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In agricultural grasslands, management practice highly determines reproductive success for ground-nesting bird species. The most effective conservation measure is the delay of first mowing dates until broods fledge or bird friendly mowing. Late mowing often implies economical losses for farmers and may increase land use abandonment, which will, in turn, cause habitat deterioration. Thus, grassland bird conservation involves the challenge to protect broods against land use and to promote an appropriate management to sustain habitat quality at the same time. Because of their late and extended breeding season Corncrakes Crex crex are in particular vulnerable to frequent mowing which increases nest destruction, chick mortality and habitat loss.
This thesis aims to gain knowledge on favourable habitat characteristics and brood protection in relation with grassland management to derive implications for the conservation of Corncrake breeding sites in floodplain meadows. Study area is the Lower Oder Valley National Park in northeastern Germany that holds a Corncrake population of 50 to 250 calling males. The study covered two study periods, before (1998-2000) and after (2012-2015) the implementation of new Corncrake conservation measures allowing inferences on the effects of different timing and intensity of mowing for brood protection and habitat conservation.
Breeding was only confirmed on meadows with high forb cover, low sedge cover, low litter heights and a close location to ditches. Radio-tracked females preferred areas with high cover of forbs (> 30%) and a distinct relief heterogeneity, which was associated with increased vegetation diversity. Vegetation characteristics on sites with day calling activity of males showed more similarity with breeding sites than with sites only used for nocturnal calling, supporting the assumption that diurnal calling indicates the occurrence of females. Favoured vegetation structure was best provided by mowing in the preceding year. Low-intensity grazing was less effective in reducing litter and sedge cover, especially when conducted late in the season. In the absence of management, meadows rapidly overgrow and dense litter accumulates from dead plant material in eutrophic floodplains, which increases walking resistance for Corncrakes and may impede prey accessibility. Plant species richness and forb cover declined after land use cessation. Male Corncrakes abandoned calling sites on meadows unmanaged for longer periods.
Besides the availability of suitable nesting sites, food supply and nest predation risk are also related to vegetation structure and may indirectly influence the habitat quality. Faecal samples of Corncrakes consisted mainly of beetles and their larvae, followed by snails, spiders and earthworms. Invertebrate biomass, sampled with pitfall-traps, was twice as high, the numbers of large ground beetles even five times higher on previously unmanaged than on managed meadows. Invertebrate abundance was highest in the first and second years after land use abandonment, but strongly decreased afterwards to a similar level like under annual management. Therefore, unmown refuge strips for Corncrake protection and alternating mowing also enhance invertebrate prey resources in floodplain meadows.
Mammals caused the majority of all observed artificial ground nest predations. Nest predation risk was higher on previously unmanaged than on managed sites. Unmanaged meadows probably attract mammalian predators, because they provide a more favourable vegetation structure for foraging and harbour high numbers of small rodents, increasing also the risk of incidental nest predations. These findings suggest that an annual removal of vegetation, if conducted late in the season to protect grassland birds may reduce predation risk of ground nests in the subsequent year.
Whereas during 1998-2000 half of the study area was managed by the end of July, land use was delayed on meadows occupied by Corncrakes until at least 15 July or 15 August during 2012-2015. On meadows mown between 15 July and 15 August refuge strips were applied. The majority of Corncrake broods were started in the second half of May and mowing postponement until 15 August allows 80% of chicks to fledge without disturbance in the study area. In 65% of broods chicks reach independence (> 14 days old) until 15 July and can be protected by Corncrake friendly mowing because then they are large enough to successfully escape during mowing. Both adults and chicks survived in 10 m wide refuge strips. Because most birds tried to leave the unmown block for the first time when it was up to 30 m wide and only 15 to 30 m wide strips served as temporary habitat for unfledged chicks from mowing to departure, 10 m should be considered as the absolute minimum width for refuge strips.
The strong reduction of land use especially during July should have allowed more chicks to survive until fledging in 2012-2015 than 1998-2000. Besides the protection of nests and higher chick survival, the decline of mowing intensity increased the extent of habitat available for second breeding attempts. In 2012-2015, broods were initiated until late July in the study area. Male Corncrakes showed continuous arrival and departure during the breeding season. Similar departure rates were estimated by a multi-state occupancy model and for radio-tracked males in the same study area and periods, which both left their home ranges spontaneous and due to the impact of mowing. Compared to 1998-2000, total departure of males during June and July was reduced by 50% in 2012-2015, when more calling sites were protected from mowing. Although male Corncrakes show high intra-seasonal dispersal due to their sequential polygamous breeding system, postponed land use should have increased mating opportunities and re-nesting at first breeding sites.
Therefore, future directions of Corncrake conservation in eutrophic floodplains should address the increase of annual late mowing to protect broods and maintain favourable habitat conditions by creating a more flexible mowing regime adjusted to actual occurrence of Corncrakes. This requires expert advice to farmers based on an intense monitoring of calling Corncrakes. Repeated nocturnal surveys during May and June are highly recommended because low detection probability in combination with constant departure substantially underestimated the number of males present. Additionally, diurnal calling activity could improve the identification of breeding sites and timing could be used to estimate chick age in July to select sites for Corncrake friendly mowing. Because currently late mowing dates are unattractive for farmers conservation actions should along with financial compensations for mowing after 15 August promote the utilization of late-cut grass with poor nutrient quality for combustion. Energy production could provide an alternative income for farmers operating in conservation areas with delayed land use dates and will increase their acceptance of Corncrake protection measures.
American and European foulbrood (AFB and EFB) are devastating bacterial brood diseases of honey bees (Apis mellifera), which cause colony and economic losses worldwide. The causative agent of AFB, Paenibacillus larvae, are grouped into different ERIC-genotypes (Enterobacterial repetitive intergenic consensus) the two most common of which are ERIC I and ERIC II. In the field, the differentiation between the symptoms of AFB and EFB (caused by Melissococcus plutonius) can be difficult. The differentiation between the ERIC-genotypes in the field based on the symptoms is not possible at all. The differentiation between the ERIC-genotypes of P. larvae during diagnosis can help to understand the spread of the AFB disease. Hence, a tool capable of detection and distinction between the bacterial brood diseases and the P. larvae-genotypes is needed. For the optimal prevention of disease spread, the diagnosis needs to be fast, cheap and reliable.
This study focuses on the development of a diagnostic sandwich ELISA and a lateral flow device (LFD) for the detection and distinction of EFB and AFB, including the differentiation of the two main occurring P. larvae genotypes. The therefore necessary specific monoclonal antibodies (mAbs) were obtained by immunizing mice with M. plutonius or P. larvae strains belonging to either ERC I or ERIC II. The generated mAbs were characterized for their specificity towards the target bacteria and for their cross reactivity towards other bee-associated bacteria. The screening for suitable mAbs resulted in two specific mAbs against M. plutonius, two against P. larvae in general and two against ERIC II. In combination with the anti-P. larvae mAbs, the anti-ERIC II mAbs were used for genotyping.
In order to evaluate the suitability of the mAbs, their antigens were identified. The target antigens of the produced mAbs turned out to be proteins that could be of further interest as they seem to be involved in the pathogenesis and host-pathogen-interaction. The mAbs with the same antigens were used in the sandwich ELISA for testing the cross reactivity and strain detection. Suitable mAb combinations were used for LFD production. The LFDs were then successfully tested against several field isolates of AFB and EFB causing agents and no cross reactivity with bee-associated bacteria was detected. The P. larvae strains used for mAb testing were genotyped to obtain information about the respective genetic variance. In the process atypical P. larvae strains were identified and further characterized using the generated mAbs. The ability of the mAbs to also recognise the atypical strains as well indicates that the mAbs bind to an antigen that is common among different P. larvae strains.
All in all, a fast tool for detection and differentiation of EFB, AFB and the two ERIC-genotypes was developed that has to be further tested for its reliability in the field.
Emerging infectious diseases are among the greatest threats to human, animal and plant health as well as to global biodiversity. They often arise following the human-mediated transport of a pathogen beyond its natural geographic range, where host species are typically not well adapted due to a lack of co-evolutionary host-pathogen dynamics. One such pathogen is the fungus Pseudogymnoascus destructans (Pd), which causes White-Nose disease in hibernating bats. While Pd was first observed in North America where it has led to mass-mortalities in some bat species, the pathogen originates from Eurasia where infection is not associated with mortality. Most of the Pd research has focused on the invasive North American range, which likely underestimated the genetic structure of the pathogen and the role it might play in the disease dynamics.
In my work, I therefore evaluated the genetic structure of Pd in its native range with the aim of uncovering cryptic diversity and further use population genetic data to address some key ecological aspects of the disease dynamics. With an extensive reference collection of more than 5,000 isolates from 27 countries I first demonstrated strong differentiation between two monophyletic clades across several genetic measures (multi-locus genotypes, full genome long-read sequencing and Illumina NovaSeq on isolate pools). These findings are consistent with the presence of two cryptic species which are both causative agents of bat White-Nose disease (‘Pd-1’, which corresponds to P. destructans sensu stricto, and ‘Pd-2’). Both species exist in the same geographic range and co-occur in the same hibernacula (i.e., in sympatry), though with specialised host preferences. I further described the fine-scale population structure in Eurasia which revealed that most genotypes are unique to single hibernacula (more than 95% of genotypes). The associated differences in microsatellite allele frequencies among hibernacula allowed the use of assignment methods to assign the North American isolates (exclusively Pd-1) to regions in Eurasia. Hence, a region in Ukraine (Podilia) is the most likely origin of the North American introduction.
To gain further insights into the spatial and temporal dynamics of White-Nose disease on a localised scale, several hibernacula were sampled with high intensity (artificial hibernaculum in Germany and natural karst caves in Bulgaria). Low rates of Pd gene flow were observed even among closely situated hibernacula. This indicates that Pd does not remain viable on bats over summer or it would be frequently exchanged among bats (and hence hibernacula) resulting in a homogenous distribution of genotypes. Instead, bats need to become re-infected each hibernation season to explain the yearly re-occurrence of White-Nose disease. Given the distribution and richness of Pd genotypes on hibrnacula walls and infected bats of the same hibernacula, bats become infected from the hibernacula walls when they return after summer. This means that environmental reservoirs exist within hibernacula (i.e., the walls) on which Pd spores persist during bat absence and which drive the yearly re-occurrence of White-Nose disease. In an experimental setup, I confirmed the long-term viability of Pd spores on abiotic substrate for at least two years and furthermore discovered temporal variations in Pd spores’ ability to germinate. In fact, these variations followed a seasonal pattern consistent with the timing of bats absence (reduced germination) and presence (increased germination) and could indicate adaptations of Pd to the bats’ life-cycle. The infection of bats from environmental reservoirs hence seems to be a central aspect of White-Nose disease dynamics and Pd biology.
Pds ability to remain viable for extended periods outside the host increases its risk of being anthropogenically transported and might have played a role in the emergence of White-Nose disease in North America. The existence of a second species (Pd-2) poses a great additional danger to North American bats considering that its introduction there could lead to deaths and associated population declines in so-far unaffected species given what is known about differing host species preferences in Eurasian bats. Even within the native range of Pd, the movement of Pd between differentiated fungal populations could facilitate genetic exchanges (e.g., through sexual reproduction) between genetically distant genotypes. Such genetic exchanges could lead to phenotypic jumps in pathogenicity or host-species preferences and should hence be prevented.
The native range of a pathogen holds great potential to better understand the genetic and ecological basis of a (wildlife) disease. My work informs about the dangers associated with the accidental transport of Pd (and other pathogens) and highlights the need for ‘prezootic’ biosecurity-oriented strategies to prevent disease outbreaks globally. Once a pathogen has arrived in a new geographic range, and particularly if it has environmentally durable spores (as demonstrated for Pd), it will be difficult/impossible to eradicate. Furthermore, a pathogen’s ability to remain viable outside the host and infect them from environmental reservoirs has been associated with an increased risk of species extinctions and needs to be considered when designing management strategies to mitigate disease impact.
For decades, evolutionary biologists have sought to understand the evolution of individual behaviour, physiology and ecology allowing organisms to cope to environmental change. One of the main challenges of current climate change is the unprecedent rate of temperature increase, as well as the increased occurence of extreme heat events. Interindividual response variability opens a whole new area of opportunities to understand how individual phenotypic traits are linked to individual response differences. In colour polymorphic species, colour honestly reflects an individual’s life-history strategy, and each morph may, therefore, represent an alternative life-history strategy. As such, colour polymorphic species, such as the Gouldian finch (Erythrura gouldiae), may be good models to assess how different strategies between morphs are linked to their espective responses to environmental variations. However, polymorphic species have mainly been disregarded for that purpose. In this context, the main aim of this thesis was to understand how the two morphs of the Gouldian finch respond through phenotypic plasticity to simulated heatwaves reaching thermocritical temperatures, and whether such differential responses may help to identify a ‘winner’ and a ‘loser’ morph in the light of climate change. To address these issues, we used an integrative approach including measurements of behavioural (Study 1), physiological (Study 2), and reproductive (Study 3) parameters. The novelty of our approach was to assess the immediate behavioural and physiological response variation of individuals of the two morphs longitudinally across different thermal conditions, as well as the postponed effects of this thermocritical heatwave exposure on their reproductive performance. In this study, although the behavioural responses generally did not differ between morphs or according to temperature intensity, the physiological and reproductive parameters differed in response to morph and temperature intensity. Blackheaded females, in particular, seem highly sensitive to thermocritical heatwaves, as they exhibited decreased body mass and increased oxidative damage during the thermocritical heatwaves, and advanced breeding initiation after these conditions, whereas these variables remained mostly unaffected in black-headed males and red-headed individuals. However, despite some response differences between morphs, both invested similarly in reproduction following intense heatwaves, and the offspring of both morphs were similarly affected. Based on these results, no morph therefore seems to appear more disadvantaged than the other following an intense heatwave, and red- and black-headed Gouldian finches may both be considered as climate stress ‘losers’.
The impact of inbreeding under different environmental conditions and of artificial selection on cold tolerance was investigated in laboratory populations of the tropical butterfly Bicyclus anynana. The investigation focused on (1) the effects of inbreeding on several fitness-related traits and whether inbred individuals are more susceptible to stress, (2) interactions between inbreeding, genetic adaptation to cold stress and environmental conditions, (3) the effects of artificial selection and inbreeding in the adult stage in other developmental stages, and (4) the effect of inbreeding depression on the heat shock response. Environmental conditions are not constant over time; consequently organisms have to deal with environmental changes. Besides naturally fluctuating conditions, human-induced climate change may increase temperature changes as well as the severity of heat or cold waves. Temperature-stress resistance describes an organism’s ability to cope with stressful temperatures. Enhanced resistance to temperature stress can be reached by phenotypic plasticity or genetic adaptation. Plastic organisms are able to react fast to changing environmental conditions, whereas genetic adaptation is more important for long-term adaptation. Natural habitats may also be affected by human impact, causing habitat loss or fragmentation and changes in population structure. A decrease in the population size may result in inbreeding and inbreeding depression (ID). Consequences of inbreeding are well documented, and inbred individuals are predicted to be more sensitive to environmental stress than outbred individuals. The long term persistence of species and populations depends on their ability to adapt to novel conditions which in turn depends on genetic diversity. Therefore, studies of temperature resistance and its evolution in relation to inbreeding are very important. First a higher susceptibility of inbred individuals to environmental stress was determined in different populations of B. anynana. Inbreeding depression was revealed for several fitness-related traits, but not for immunity traits or heat tolerance. Temperature affected most traits, revealing the importance of temperature on ectotherms; just two hours of thermal stress affected important reproductive, life-history and immunity traits already. Importantly though, no evidence were found that inbred individuals are more susceptible to stressful temperatures than outbred individuals. Genetic adaptation and phenotypic plasticity can interact with one another, resulting in genotype-environmental interactions (G x E). The hypotheses tested here were that some genotypes are more plastic than others and that lines with increased cold stress resistance are less plastic with regard to cold resistance than control lines. To induce plastic responses the exposed lines differed in cold tolerance and inbreeding to different temperatures as well as different feeding regimes and measured fitness-related traits. Several interactions were detected in which a selection regime was involved, but these interactions did not show a clear overall pattern. In summary though, findings were that marginal impacts of directional selection and inbreeding on plastic responses and suggest that, at least for my study organism, the genetic architecture of fitness-related traits is not connected with the architecture of plastic responses. The next investigation concerned with the manifestation of genetic adaptation to produce one specific phenotype across development stages and possible trade-offs. The assumption tested was that there is a genetic link between different developmental stages to produce one definite phenotype by imposing selection in the adult stage only. Lines selected for increased cold resistance in the adult stage were used and increased cold resistance throughout all developmental stages was expected. However, higher cold resistance was found only in the adult stage and not in developmental stages. This could be either the result of a resource allocation trade-off between different stages or that there is no cold resistance phenotype. Thus, if selection takes place in the adult stage it does not affect the others. In the last experiment investigation was directed to determine whether there are negative inbreeding effects on the heat shock protein (HSP) response. Under stressful conditions, organisms produce the HSPs and they act as chaperons required for refolding and repairing of stress degraded proteins. Testing was oriented to find if inbreeding as a genetic stressor´ provokes a higher HSP expression and if there is evidence for higher temperature stress susceptibility on inbred individuals. Findings indeed showed a stronger HSP up-regulation in control compared to inbred lines with a negative inbreeding impact occurrence, which may causally underlie inbreeding depression.
The need for the diversification of utilised species has emerged in the present aquaculture
production environment. Shifts in consumer interest, climate change-induced temperature
increases, and major fish disease outbreaks have put a strain on this industry. In this context,
the pikeperch (Sander lucioperca) has become a new target species for aquaculture in Central
Europe. This new aquaculture focus species exhibits high numbers of offspring, fast growth,
and high consumer acceptance. It can also effectively deal with higher temperatures and turbid
water. However, the rate of successful rearing is still low, as various developmental
transformations and environmental effects commonly lead to high mortality rates during the
early ontogenetic stages. The aim of this doctoral project was thus to obtain insight into
embryonic to larval developmental changes during pikeperch ontogeny. Specifically, the times
of change that influence survival were of focus. Based on the available literature, particular
attention was paid to general growth patterns and the connected developmental changes, the
determination of myogenesis gene marker expression changes, and the support of animal
welfare efforts for pikeperch rearing procedures. To achieve the aims of the study, a methodical
setup consisting of morphometric and developmental observations was combined with
transcriptome gene marker analysis for the different ontogenetic stages.
Three developmental phases were differentiated during the embryo-larval transition. Each of
these possessed distinct growth patterns with different growth rates. The intermediate
threshold phase showed internal organ development that focused on digestive, neuronal, and
heart tissues. Three activity phases of myogenesis were determined: during early embryonic
development, before hatching, and after hatching during the larval stages. Therefore, muscle
development seemed to be regulated to balance energy expenditures. Additionally, two
coinciding skeletogenic phases were found. Furthermore, a cell line from whole embryos was
developed to support the replacement of animals in future experimental setups. A software
system for video analyses was developed to support rearing procedures in aquaculture
facilities. This prototype can be used to automate the counting of specimens and thus allows
for faster responses to increasing mortalities. Based on the results of this thesis project, further
insights into the early development of pikeperches were obtained. This will facilitate the design
and adaptation of raising and husbandry protocols, which can help to further establish
pikeperch as an aquaculture species and support its application in modern recirculatory
systems.
The goal of this thesis was to study the systematic relationships within the superfamily Sylvioidea (Aves: Passeriformes) in general and within the closely related families Acrocephalidae and Locustellidae in particular, by means of DNA sequences. Sylvioidea itself and families therein were the focus of many studies based as well on morphological characters as on DNA. Due to their morphological similarity and their presumably rapid radiation most studies failed to solve relationships between sylvioidean families and also demarcations of single families and relations within are still in progress. In this study, an enlargement of previous datasets, both taxa and number of DNA sequences, and more sophisticated analysis methods were used to improve the resolution in Sylvioidea, Acrocephalidae and Locustellidae. In addition, the applicability of barcoding in Acrocephalidae was tested. The monophyly of Sylvioidea could be supported and the families Paridae and Remizidae, which were sometimes still included, clustered among the outgroup taxa. Four families, Nicatoridae, Panuridae, Alaudidae, and Macrosphenidae constitute basal splits within Sylvioidea. The division of the former sylviid/timaliid clade in five families, Sylviidae, Leiothrichidae, Pellorneidae, Timaliidae, and Zosteropidae was supported. Scotocerca, Erythrocercus, and Hylia, previously supposed to be members of Cettiidae, were shown not to belong to this family. As the three genera are also morphologically and ecologically different, they were here proposed to be elevated to family rank, Scotocercidae, Erythrocercidae and Hyliidae, respectively. The family Acrocephalidae consisted of the four genera, Nesillas, Acrocephalus, Hippolais, and Chloropeta. In the analysis for this thesis, the latter three appeared to be non-monophyletic. One Acrocephalus species, A. aedon was sister to a clade containing four species of Hippolais as well as two out of three Chloropeta species. They were all merged in the genus Iduna, based on the DNA evidence and shared morphological and ecological characters. Iduna had priority over Hippolais or Chloropeta according to the International Code of Zoological Nomenclature. The one remaining Chloropeta species (C. gracilirostris) had to be renamed to Calamonastides as Chloropeta was no longer available for this taxon. Seven genera were included in the re-analysis of the family Locustellidae: Locustella, Bradypterus, Megalurus, Dromaeocercus, Schoenicola, Cincloramphus, and Eremiornis. Apart from the monotypic genera Dromaeocercus and Eremiornis and Schoenicola, of which only one species was included, the remaining genera were found to be non-monophyletic. One clade contained all Locustella species, Megalurus pryeri and all Asian/Oriental Bradypterus species. All species in this clade were synonymized with Locustella, as the type species of Locustella was included, whereas the type species of Bradypterus fell in a different clade. Therefore, the remaining African Bradypterus species retained their genus name, and Dromaeocercus was renamed to Bradypterus as it clustered within Bradypterus. Cincloramphus, intermingling with the remaining Megalurus species, was synonymized with the latter. Barcoding, growing in popularity for delimiting species, was tested in its applicability for Acrocephalidae. Fourteen taxa currently recognized as full species would fall under the 2% threshold of sequence divergence proposed for delimiting species using the mitochondrial cytochrome b gene. It was also shown that it is important to clarify which part of a DNA sequence is used, as different parts can give different results regarding the 2% threshold. In addition, the choice of “complete deletion” or “pairwise deletion” in calculating genetic distances is important, if incomplete are sequences used.
Global climate change is omnipresent all over the world and is affecting and challenging organisms in various ways. Species either have to adapt to the changing environmental conditions or move to new habitats in order to avoid extinction.
Possible ways for an organism to react can be dispersal, phenotypic plasticity, genetic adaptation or a combination of these factors. Among the various consequences of climate change, especially changes in temperature affect plenty of species. In ectotherms, the body temperature and associated mechanisms are strongly dependent on environmental conditions.
The aim of this work was to investigate the mechanisms underlying adaptation to thermal variation and heat stress in the widespread butterfly species <i>Pieris napi<i>.
Focusing on indicators of individual condition, including morphology, physiology and life history traits, the purpose was to specify whether the species’ responses to temperature variation have a plastic or genetic basis. In the first experiment, phenotypic variation along a latitudinal and altitudinal cline was investigated. Yellow reflectance of wings was negatively correlated with wing melanisation, providing evidence for a trade-off between a sexually selected trait (yellow color) and thermoregulation (black color). Body size decreased with increasing latitude and led to the assumption that warmer conditions are more beneficial for <i>P. napi<i> than cooler ones. An increased flight performance at higher altitudes but not latitudes may
indicate stronger challenges for flight activity in high-altitude environments.
The second experiment focused on clinal variation and plasticity in morphology, physiology and life history in F1-generation individuals reared in captivity at different temperatures. It could be shown that individuals from cooler environments were less heat-tolerant, had a longer development but were nevertheless smaller, and had more melanised wings. These differences were genetically-based. Furthermore, it could be shown that a higher developmental temperature speeded up development, reduced body size, potential metabolic activity, and wing melanisation but increased heat tolerance, documenting plastic responses.
In a third experiment, we examined physiological responses to heat stress. A transcriptome analysis revealed an upregulation in molecular chaperones under hot conditions, whereas antioxidant responses and oxidative damage remained unaffected. The antioxidant glutathione (GSH) though was reduced under both cold and hot conditions. Interestingly, Swedish individuals were characterized by higher levels of GSH, lower early fecundity, and lower larval growth rates compared with German or Italian populations, suggesting a ‘pace-of-life’ syndrome. Thus, the individuals from warmer regions show the opposite pattern with a lower investment into maintenance but a faster lifestyle.
In summary, we found clinal variation in body size, growth rates and concomitant development time, wing aspect ratio, wing melanisation and heat tolerance. The effects of high developmental temperature very likely reflect adaptive phenotypic plasticity. When speeding up development; heat tolerance is increasing while body size, potential metabolic activity and wing melanisation are decreasing. Overall, body size of <i>P. napi<i> individuals decreased from south to north while the melanisation of the wings increased. Furthermore, we found a connection between increased wing melanisation and decreased yellow reflectance, most likely caused by a trade-off between the two. We could confirm that <i>P. napi<i> individuals from warmer environments were more heat-tolerant and larger than individuals from colder environments. Due to increasing temperatures and heat waves becoming more frequent in the future, being able to cope with such conditions will be advantageous. As warmer conditions had positive effects on individual development, <i>P. napi<i> may benefit from global warming, but its association with moist habitats suggests negative consequences of climate change. We could also reveal pronounced plastic and genetic responses in <i>P. napi<i>, which may indicate high adaptive capacities. Thus, increasing temperature may not be too problematic for the species, as it seems to be rather well equipped to deal with such challenges. However, as climate change entails changes in precipitation / humidity along with temperature changes, such issues need further investigation.
Deflected by the barrier function of topographical structures such as high mountain ranges, open water bodies or desert, migrating birds concentrate at certain points or corridors referred to as ‘bottlenecks’. An area like this was discovered at Mount Besh Barmag (Azerbaijan) in autumn 2007, but the data gathered during a four-week survey was insufficient to do more than hint at the existence of a major bird migration bottleneck. Therefore, a comprehensive bird migration study was conducted to analyse the magnitude of this potential bottleneck site. The study covers the periods from August to mid-November 2011 and from March to the end of May 2012 and includes daily counts at three observation points focusing on three different migrant types: passerine, waterbirds and soaring birds. In addition, a sound recorder with an omnidirectional microphone collected bird migration calls by both day and night. In total, 278 bird species were observed in an estimated passage of 1,239,369–1,514,267 diurnally migrating individuals in autumn 2011 and 646,733–817,183 individuals in spring 2012. Fifteen species passed through the study area in numbers exceeding 1% of their world populations and 34 species in more than 1% of their flyway populations in at least one of the observation periods. 84% of the observed migrating birds in autumn 2011 and 95% of them in spring 2012 passed through at heights below 50 m above ground exposing them imminently to the danger of collision with obstacles. In the analysis of nocturnal sound recordings, 119 bird species were identified of which 106 were expected to occur as migrants, and calculated estimates revealed the occurrence of 108,986 calls in autumn 2011 and 33,348 calls in spring 2012. The volume of diurnal bird migration emerging from the data with respect to species number and number of individuals is certainly a strong indication of the existence of a major bird migration bottleneck at Besh Barmag. On account of methodological constraints, the high number of night flight calls can only hint at a nocturnal bird migration bottleneck and confirmatory research aided by visual methods (radar, thermal imaging) is necessary to back up the acoustic results. The Besh Barmag bottleneck offers a great opportunity to establish a standardised long-term monitoring programme to investigate avian population dynamics in the vast and little known Eurasian landmass. Acoustic-based monitoring might be a cost-effective method, but it is limited to a few vocally prolific species only. The aim should rather be the establishment of a bird observatory as already successfully installed in a number of European bird migration bottlenecks.
Bats spend half of their life at roosting sites. Hence, exploring for potential roosts is an essential task for their survival, especially for those species which switch roosts regularly, such as several temperate bat species. However, localizing new roosts is a difficult task due to bats’ sensory limitations (e.g., vision, echolocation range). To compensate such constrains, it has been hypothesized that bats rely on cognitive processes like associative learning, spatial memory, social information use and memory retention for an efficient roost localization. However, no previous study has assessed these cognitive skills under natural conditions.
The aim of my thesis was to assess how individually RFID-marked, free-ranging bats use different cognitive processes when localizing suitable day roosts. For this purpose, I used a pairwise roost-quality (suitable vs. unsuitable) choice experiment with automatic monitoring and assessed bats’ cognitive processes according to different cues available. Cues were echo-reflective (spectral signature of boxes), spatial (position of the box within the experimental pair) and social (presence of conspecific at roosts), each one linked to a different cognitive process.
I found that Bechstein’s bats (Myotis bechsteinii) used associative learning to discriminate between suitable and unsuitable newly placed boxes according to their echo-reflective cues. However, when individuals returned to known suitable roosts, they relied more on spatial memory to localize them. This was evidenced by the higher proportion of visits to the unsuitable boxes after swapping box positions within the same experimental pairs. When social cues were available, bats discovered a higher number of suitable roosts and re-localized previously occupied roosts more accurately. Taken together, Bechstein’s bats used multiple cognitive processes and prioritized one process over another depending on the relevance of the cues and search context.
Memory retention of the learned association was analyzed one year later, after the bats had returned to their breeding sites from their hibernacula. I found no evidence that individuals remembered the association between roosts’ suitability and their respective echo-reflective cue. The lack of memory retention could be attributed to hibernation or the duration of the period that the bats spent away from their summer habitat without the opportunity to reinforce the association contingencies. Nevertheless, bats quickly relearned the same association in a short period of time. This emphasizes the high behavioral flexibility of the bats.
Given the ability of Bechstein’s bats to quickly learn to discriminate roosts based on their external echo-reflective cue via associative learning, I investigated whether the use of echo-reflective cues improves box detectability and further occupancy. This was also assessed in free-ranging Natterer’s (Myotis nattereri) bats and the brown long-eared bats (Plecotus auritus). I found that the use of echo-reflective cues did not improve the detectability and occupancy of newly placed boxes despite the previous experience of the colonies with such cues. There were differences among species in the number of discovered boxes, visits and roosting days. These differences could be related to the species-specific explorative behavior and roost-switching behavior. Box supplementations programs aimed to conserve or relocate bat colonies should consider these behaviors to increase their likelihood of success even when bat colonies are used to roosting in artificial shelters.
My research underlined the importance of evaluating multiple cues under natural conditions to understand how natural selection has shaped the cognitive process used for localizing resources. Cognitive field studies are logistically challenging given the number of factors to control. However, automatic monitoring techniques like the one used in this study give the possibility to deepen the understanding of the cognitive ecology of animals. I finally discuss two venues of further research to understand the spread of information within colony members about novel roosts and the recruitment dynamic to novel roosts.