of Embryo Development
Gene expression patterns of red sea urchins (Mesocentrotus franciscanus) exposed to different combinations of temperature and pCO2 during early development
BMC Genomics (2021)
Systematic Biology (2021)
Global Ecology and Biogeography (2021)
Ecological Applications (2020)