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There is an increasingly urgent need to understand and predict how organisms will cope with the environmental consequences of global climate change. Adaptation in any form can be mediated by genetic adaptation and/or by phenotypic plasticity. Disentangling these two adaptive processes is critical in understanding and predicting adaptive responses to environmental change. Usually, disentangling genetic adaptation from phenotypic plasticity requires common garden experiments conducted under controlled laboratory conditions. While these experiments are powerful, it is often difficult to translate the results into natural populations and extrapolate to naturally occurring phenotypic variation. One solution to this problem is provided by the many examples of invasive species that exhibit wide phenotypic variation and that reproduce asexually. Besides selecting the appropriate in situ model, one must carefully choose a relevant trait to investigate. Ecomorphology has been a central theme in evolutionary biology because it reflects how organisms can adapt to their environment through their morphology. Intraspecific ecomorphological studies are especially well suited to identify adaptive pressures and provide insights into the microevolutionary mechanisms leading to the phenotypic differentiation.
One excellent candidate for an intraspecific ecomorphological study aiming to understand adaptation through genetic adaptation and phenotypic plasticity is the invasive New Zealand mudsnail Potamopyrgus antipodarum Gray (1853). This ovoviviparous snail features high variability in shell morphology and has successfully invaded a wide range of fresh- and brackish water habitats around the world. The evolutionary and ecological situations in this species’ native and invasive ranges is drastically different. In New Zealand, P. antipodarum’s native range, sexual and asexual individuals coexist and experience selective pressure by sterilizing endoparasites. By contrast, only a few asexual lineages have been established in invaded regions around the globe, where parasite infection is extremely rare. Here, we took advantage of the low genetic diversity among asexually reproducing European individuals in an attempt to characterize the relative contribution of genetic variation and phenotypic plasticity to the wide variation in shell morphology of this snail.
Analysing the ecomorphology of 425 European P. antipodarum in a geometric-morphometric framework, using brood size as proxy for fecundity, and mtDNA and nuclear SNPs to account for relatedness and identify reproductive mode, we hypothesized that 1) shell variation in the invasive range should be adaptive with respect to colonization of novel habitats, and 2) at least some of the variation might be caused by phenotypic plasticity. We then expanded our ecomorphological scope by analysing 996 native specimens, expecting 1) genetic and morphological diversity to be higher in the native range compared to invaded regions; 2) morphological diversity to be higher in sexual compared to asexual individuals according to the frozen niche hypothesis; and 3) shell morphology to be habitat specific, hence adaptative. In a last part, we used computational fluid dynamics simulations to calculate relative drag and lift forces of three shell morphologies (globular, intermediate, and slender). Here, we tested the overall hypothesis that shell morphology in gastropods is an adaptation against dislodgement through lift rather than drag forces, which would explain the counterintuitive presence of wider shells with shorter spires in lotic environments. With a final flow tank experiment, we tested the specific hypothesis that the dislocation velocity of living snails is positively linked to foot size, and that the latter can be predicted by shell morphology, in particular the aperture area as assumed by several authors.
As expected, we found genetic and morphological diversity to be higher in native than in invasive snails, but surprisingly no higher morphological diversity in sexual versus asexual individuals. The relationships between shell morphology, habitat, and fecundity were complex. Shape variation was primarily linked to genetic relatedness, but specific environmental factors including flow rate induced similar shell shapes. By contrast, shell size was largely explained by environmental factors. Fecundity was correlated with size, but showed trade-offs with shape in increasingly extreme conditions. With increasing flow and in smaller habitats such as springs, the trend of shell shape becoming wider was reversed, i.e. snails with slender shells were brooding more embryos. This increase in fitness was explained by our CFD simulations: in lotic habitats, slender shells experience less drag and lift forces compared to globular shells. We found no correlation between foot size and shell shape or aperture area showing that the assumed aperture/foot area correlation should be used with caution and cannot be generalized for all aquatic gastropod species. Finally, shell morphology and foot size were not related to dislodgement speed in our flow tank experiment. We concluded that the relationship of shell morphology and flow velocity is more complex than assumed. Hence, other traits must play a major role in decreasing dislodgement risk in stream gastropods, e.g. specific behaviours or pedal mucus stickiness. Although we did not find that globular shells are adaptations decreasing dislodgement risk, we cannot rule out that they are still flow related adaptations. For instance, globular shells are more crush-resistant and might therefore represent a flow adaptation in terms of diminishing damage caused by tumbling after dislodgement or against lotic specific crush-type predators.
At this point, we can conclude that shell morphology in P. antipodarum varies at least in part as an adaptation to specific environmental factors. This study shows how essential it is to reveal how plastic, genetically as well as phenotypically, adaptive traits in species can be and to identify the causal factors and how these adaptations affect the fitness in order to better predict how organisms will cope with changing environmental conditions.
Abstract
The neritid snail Theodoxus fluviatilis has formed regional subgroups in northern Europe, where it appears in both freshwater (FW) and brackish water (BW) in coastal areas of the Baltic Sea. These ecotypes show clear differences in osmotolerance and in the modes of accumulating organic osmolytes under hyperosmotic stress. We reasoned that the expression patterns of soluble proteins in the two ecotypes may differ as well. BW snails have to deal with a higher salinity (up to 20‰) than FW snails (0.5‰) and also cope with frequent fluctuations in environmental salinity that occur after heavy rains or evaporation caused by extended periods of intense sunshine. Therefore, the protein expression patterns of specimens collected at five different FW and BW sites were analyzed using 2D SDS‐PAGE, mass spectrometry, and sequence comparisons based on a transcriptome database for Theodoxus fluviatilis. We identified 89 differentially expressed proteins. The differences in the expression between FW and BW snails may be due to phenotypic plasticity, but may also be determined by local genetic adaptations. Among the differentially expressed proteins, 19 proteins seem to be of special interest as they may be involved in mediating the higher tolerance of BW animals towards environmental change compared with FW animals.
Abstract
Surface waters are warming due to climate change, potentially pushing aquatic organisms closer to their thermal tolerance limits. However, cyanobacterial blooms are expected to occur more often with rising temperature, increasing the likelihood of poor‐quality food available for herbivorous zooplankton. Zooplankton can adapt locally by genetic differentiation or via adaptive phenotypic plasticity to increasing temperatures, but there is limited knowledge on how these processes may be affected by food quality limitation imposed by cyanobacteria.
To test the effects of cyanobacteria‐mediated food quality on local temperature adaptation, we measured juvenile somatic growth and reproduction of five Daphnia magna clones from different latitudinal origin grown on three food qualities at 20, 24, and 28°C. Additionally we estimated short‐term heat tolerance, measured as knockout time (time to immobility) at lethally high temperature, of two clones acclimated to the three temperatures and two food quality levels to test for the effects of food quality on adaptive plastic responses.
As expected, clones from lower latitudes showed on average better somatic growth and reproduction than clones from higher latitudes at higher temperatures. However, the difference in somatic growth diminished with increasing cyanobacteria abundance in the diet, suggesting constraints on local genetic adaptation under predicted decreases in food quality. As expected, short‐term heat tolerance of the clones generally increased with increasing acclimation temperature. However, heat tolerance of animals acclimated to the highest temperature was larger when grown at medium than at good food quality, whereas the opposite response was observed for animals acclimated to the lowest temperature. This suggests a better adaptive phenotypic response of animals to elevated temperatures under higher cyanobacteria abundance, and thus shows an opposite pattern to the results for somatic growth.
Overall, we demonstrate that food quality limitation can mediate responses of D. magna life history traits and heat tolerance to increasing temperatures, and that the effects differ depending on the time scale studied, that is, mid‐term (somatic growth) versus short‐term (tolerance to acute heat stress). These aspects will need further attention to accurately predict of how organisms will cope with future global warming by local adaptation and adaptive phenotypic plasticity.
How well populations can cope with global warming will often depend on the evolutionary potential and plasticity of their temperature-sensitive, fitness-relevant traits. In Bechstein's bats (Myotis bechsteinii), body size has increased over the last decades in response to warmer summers. If this trend continues it may threaten populations as larger females exhibit higher mortality. To assess the evolutionary potential of body size, we applied a Bayesian ‘animal model’ to estimate additive genetic variance, heritability and evolvability of body size, based on a 25-year pedigree of 332 wild females. Both heritability and additive genetic variance were reduced in hot summers compared to average and cold summers, while evolvability of body size was generally low. This suggests that the observed increase in body size was mostly driven by phenotypic plasticity. Thus, if warm summers continue to become more frequent, body size likely increases further and the resulting fitness loss could threaten populations.
Currently, poleward range expansions are observed in many taxa, often in response to anthropogenic climate change. At the expanding front, populations likely face cooler and more variable temperature conditions, imposing thermal selection. This may result in changes in trait means or plasticity, the relative contribution of which is not well understood. We, here, investigate evolutionary change in range‐expanding populations of the butterfly Pieris mannii, by comparing populations from the core and the newly established northern range under laboratory conditions. We observed both changes in trait means and in thermal reaction norms. Range‐expanding populations showed a more rapid development, potentially indicative of counter‐gradient variation and an increased cold tolerance compared with core populations. Genotype‐environment interactions prevailed in all associated traits, such that the above differences were restricted to cooler environmental conditions. In range‐expanding populations, plasticity was decreased in developmental traits enabling relatively rapid growth even under cooler conditions but increased in cold tolerance arguably promoting higher activity under thermally challenging conditions. Notably, these changes must have occurred within a time period of ca. 10 years only. Our results suggest, in line with contemporary theory, that the evolution of plasticity may play a hitherto underestimated role for adaptation to climatic variation. However, rather than generally increased or decreased levels of plasticity, our results indicate fine‐tuned, trait‐specific evolutionary responses to increase fitness in novel environments.
How organisms that are part of the same trophic network respond to environmental variability over small spatial scales has been studied in a multitude of systems. Prevailing theory suggests a large role for plasticity in key traits among interacting species that allows matching of life cycles or life‐history traits across environmental gradients, for instance insects tracking host‐plant phenology across variable environments (Posledovich et al. 2018). A key aspect that remains understudied is the extent of intrapopulation variability in plasticity and whether stressful conditions canalize plasticity to an optimal level, or alternatively if variation in plasticity indeed could increase fitness in itself via alternative strategies. In a From the Cover article in this issue of Molecular Ecology, Kahilainen et al. (2022) investigate this issue in a classical insect study system, the metapopulation of the Glanville fritillary butterfly (Melitea cinxia) in the Åland archipelago of Finland. The authors first establish how a key host plant responds to water limitation, then quantify among‐family variation in larval growth and development across control and water‐limited host plants. Finally, they use RNA sequencing to gain mechanistic insights into some of these among‐family differences in larval performance in response to host‐plant variation, finding results suggesting the existence of heritable, intrapopulation variability in ecologically relevant plasticity. This final step represents a critically important and often overlooked component of efforts to predict sensitivity of biological systems to changing environmental conditions, since it provides a key metric of adaptive resilience present in the system.
Unstable environments and habitats changing due to climate change force individuals to either respond by genetic adaptation, phenotypic plasticity or by dispersal to suitable environments. Theodoxus fluviatilis (Linneaus, 1758) is a good study organisms when researching phenotypic plasticity and genetic adaptation as it naturally appears in freshwater (FW) as well as brackish water (BW) and thus inhabits a wide range of environmental salinities (0-18‰). It is a euryhaline snail that can be found in shallow waters with stony ground or on Fucus spp. and has formed regional subgroups. The brackish water and the freshwater subgroups are spatially separated and the species cannot be found in areas inbetween, e.g. estuaries.
The species shows great variability in shell patterning and shell size and there is still debate whether the subgroups are distinguishable by these traits or not. The mitochdrial RNA marker cytochrome c subunit I did not show differences between the subgroups indicating that they must be closely related, but salinity tolerance has been observed to be higher in BW snails. This might be caused by the different protein expression patterns and osmolyte accumulation (measured as ninhydrin-positive substances) observed in this species in previous studies. The exact mechanisms regulating protein expression and osmolyte accumulation, however, are not fully understood yet.
Data collected for this thesis shows differences in shell size and suggests a less strict grouping of FW and BW individuals as shell sizes of one FW site are more similar to BW individuals than the other FW ones. A better salinity tolerance towards high salinities and a higher physiological salinity limit of BW snails was confirmed and extended by demonstrating an expanded tolerance range through slow acclimation to challenging salinities in snails from both subgroups. This was achieved by a shift in the slope of their reaction norms that was much more pronounced in BW snails than FW ones. S3 individuals showed a shift similar to that of BW individuals. The data for the salinity tolerance indicates that the underlying mechanism for these tolerances are a combination of phenotypic plasticity and genetic adaptation. Despite an acclimation and shift in the slope of the reaction norms and therefore an increased tolerance towards high salinities (plasticity) FW individuals from two collection sites were not able to cope with salinities as high as BW individuals (local adaptation). The general ability to mobilise free amino acids (FAA) as organic osmolytes was not the reason for this tolerance difference. Individuals from BW and FW sites were capable of accumulating quantities of FAAs equally well. Proline, alanine and urea were the most important components of the accumulated cocktail of organic osmolytes. Even though the total amount of FAAs accumulated under hyperosmotic conditions was the same in both subgroups, there were differences in the metabolic pathways involved in osmolyte accumulation in the foot muscle. The data indicates that the hydrolysis of storage proteins and the synthesis of proline and alanine are the main processes to avoid detrimental body volume shrinkage in T. fluviatilis. While FW individuals seemed to rely on the degradation of proteins and synthesis of alanine, BW individuals depended on newly synthesising proline and alanine and accumulating urea as a side product of transamination. The accumulation of urea is a new finding in aquatic living snails and has not been reported as a mechanism to avoid cell volume shrinkage in these animals.
Differing protein expression patterns were observed under control conditions across all collection sites. 9 spots showed volume changes in BW snails opposite to those of FW snails from collection sites S1 and S2. For 6 of those spots, S3 individuals showed patterns similar to those of BW individuals and for the remaining 3 they showed patterns similar to those of FW animals. The patterns observed when exposing snails to hypo- or hyperosmotic stress were not conclusive in relation to pinpointing individual spots that show the same pattern in all collection sites, but revealed the heterogeneity of protein expression in snails from the different collection sites and in the process of osmoregulation. It also showed the general tendency of protein reduction when snails where under osmotic stress of either kind (hypo- or hyperosmotic), which supports the hypothesis of storage protein degradation.
The investigation of an ANP-receptor showed two variations of the encoding sequence expressed in T. fluviatilis. S3 individuals as well as BW individuals were found to express one type, while FW individuals, with the exception of one sample expressed the other type. This showed that the FW subgroup of T. fluviatilis seems to be more heterogeneous than the BW subgroup, but also raises the question of the dispersal history of this species. The collected data indicates that T. fluviatilis individuals are firstly capable of surviving the acidity of a duck's gizzard and secondly can tolerate acute salinity changes to 16‰ when introduced into a new environment. Hence, if snails from the FW were to be transported to waters with a salinity of up to 16‰ by man, bird, drifting plants or some other means of transport, they would most likely survive and possibly be able to thrive and spread.
Photosynthetic activity in both algae and cyanobacteria changes in response to cues of predation
(2022)
A plethora of adaptive responses to predation has been described in microscopic aquatic producers. Although the energetic costs of these responses are expected, with their consequences going far beyond an individual, their underlying molecular and metabolic mechanisms are not fully known. One, so far hardly considered, is if and how the photosynthetic efficiency of phytoplankton might change in response to the predation cues. Our main aim was to identify such responses in phytoplankton and to detect if they are taxon-specific. We exposed seven algae and seven cyanobacteria species to the chemical cues of an efficient consumer, Daphnia magna, which was fed either a green alga, Acutodesmus obliquus, or a cyanobacterium, Synechococcus elongatus (kairomone and alarm cues), or was not fed (kairomone alone). In most algal and cyanobacterial species studied, the quantum yield of photosystem II increased in response to predator fed cyanobacterium, whereas in most of these species the yield did not change in response to predator fed alga. Also, cyanobacteria tended not to respond to a non-feeding predator. The modal qualitative responses of the electron transport rate were similar to those of the quantum yield. To our best knowledge, the results presented here are the broadest scan of photosystem II responses in the predation context so far.
In times of recent climate change, mechanisms to deal with different environments (e.g. via dispersal to other habitats, or via in-situ responses such as genetic adaptation or phenotypic plasticity) are essential. In regions showing seasonality, organisms are already adapted to regular and, thus, often predictable environmental changes. One well-known strategy to survive periods of food shortage, especially during the winter, is hibernation. Although hibernation is already an adaptation to overcome unfavourable conditions, the optimal timing of hibernation to match for example food abundance peaks is likely to be influenced by changing climatic conditions, as expected during human-induced global change. Thus, the ability to respond to changes in optimal timing of hibernation can be crucial for organisms. All hibernators are positioned at the slow end of the slow-fast life history continuum. Longevity combined with a low annual reproductive output can result in slow recovery from population crashes and is expected to be associated with slow genetic adaptation. Therefore, it is assumed that phenotypic plasticity, a rather rapid and sometimes reversible process, is a crucial mechanism in long-lived organisms to adapt to changing environments. However, how differences in individual hibernation behaviour influence mortality and whether individuals are plastic with respect to their hibernation behaviour are largely unknown.
Recent studies suggest that climatic change can influence hibernation behaviour in various species differently, in a positive or negative way. Female Columbian ground squirrels (Urocitellus columbianus) delayed their emergence from hibernation with later snow melt and lower spring temperatures. Next to the environmental impact, emergence date showed a moderate heritability in female Columbian ground squirrels. Yellow-bellied marmots (Marmota flaviventris) emerged earlier from hibernation with warmer spring temperatures which resulted in a longer growing period for their offspring and, therefore, higher survival rates. In contrast, in alpine marmots (Marmota marmota) lower snow cover due to higher temperatures and, thus, less isolation led to lower juvenile survival. Negative effects, such as reduced juvenile survival, would be of high concern, especially for long-lived species with a low reproductive output.
Bats are exceptionally long-lived compared to other mammals of the same size and often show a low reproductive output with one offspring per year. This is especially true in the temperate zone where bats, furthermore, are characterized by seasonality and depend on hibernation during winter period to survive food and water shortage. Because bats are of high conservation concern it is of prime importance to understand their ability to respond to different climatic conditions and associated mortality costs.
The basis of this study was a five-year data set of 1047 RFID-tagged individuals from two bat species, Natterer’s bats (Myotis nattereri) and Daubenton’s bats (Myotis daubentonii), that were automatically tracked when entering or leaving the joint hibernaculum, “Brunnen Meyer”, located in north-western Germany. The two species are similar sized, share demographical traits and often occupy the same areas. Nevertheless, they differ in their foraging strategy and activity pattern during hibernation period. Natterer’s bats are able to glean insects from surfaces, even at low temperatures. Daubenton’s bats depend on flying arthropods and, thus, warmer temperatures. And indeed there is evidence that Natterer’s bats are able to hunt during hibernation period, while in Daubenton’s bats a lack of feeding during the hibernation period is suggested. Furthermore, Natterer’s bats are characterized by a higher activity at the hibernaculum throughout the hibernation period, while Daubenton’s bats on average arrive earlier, stay inactive through the winter and leave later in spring.
In both species, the aim was to investigate the impact of their individual hibernation behaviour, precisely the timing of departure in late winter and early spring, on mortality, their adjustment of departure timing to the North Atlantic Oscillation Index (NAO), as well as differences within and between the two species from 2011 until 2015.
To later on estimate the potential mortality costs of departure timing, gaining knowledge about the seasonal survival pattern (winter vs. summer) in the two species was a first necessity. In birds, particularly small species were described as winter-regulated populations with a higher mortality during winter. In contrast, in hibernating mammal species, such as bats, a relatively lower or similar winter survival compared to summer survival was shown. In this study, the analysed data demonstrated that the winter 2010/2011 was exceptionally catastrophic in Natterer’s bats and did not impact Daubenton’s bats. When excluding this catastrophic winter in Natterer’ bats, our results revealed a stable winter-summer-survival difference (higher winter and lower summer survival) in adult Natterer’s and Daubenton’s bats, with inter-annual variation in the level of survival which indicates a potential environmental impact on survival. This winter-summer survival pattern is in line with the survival pattern shown for other hibernators. Juveniles always had a lower survival rate than adult bats in both species. Nevertheless, the extent to which the species differ between seasons and age classes was stronger in Daubenton’s bats. They always showed a slightly higher winter survival and a lower summer survival than Natterer’s bats. Together with the catastrophic winter 2010/2011 in Natterer’s bats, this indicates a species-specific sensitivity to the timing of specific weather events which is in line with their foraging strategies and activity pattern during hibernation period.
With respect to emergence behaviour from the hibernaculum, the results of this study suggest considerable differences among individuals within as well as between bat species. In comparison to Daubenton’s bats, Natterer’s bats tuned their emergence more closely to weather conditions, specifically the NAO, a large scale weather index related to winter severity, and showed individual variation in behavioural plasticity. In Daubenton’s bats only the females responded to changing conditions and left earlier in individually-experienced warmer and milder winters, comparable to Natterer’s bats females. A potential reason might be reproductive advantages for the females resulting in a longer growing period for their offspring. The shown higher winter survival in adult bats of both species indicated already higher energy expenditure outside the hibernaculum. Thus, leaving early, being active and staying outside longer by itself bore a risk (exposure risk effect). Under consideration of longer exposure times, early departing individuals had on top of that an increased risk to die. This was not given in each year, but a species- and year-specific pattern was revealed. Natterer’s bats were only significantly affected by early departure in 2011, while the remaining years show no significant additional risk of leaving early. In Daubenton’s bats, the years 2014 and 2015 were associated with a significantly higher mortality of leaving early. This is in line with the hypothesis that Daubenton’s bats might not be able to hunt for insects leaving too early and do so as a best out of a bad job. Nevertheless, the year-specific pattern suggests that early bats might profit from advantageous weather conditions during early spring.
An additional hint for an environmental impact on early bat survival in at least Daubenton’s bats is that the median proportion of night hours above 3 °C within five days after departure was included in the model with the lowest AIC. However, the effect was not strong enough to be selected as the best model and, therefore, further analyses are needed to investigate this first hint.
In conclusion, the reduced winter survival of juveniles compared to adults highlights the importance of considering age class effects in studies that investigate seasonal survival patterns. The stable species-specific winter-summer-survival difference with a higher winter survival compared to summer survival, as well as the one catastrophic winter in Natterer’s bats underline the importance of including seasonal survival patterns in assessing potential fitness costs of changed behaviour. Furthermore, our results suggest that long-lived hibernating bat species have the potential to plastically adjust to changing climatic conditions, but this potential differs between species. Among-individual differences in emergence together with species-specific mortality costs of early emergence suggest the potential for natural selection to shape hibernation phenology. In summary, our findings suggest species-, population- and group-specific differences in the ability to respond to changing environments and, therefore, underline the necessity to further investigate local responses in various organisms to estimate consequences of recent climate change on a wider range.