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The globally threatened Aquatic Warbler (Acrocephalus paludicola) is the rarest migratory songbird in Europe. Before the population declined dramatically after 1960, the Aquatic Warbler was a common species in European mires and river flood¬plains. Today, the global population is estimated to count 27 600 individuals, of which approx. 90 % are concentrated in only three countries during the breeding season: Belarus, Poland and Ukraine. Despite numerous conservation efforts mainly under¬taken in European countries, the population decline has not been stopped. Although the Aquatic Warbler is considered a “European” bird species because of the location of its breeding grounds, it spends up to six months on migration and on the wintering grounds on the African continent. A comprehensive species conservation strategy must therefore include the preservation of African resting and wintering grounds. This study analyses the ecol¬ogy of Aquatic Warbler in its wintering grounds using the example of the Djoudj National Park area in north-western Senegal. The study aims, first, to close knowledge gaps regarding the behaviour and the habitat requirements of Aquatic Warblers during their stay on the wintering grounds to provide a scientific base for long-term species conservation management; second, to assess the importance of the wintering site in the Djoudj area is in a global perspec¬tive; and third, to identify threats to the Djoudj area as a suitable Aquatic Warbler habitat. In a fourth step, science-based management recommendations are formu¬lated to support the ongoing practical conservation work of the Djoudj National Park administration with regard to the Aquatic Warbler. The main outcomes of the study are the following: (I) We confirmed the presence of Aquatic Warblers in the Djoudj area between mid-December and the end of March. (II) The connection between the wintering ground “Djoudj National Park area” and the breeding ground “Biebrza valley” (eastern Poland) was confirmed by the resighting of a ringed Aquatic Warbler individual. (III) The remiges moult of the species was observed under natural conditions for the first time. We confirmed that the Aquatic Warbler undergoes a complete moult on its wintering grounds, following the typical sequence of passerine moult. (IV) Aquatic Warblers occur in shallowly inundated vegetation with dominant stands of Oryza longistaminata, Eleocharis mutata, Scirpus maritimus, Scirpus litto¬ralis and Sporobulus robustus interspersed with small (1–2 m²) areas of open water. The afore mentioned herbaceous species form a homogenous wetland vegetation of approximately 0.6–1.5 m height, with a coverage of 80 % to 100 %. Wild rice (Oryza longistaminata) may provide the most suitable habitat conditions as suggested by the very high density of Aquatic Warblers at sites dominated by this species. Preferential habitat may include a few solitary trees, but open woodland or scrublands are unsuit-able for Aquatic Warbler. Pure stands of cattail (Typha australis) are avoided. The water level in the habitat areas varies between 0 (humid soil) and 40 cm above the ground. Constant inundation seems to be essential, as Aquatic Warblers were never encountered in dry parts of the study area. All known Aquatic Warbler habitats in the study area are influenced by brackish or salty water. (V) During winter Aquatic Warblers use a home range of 3.9 ha (± 1.9) in aver¬age, which is shared with other individuals and species. No territorial behaviour was observed in the winter quarters. (VI) The vegetation and land cover map prepared distinguishes six classes of her¬baceous vegetation and five general land cover classes. (VII) There are 4 729 ha of potential Aquatic Warbler habitat within the study area. (VIII) We estimate the density of the Aquatic Warbler population in the study area to range between 0 and 2.26 individuals per hectare with a total population size of 776 individuals, or 260–4 057 individuals in a 95 % credibility interval. Hence we conclude that 1.1–3.8 % (0.37–19.8 % within the 95 % credibility interval) of the global Aquatic Warbler wintering population are found in the Djoudj area. (VIII) The Aquatic Warbler habitats in the Djoudj area are affected by the inun¬dation regime, water circulation, changes in salinity, grazing, the spread of cattail (Typha australis), the encrustation of vegetation, the protection status of passerine migrator habitats and the expansion of rice cultivation a. Our management proposals for the preservation of existing and the development of new Aquatic Warbler habitats were formulated and incorporated into the Management Plan of the Djoudj National Park 2014–2018.
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.
In Germany, basic data on the biology, ecology and distribution of rare mosquito species are insufficiently recorded leading to knowledge gaps, for example regarding their vector potential. The introduction of new mosquito species and of the pathogens they transmit has increased the risk of diseases previously uncommon in Germany. These circumstances have led to increased efforts within the past 10 years to better understand the spatio-temporal occurrence and underlying habitat binding of mosquito species and to predict their future distribution, particularly with regard to the changing climatic conditions and changing landscape. A reliable morphological and genetic identification was lacking for several native mosquito species, which forms the basis for any robust monitoring within mosquito surveillance programs or insect conservation projects.
The aim of this thesis was to gain detailed knowledge on the current spatial and temporal occurrence, the habitat binding, and morphological and genetic features with regard to species identification for the non-native species Aedes albopictus (Skuse, 1895), the native species of the Aedes Annulipes Group, and the native and rare species Aedes refiki Medschid, 1928, Culex martinii Medschid, 1930 and Culiseta ochroptera (Peus, 1935).
The thesis compares the suitability of the local climate for the persistence of the species Aedes albopictus sporadically observed in Jena (Thuringia) from 2015 to 2018 with two populations in southern Germany. The focus was on the analysis of extreme winter temperatures and the duration below selected temperature thresholds. In addition to critical temperature conditions, aquatic habitat conditions were of importance. The results of this study suggest that the population could become established in the long term.
Through the monitoring conducted for this thesis, the very rare mosquito species Aedes refiki, Culex martinii in Thuringia and Culiseta ochroptera were rediscovered at several sites in northern and eastern Germany. It was possible to add new information on habitat binding, distribution and abundance for the considered mosquito species. The survival of these rare native mosquito species depends on the preservation of a few remaining habitats. In addition, it can be assumed that these species will become even rarer with future climate change in Germany and, therefore, should be considered endangered. In contrast, other mosquito species could benefit from an increase in average temperatures or precipitation in individual cases.
Due to the contribution to species identification, difficulties in the morphological and genetic identification of selected mosquito species native to Germany could be dispelled. Three forms each were assigned to the known morphological variants of Aedes refiki and Culiseta ochroptera and their peculiarities were described, as well as a new character for species identification was highlighted in the case of Culiseta ochroptera. Generated CO1 mtDNA sequences provide the first DNA-barcodes of Aedes refiki and Culex martinii for Germany.
In five native mosquito species of the Aedes Annulipes Group, twenty types of aberrant tarsal claws were illustrated and described in their morphology. Morphological peculiarities and an asymmetrical occurrence of the aberrant claw types were observed and possible causes for their development were discussed. Together with the development of a basic blueprint of mosquito tarsal claws, the results opened another field of research for the taxonomy, developmental biology and aquatic ecology of arthropods.