Bumblebees have shown both long and short-term declines throughout their range. These declines may be attributed to a range of factors including changes in land use, alterations in climatic conditions and species introductions. However, management strategies for bumblebee conservation often focus on provision of summer forage resources and other factors are frequently overlooked. Provision of spring forage and nesting sites for bumblebee queens are rarely considered, though colony foundation and early colony growth are two of the most sensitive stages in bumblebee life history. Here, the efficacy of certain agri-environment prescriptions for providing spring forage and nest sites for bumblebees is assessed, highlighting a need for specific schemes targeted towards the provision of these vital resources in the rural environment. The nesting ecology of bumblebees is poorly understood because wild colonies are difficult to locate. However, a greater knowledge of the colony-level effects of environmental change is crucial to understanding bumblebee declines. Attracting bumblebee queens to nest in artificial domiciles could provide a valuable tool for studying colony-level responses. However, domicile trials and the findings of a literature review presented here demonstrate that this approach may be largely impractical for use in the UK. Conversely, a nationwide public bumblebee nest survey produced numerous data regarding nest site preferences among bumblebee species and also demonstrated that citizen science may also provide a sensitive method for detecting declines in currently common bumblebee species. An understanding of the ecology of species interactions and coexistence can provide valuable insights into factors that may influence declines. Data presented here suggest that coexistence between some bumblebee species may be maintained by resource partitioning based on diel activity patterns that are linked to species-specific environmental tolerances. If this is the case, the potential role of climate change in bumblebee declines may be severely underestimated. There is also increasing evidence that genetic factors may play a role in bumblebee losses, accelerating declines of small, fragmented populations as a result of reduction in genetic diversity and inbreeding depression. Here, the feasibility of reintroducing British B. subterraneus (now extinct in the UK) from New Zealand into England is assessed using population genetic techniques. The findings suggest that the population history of B. subterraneus in New Zealand has resulted in a dramatic loss of genetic diversity and high genetic divergence from the original UK population, suggesting that it may not be a suitable for use in the reintroduction attempt. This work draws together some understudied aspects of bumblebee ecology with a particular focus on nest site requirements, availability of spring forage, mechanisms of avoidance of inter-specific competition and population genetic processes. The potential role of these in bumblebee declines is considered and new data relevant to the conservation of these important species is presented. It is hoped that this work will inform future management strategies for bumblebee conservation, highlight areas in need of further study and provide a sound starting point for future research in these areas.

The populations of many farmland birds have severely declined during the past years. Even (formerly) common species such as the Eurasian Skylark (Alauda arvensis) and the Northern Lapwing (Vanellus vanellus) are strongly affected. The declines were mainly caused by agricultural intensification. In response to the declines, agri-environmental schemes (AES) that integrate protection objectives into agricultural practices are a promising strategy. Until 1992 all EU member states were obliged to develop agri-environment programmes and since this time, AES are widely used. AES are often criticised for being ineffective and expensive. However, good results have been achieved with measures targeted on one bird species and used in projects advising farmers where and how to apply AES. Despite legitimate criticism, AES can help to slow down the declines of farmland bird populations, at least for a transitional period until sustainable agriculture has been established. This requires species-specific AES which are easy to implement and work well for the target species. In the German federal state of Saxony, such AES were developed and tested from 2009 to 2013 in a state-wide conservation project for ground-nesting farmland birds. Two of the studies with AES for the Skylark (study 1) and the Lapwing (study 2), which were part of scientific research, are presented here. For the Skylark, Skylark plots were tested at conventionally managed fields with winter cereals (n=10) or winter oilseed rape (n=10). Each field was divided in a test site with skylark plots and a control site without treatment. Skylark plots are unsown plots about 20 m² in size and applied in a density of about two plots per hectare. Further ten fields with winter cereals were in the same way equipped with additional tramlines that were not used for crop management. Both measures aimed to open the otherwise closed crop canopy to allow Skylarks to reach the ground and improve habitat conditions. Skylark territory mapping was carried out to reveal effects of the treatment. For the Lapwing, 61 lapwing plots were established within conventionally managed winter wheat and winter oilseed rape fields. These unsown fallow plots, mostly 1-2 ha in size, were created during autumn tillage and left bare until next summer. They were meant to provide a breeding site and a habitat for rearing the young. Lapwings and other bird species were mapped at the lapwing plots and nearby control sites. Factors influencing the success of the plots were modelled to obtain information on the design of a well-working AES. All three measures proved to be working well for the target species. At sites with skylark plots or additional tramlines, Skylark territory densities were about twice as high as at untreated control sites. The lapwing plots were also used about twice as likely as the untreated control sites. The hatching success was significantly higher, too. Particularly successful were large (>2 ha), sparsely vegetated lapwing plots at damp sites traditionally used for breeding. Other species also benefitted, especially from lapwing plots. The measures are therefore promising to provide positive effects on Skylark or Lapwing populations. They are relatively easy to implement and were repeatedly applied by the farmers involved in the project. Furthermore, synergy effects for other bird and plant species as well as for the biotope network can be expected by establishing lapwing plots at damp sites. The measures are suitable AES which, if widely adopted, have the potential to slow down, stabilise or even reverse the negative population trends. To promote these and to ensure their correct implementation, advise of farmers seems to be necessary, particularly for lapwing plots. / Bei vielen Agrarvögeln waren in den vergangenen Jahren starke Bestandsrückgänge zu verzeichnen, wobei mit Kiebitz (Vanellus vanellus) und Feldlerche (Alauda arvensis) zwei der ehemals häufigsten Arten am stärksten betroffen sind. Hauptursache hierfür ist die Intensivierung der Landwirtschaft. Eine mögliche Gegenstrategie sind nutzungsintegrierte Artenschutzmaßnahmen, mit denen versucht wird, die Belange des Artenschutzes eng in den landwirtschaftlichen Produktionsprozess einzubetten. Bedeutendstes Umsetzungsinstrument sind hierbei die EU-geförderten Agrarumweltmaßnahmen (AUM), die es seit 1992 in allen Mitgliedsstaaten gibt. Diese erwiesen sich in der Praxis jedoch oft als teuer und wenig erfolgreich. Vielversprechende Resultate wurden meist dann erzielt, wenn die Maßnahmen eng auf die Erfordernisse der Zielart(en) zugeschnitten waren und die Landwirte Beratung und Unterstützung bei der Umsetzung erhielten. Trotz aller Kritik an den AUM können diese zumindest für eine Übergangsphase auf dem Weg zu einer tatsächlich nachhaltigen Landwirtschaft helfen, die drastischen Bestandsrückgänge vieler Agrarvogelarten zu vermindern. Dazu werden aber zielartenspezifische und einfach umsetzbare Maßnahmen benötigt. Im sächsischen Bodenbrüterprojekt wurden von 2009 bis 2015 nutzungsintegrierte Artenschutzmaßnahmen entwickelt und erprobt. Zwei der projektbegleitenden wissenschaftlichen Studien zu AUM für Feldlerche (Studie 1) und Kiebitz (Studie 2) sind in der vorliegenden Arbeit zusammengefasst. Für die Feldlerche erfolgten Siedlungsdichteuntersuchungen auf konventionell bewirtschafteten Feldern mit Wintergetreide (n=10) oder Winterraps (n=10), die jeweils etwa zur Hälfte mit Feldlerchenfenstern bestellt waren, während der Restschlag als Vergleichsfläche diente. Zehn weitere Felder, ausschließlich in Wintergetreide, dienten in gleicher Weise der Erprobung der Anordnung zusätzlicher, für die Bewirtschaftung nicht benötigter Fahrgassen. Feldlerchenfenster sind ca. 20 m² große Saatlücken, die in einer Dichte von etwa zwei Fenstern je Hektar, ebenso wie die zusätzlichen Fahrgassen, die ansonsten dichten Kulturbestände öffnen und dadurch die Besiedlung durch die Zielart erleichtern. Für den Kiebitz wurden 61 Kiebitzinseln in konventionell bewirtschafteten Wintergetreide- und Winterrapsfeldern angelegt. Dies waren selbstbegrünte, meist 1-2 ha große Brachen, die bei der Herbstbestellung zwar bearbeitet, aber nicht gesät wurden. Im folgenden Frühjahr sollten die Flächen der Brut und Jungenaufzucht dienen. Die Untersuchungen beinhalteten Erfassungen der Zielart und weiterer Vogelarten auf den Kiebitzinseln und Vergleichsflächen sowie die statistische Modellierung verschiedener Faktoren für den Erfolg der Flächen. Im Ergebnis erwiesen sich alle drei Maßnahmen als erfolgreich. Auf Flächen mit Feldlerchenfenstern und zusätzlichen Fahrgassen war die Territoriendichte der Zielart etwa doppelt so hoch wie auf den Vergleichsflächen ohne Maßnahme. Die Kiebitzinseln wurden gleichfalls annähernd doppelt so oft von Kiebitzen besiedelt wie die Kontrollflächen. Der Schlupferfolg war signifikant höher. Besonders erfolgreich waren große (ca. >2 ha), spärlich bewachsene Kiebitzinseln an traditionell als Brutplatz genutzten Nassstellen. Insbesondere im Falle der Kiebitzinseln profitierten auch andere Arten. Die untersuchten Maßnahmen sind daher grundsätzlich geeignet, positive Effekte auf die Bestände von Feldlerche oder Kiebitz zu entfalten. Sie sind zudem vergleichsweise einfach umsetzbar und wurden von den am Projekt beteiligten Landwirten wiederholt realisiert. Mit der Anlage von Kiebitzinseln an Nassstellen lassen sich zudem Synergieeffekte für andere Tier- und Pflanzenarten sowie für den Biotopverbund erzielen. Die untersuchten Maßnahmen stellen damit geeignete AUM dar, die bei hinreichender Anwendung das Potenzial haben, die derzeit negativen Bestandstrends der Zielarten zu verlangsamen, zu stabilisieren oder sogar umzukehren. Zur Förderung der Umsetzung erscheint insbesondere im Fall der Kiebitzinseln eine fachliche Beratung der Landwirte unabdingbar.

Conservation in the EU and all over the world aims at reducing biodiversity loss which has become a great issue in the last decades. However, despite existing efforts, Earth is assumed to face a sixth mass extinction. One major challenge for conservation is to reconcile the targets with conflicting interests, e.g. for food production in intensively used agricultural landscapes. Agriculture is an example of a coupled human-environment system that is approached in this thesis with the help of mathematical models from two directions. Firstly, the ecological subsystem is considered to find processes relevant for the effect of habitat connectivity on population abundances. Modelling theory predicts that the species-specific growth parameters (intrinsic growth rate and carrying capacity) indicate whether dispersal has a positive or negative effect on the total population size at equilibrium (r-K relationship). We use laboratory experiments in combination with a system of ordinary differential equations and deliver the first empirical evidence for a negative effect of dispersal on the population size in line with this theory. The result is of particular relevance for the design of dispersal corridors or stepping stones which are meant to increase connectivity between habitats. These measures might not be effective for biological conservation. A second population model, consisting of two coupled Ricker maps with a mate-finding Allee effect, is analyzed in order to examine the effect of bistability due to the Allee effect in combination with overcompensation in a spatial system. The interplay can cause complex population dynamics including multiple coexisting attractors, long transients and sudden population collapses. Essential extinction teaches us that not only small populations are prone to extinction but chaotic dynamics can drive a population extinct in a short period of time as well. By a comprehensive model analysis, we find that dispersal can prevent essential extinction of a population. In the context of conservation that is: habitat connectivity can promote rescue effects to save a population that exhibits an Allee effect. The two findings of the first part of this thesis have contrasting implications for conservation which shows that universal recommendations regarding habitat connectivity are impossible without knowledge of the specific system. Secondly, a model for the socio-economic subsystem is presented. Agri-environment schemes (AES) are payments that compensate farmers for forgone profits on the condition that they improve the ecological state of the agricultural system. However, classical economic models that describe the cost-effectiveness of AES often do not take the social network of farmers into account. Numerical simulations of the socio-economic model presented in this thesis suggest that social norms can hinder farmers from scheme participation. Moreover, social norms lead to multistability in farmers’ land-use decision behaviour. Informational campaigns potentially decrease the threshold towards more long-term scheme participation and might be a good tool to complement compensation payments if social norms affect land-use decisions. Finally, a coupled human-environment system is analyzed. An integrated economicecological model is studied to investigate the cost-effectiveness of AES if the species of concern exhibits an Allee effect. A numerical model analysis indicates large trade-offs between agricultural production and persistence probability. Moreover, conservation success strongly depends on the initial population size, meaning that conservation is well advised to start before the species is threatened. Spatial aggregation of habitat can promote rescue effects, suggesting land-sparing solutions for conservation. In that case,agglomeration bonuses may serve to increase the effectiveness of AES. Possible causes for population declines are diverse and can be a combination of human influences, e.g. due to habitat degradation and inherent ecosystem properties. That complicates the task of conservation. The models presented in this thesis simplify complex systems in order to extract processes relevant for biological conservation. The analysis of spatial effects and dynamical model complexity, e.g. due to Allee effects or a nonlinear utility function, allows us improve the understanding of coupled human-environment systems.

No description available.