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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.
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.