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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
Climate change may force organisms to adapt genetically or plastically to new environmental conditions. Invasive species show remarkable potential for rapid adaptation. The ovoviviparous New Zealand mud snail (NZMS), Potamopyrgus antipodarum, has successfully established across Europe with two clonally reproducing mitochondrial lineages since its arrival in the first half of the 19th century. Its remarkable variation in shell morphology was shown to be fitness relevant. We investigated the effects of temperature on shell morphology across 11 populations from Germany and the Iberian Peninsula in a common garden across three temperatures. We analyzed size and shape using geometric morphometrics. For both, we compared reaction norms and estimated heritabilities. For size, the interaction of temperature and haplotype explained about 50% of the total variance. We also observed more genotype by environment interactions indicating a higher degree of population differentiation than in shape. Across the three temperatures, size followed the expectations of the temperature‐size rule, with individuals growing larger in cold environments. Changes in shape may have compensated for changes in size affecting space for brooding embryos. Heritability estimates were relatively high. As indicated by the very low coefficients of variation for clonal repeatability (CVA), they can probably not be compared in absolute terms. However, they showed some sensitivity to temperature, in haplotype t more so than in z, which was only found in Portugal. The low CVA values indicate that genetic variation among European populations is still restricted with a low potential to react to selection. A considerable fraction of the genetic variation was due to differences between the clonal lineages. The NZMS has apparently not been long enough in Europe to accumulate significant genetic variation relevant for morphological adaptation. As temperature is obviously not the sole factor influencing shell morphology, their interaction will probably not be a factor limiting population persistence under a warming climate in Europe.
Abstract
Understanding how organisms adapt to complex environments is a central goal of evolutionary biology and ecology. This issue is of special interest in the current era of rapidly changing climatic conditions. Here, we investigate clinal variation and plastic responses in life history, morphology and physiology in the butterfly Pieris napi along a pan‐European gradient by exposing butterflies raised in captivity to different temperatures. We found clinal variation in body size, growth rates and concomitant development time, wing aspect ratio, wing melanization and heat tolerance. Individuals from warmer environments were more heat‐tolerant and had less melanised wings and a shorter development, but still they were larger than individuals from cooler environments. These findings suggest selection for rapid growth in the warmth and for wing melanization in the cold, and thus fine‐tuned genetic adaptation to local climates. Irrespective of the origin of butterflies, the effects of higher developmental temperature were largely as expected, speeding up development; reducing body size, potential metabolic activity and wing melanization; while increasing heat tolerance. At least in part, these patterns likely reflect adaptive phenotypic plasticity. In summary, our study revealed pronounced plastic and genetic responses, which may indicate high adaptive capacities in our study organism. Whether this may help such species, though, to deal with current climate change needs further investigation, as clinal patterns have typically evolved over long periods.
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.