Chapter I The gradual turnover of dead organic material into mineral nutrients is a key ecological function, linking decomposition and primary production, the essential parts of the nutrient-energy cycle. However, disturbances in terms of species or resource losses might impair the equilibrium between production and decomposition. Humanity has converted large proportions of natural landscapes and intensified land-use activity for food production. Globally, only very few areas are totally unaffected by human activity today. To ensure the maintenance of both essential ecosystem services, knowledge about the interplay of biodiversity and ecosystem functioning as well as effects of intensified management on both is crucial. The vast majority of terrestrial biomass production as well as decomposition take place in forest ecosystems. Though forestry has a long sustainable history in Europe, its intensification during the last century has caused severe impacts on forest features and, consequently, on the associated biota, especially deadwood dependent organisms. Among these, saproxylic beetles are the most diverse group in terms of species numbers and functional diversity, but also most endangered due to habitat loss. These features classify them as ideal research organisms to study effects of intensified forestry on ecosystem services. The BELONGDEAD project located in Germany aimed to investigate deadwood decay and functional consequences of diversity changes in the associated fauna on the decomposition process from the initialisation of deadwood decay to complete degradation. As part of the BeLongDead project, this dissertation focussed on saproxylic beetle species, thereby evaluating (1) regionally effects of tree species identity of fresh deadwood and (2) forest management of varying intensities on the diversity, abundance and community composition of saproxylic beetles (chapter II); (3) the specialisation degree of different trophic guilds of saproxylic beetles, and thus the stability and robustness of their interaction networks against disturbances (chapter III); (4) the impact of environmental features of local to regional spatial scales on species richness of saproxylic beetles differing in their habitat niche in terms of deadwood decay stages (chapter IV). Chapter II The vast majority of European forest ecosystems have been anthropogenically affected, leaving less than 1% of the about 1 milliard hectare as natural forests. A long history of forestry and especially the technological progress during the last century have caused massive habitat fragmentation as well as substantial loss of essential resources in European forest ecosystems. Due to this, the substrate-dependent group of saproxylic beetles has experienced severe species losses. Thus, investigations concerning saproxylic diversity and deadwood volume were badly needed. However, the importance of different deadwood in terms of tree species identity for the colonization by saproxylic beetles under different local and regional management regimes is poorly understood. Therefore, we studied possible regional differences in colonization patterns of saproxylic beetle species in a total of 688 fresh deadwood logs of 13 tree species in 9 sites of managed conifer and beech forests, and unmanaged beech forests, respectively. We found that tree species identity was an important driver in determining saproxylic species composition and abundance within fresh deadwood. However, saproxylic species showed different colonization patterns of deadwood items of the same tree species among the study regions. Regionally consistent, conifer forests were most diverse. We attribute the latter result to the historically adaption of saproxylic beetle species to semi-open forests, which conditions are actually best reflected by conifer forests. To preserve a diverse local species pool of early successional saproxylic beetles, we suggest an equal high degree of deadwood diversity in a tree species context in due consideration of regional differences. Chapter III The extinction risk of a particular species corresponds with its species-specific requirements on resources and habitat conditions, in other words with the width of the species` ecological niche. Species with a narrow ecological niche are defined as specialists. Members of this group experience higher extinction risk by resource limitation than generalists, which are able to utilize a variety of resources. For the classification of species as specialists or generalists, thus evaluating possible extinction risks, ecologists use the concept of interaction networks. This method has often been applied for mutualistic or antagonistic plant-animal interactions, but information for networks of detritivores is scarce. Therefore, saproxylic beetle species sampled as described in chapter II were categorised according to their larval diet; additionally their interaction networks (N=108) with 13 dead host tree species were analysed. Specialisation degree was highest for wood-digesting beetles and decreased with increasing trophic level. Also the network indices evaluating robustness and generality indicated a higher susceptibility to species extinctions for xylophagous than for mycetophagous and predatory beetles. The specialisation of xylophagous species on specific tree species might be an adaption to tree species specific ingredients stored for defence against pathogens and pests. However, we conclude that the high specialisation degree of xylophages and thus their higher extinction risk by resource loss harbours certain dangers for ecosystem function and stability as species diversity is positively linked to both. Chapter IV Populations depend on individual emigration and immigration events to ensure genetic exchange. For successful migration it is of utmost importance that spatially separated populations are obtainable by specimen. Migratory success depends on the one hand on the species dispersal abilities and on the other on the availability of suitable habitats in the surrounding landscape in which the distinct host populations exist. However, consequences of intensive forest management correspond not only to severe reduction of local deadwood amount, but, among others, also a change in tree species composition and high levels of fragmentation in the surrounding forest area. Saproxylic beetle species differ in their dispersal behaviour according to the temporal availability of their preferred habitat. Generally, early successional saproxylic beetles are able to disperse over large distances, whereas beetles inhabiting advanced decayed wood often remain close to their larval habitat. Due to this, environmental factors might affect saproxylic beetle guilds differently. We classified the saproxylic beetles sampled as described in chapter II according to their calculated habitat niche as early, intermediate or late successional saproxylic beetles. For the different guilds the effects of 14 environmental factors on different spatial scales (stand factors at 0.1 km radius, landscape composition at 2 km radius, and regionally differing abiotic factors in 400 km to 700 km distance) were investigated. Consistently for all guilds, species richness decreased with fragmentation at local and landscape scale, and increased in warmer climate. However, we found contradictory results between the guilds to some extent. We relate this to guild specific habitat requirements of the saproxylic beetles. Therefore, for the development of appropriate conservation practices guild-specific requirements saproxylic beetles have to be considered not only locally but on larger spatial scales. Chapter V In conclusion, this dissertation identified main drivers of early successional saproxylic beetle species richness on various spatial scales. Our results emphasize the importance to develop management schemes meeting species-specific and guild-specific habitat requirements of the saproxylic beetle fauna at relevant spatial and temporal scales. Therefore, short-term actions suggested for sustainable forest management should be the focus on a diverse tree species composition consisting of indigenous tree species with respect to regional differences. Moreover, senescent trees, fallen and standing deadwood should remain in the forests, and some tree individuals should be allowed to grow old. Long-term actions should involve the reduction of forest fragmentation and the connection of spatial widely separated forest fragments. Furthermore, to fully understand the effects of forest management long-term research should be conducted to compare habitat requirements of intermediate and late successional beetles with the results presented in this dissertation.

1) Modern European agricultural landscapes form a patchy mosaic of highly fragmented natural and semi-natural habitat remnants embedded in a matrix of intensively managed agricultural land. In those landscapes many organism frequently cross habitat borders including the crop – non-crop boundary, hereby connecting the biotic interactions of multiple habitat types. Therefore biodiversity and ecosystem functions within habitats are expected to depend on adjacent habitat types and the surrounding landscape matrix. In this thesis the biodiversity of non-crop habitats, and ecosystem services and disservices in crop habitats were studied in the human-dominated agricultural landscape in the district Lower Franconia, Bavaria, Germany. First we examined the effect of adjacent habitat type on species composition, diversity and ecosystem functions in semi-natural calcareous grasslands, a biodiversity-rich habitat of high conservation value (chapter 2 and 3). Second we studied the effect of habitat composition in the landscape on herbivory, biological pest control and yield in oilseed rape fields (chapter 4). 2) We examined the effect of adjacent habitat type on the diversity of carabid beetles in 20 calcareous grasslands using pitfall traps. Half of the grasslands were adjacent to a coniferous forest and half to a cereal crop field. We found different species compositions of carabid beetles depending on adjacent habitat type. In addition calcareous grasslands adjacent to crop fields harboured a higher species richness and activity density but a lower evenness of carabid beetles than calcareous grasslands adjacent to forests. These differences can be explained by the spillover of carabid beetles from the adjacent habitats. After crop harvest carabid beetle activity density in crop fields decreased while in parallel the activity density in the calcareous grasslands adjacent to the crop fields increased, indicating an unidirectional carabid beetle spillover. Our results underline that type and management of adjacent habitats affect community composition and diversity in calcareous grasslands. Therefore nature conservation measures, which focused on the improvement of local habitat quality so far, additionally need to consider adjacent habitat type. 3) In addition to carabid beetle communities we also surveyed predation rates of ground-dwelling predators on the same calcareous grasslands in two study periods (June and late August). As ground-dwelling predators of forests or crop fields can move into adjacent calcareous grasslands we expected different predation rates depending on adjacent habitat type. We exposed in total 32.000 lady bird eggs as prey items on the calcareous grasslands in distances of 5 and 20m from the habitat border. We found higher predation rates on calcareous grasslands adjacent to forests than on calcareous grasslands adjacent to crop fields, but only on cool days. On warm days a very high extent (often 100%) of the exposed prey items were consumed adjacent to both habitat types, which did not allow the detection of possible differences between the adjacent habitat types. Predation rates differed not between the two study periods or the two distances to the habitat edge. The higher predation rates adjacent to forests can be explained by the spillover of ground-dwelling predators from forests into calcareous grasslands. Our results show, that spillover into semi-natural habitats affects ecosystem functioning in addition to species composition and diversity. 4) In chapter 4 of this thesis we examined the effect of spatiotemporal changes in crop cover on pest - natural enemy interactions and crop yields. During two study years we surveyed the abundance of adult and larval pollen beetles, parasitism of pollen beetle larvae by a hymenopteran parasitoid and oilseed rape yields of 36 oilseed rape fields. The surrounding landscape of the fields (1 km radius) differed in the oilseed rape proportion and in the inter-annual change in the oilseed rape proportion since the previous year. We found a dilution effect, i.e. a decreasing abundance with increasing oilseed rape proportions, for pollen beetle larvae and parasitoids in both study years and for adult pollen beetles in one study year. Oilseed rape yields increased with increasing oilseed rape proportions. Inter-annual changes in oilseed rape proportions led to inter-annual crowding and dilution effects for pollen beetles, but had no effect on parasitism or yield. Our results indicate the potential to reduce pest loads and increase yields in intensively managed oilseed rape fields by a coordinated management of the spatiotemporal oilseed rape cover in the landscape. 5) In summary, we showed in this thesis that the biodiversity and functioning of crop and non-crop habitats within agricultural landscapes is affected by the spillover of organisms and thus by the habitat composition in the close surrounding and in the broader landscape context. Spillover affects also ecosystem services and disservices and therefore crop productivity. Thereby the spatial and temporal variation of specific crop types in the landscape can be of particular importance for crop yields. Thus a coordinated landscape wide management can help to optimize both biodiversity conservation and the delivery of ecosystem services and thus crop yields. Future studies integrating landscape effects across several ecosystem functions, multiple taxonomic groups and different crop types are necessary to develop definite landscape management schemes.

1. Since the early nineteenth century describing (and understanding) patterns of distribution of biodiversity across the Earth has represented one of the most significant intellectual challenges to ecologists and biogeographers. Among the most striking patterns of species richness are: the latitudinal and elevational gradients, with peaks in number of species at low latitudes and somewhere at mid altitudes, although other patterns, e.g. declines with increasing elevation, are often observed. Even in highly diverse tropical regions, species richness is not evenly distributed but there are “hotspots” of biodiversity where an exceptional number of species, especially endemics, are concentrated. Unfortunately, such areas are also experiencing dramatic loss of habitat. Among vertebrate taxa, amphibians are facing the most alarming number of extinctions. Habitat destruction, pollution and emergence of infectious diseases such as chytridiomycosis, are causing worldwide population declines. Responses to these drivers can be multidirectional and subtle, i.e. they may not be captured at the species but at the genetic level. Moreover, present patterns of diversity can result from the influence of past geological, climatic and environmental changes. In this study, I used a multidisciplinary and multilevel approach to understand how and to which extent the landscape influences amphibian diversity. Mount Kilimanjaro is an exceptional tropical region where the landscape is rapidly evolving due to land use changes; additionally, there is a broad lack of knowledge of its amphibian fauna. During two rainy seasons in 2011, I recorded anurans from the foothills to 3500 m altitude; in addition, I focused on two river frog species and collected tissue samples for genetic analysis and swabs for detection of chytridiomycosis, the deadly disease caused by Batrachochytrium dendrobatidis (Bd). 2. I analyzed how species richness and composition change with increasing elevation and anthropogenic disturbance. In order to disentangle the observed patterns of species diversity and distribution, I incorporated inferences from historical biogeography and compared the assemblage of Mt. Kilimanjaro and Mt. Meru (both recent volcanoes) with those of the older Eastern Arc Mountains. Species richness decreased with elevation and locally increased in presence of water bodies, but I did not detect effects of either anthropogenic disturbance or vegetation structure on species richness and composition. Moreover, I found a surprisingly low number of forest species. Historical events seem to underlie the current pattern of species distribution; the young age of Mt. Kilimanjaro and the complex biogeographic processes which occurred in East Africa during the last 20 million years prevented montane forest frogs from colonizing the volcano. 3. I focused on the genetic level of biodiversity and investigated how the landscape, i.e. elevation, topographic relief and land cover, influence genetic variation, population structure and gene flow of two ecologically similar and closely related river frog species, namely Amietia angolensis and Amietia wittei. I detected greater genetic differentiation among populations in the highland species (A. wittei) and higher genetic variation in the lowland species (A. angolensis), although genetic diversity was not significantly correlated with elevation. Importantly, human settlements seemed to restrict gene flow in A. angolensis, whereas steep slopes were positively correlated with gene flow in A. wittei. This results show that even ecologically similar species can respond differently to landscape processes and that the spatial configuration of topographic features combined with species-specific biological attributes can affect dispersal and gene flow in disparate ways. 4. River frogs of the genus Amietia seem to be particularly susceptible to chytridiomycosis, showing the highest pathogen load in Kenya and other African countries. In the last study, I collected swab samples from larvae of A. angolensis and A. wittei for Bd detection. Both species resulted Bd-positive. The presence of Bd on Mt. Kilimanjaro has serious implication. For instance, Bd can be transported by footwear of hikers from contaminated water and soil. Tourists visiting Mt. Kilimanjaro may translocate Bd zoospores to other areas such as the nearby Eastern Arc Mts. where endemic and vulnerable species may still be naïve to the fungus and thus suffer of population declines. 5. My study significantly contributed to the knowledge of the amphibian fauna of Mt. Kilimanjaro and of East Africa in general, and it represents a valuable tool for future conservation actions and measures. Finally, it highlights the importance of using a multidisciplinary (i.e. community ecology, historical biogeography, landscape genetics, disease ecology) and multilevel (i.e. community, species, population, gene) approach to disentangle patterns of biodiversity.

1. Today honey bee colonies face a wide range of challenges in modern agricultural landscapes which entails the need for a comprehensive investigation of honey bees in a landscape context and the assessment of environmental risks. Within this dissertation the pollen foraging of honey bee colonies is studied in different agricultural landscapes to gain insight into the use of pollen resources and the influence of landscape structure across the season. General suggestions for landscape management to support honey bees and other pollinators are derived. 2. Decoding of waggle dances and a subsequent spatial foraging analysis are used as methods in Chapters 4 and 5 to study honey bee colonies in agricultural landscapes. The recently developed metabarcoding of mixed pollen samples was applied for the first time in honey bee foraging ecology and allowed for a detailed analysis of pollen, that was trapped from honey bees in front hive entrances (Chapter 6). 3. Pollen identification through molecular sequencing and DNA barcoding has been proposed as an alternative approach to light microscopy, which still is a tedious and error-prone task. In this study we assessed mixed pollen probes through next-generation sequencing and developed a bioinformatic workflow to analyse these high-throughput data with a newly created reference database. To evaluate the feasibility, we compared results from classical identification based on light microscopy from the same samples with our sequencing results. Abundance estimations from sequencing data were significantly correlated with counted abundances through light microscopy. Next-generation sequencing thus presents a useful and efficient workflow to identify pollen at the genus and species level without requiring specialized palynological expert knowledge. 4. During maize flowering, four observation hives were placed in and rotated between 11 landscapes covering a gradient in maize acreage. A higher foraging frequency on maize fields compared to other landuse types showed that maize is an intensively used pollen resource for honey bee colonies. Mean foraging distances were significantly shorter for maize pollen than for other pollen origins, indicating that effort is put into collecting a diverse pollen diet. The percentage of maize pollen foragers did not increase with maize acreage in the landscape and was not reduced by grassland area as an alternative pollen resource. Our findings allow estimating the distance-related exposure risk of honey bee colonies to pollen from surrounding maize fields treated with systemic insecticides. 5. It is unknown how an increasing area of mass-flowering crops like oilseed rape (OSR) or a decrease of semi-natural habitats (SNH) change the temporal and spatial availability of pollen resources for honey bee colonies, and thus foraging distances and frequency in different habitat types. Sixteen observation hives were placed in and rotated between 16 agricultural landscapes with independent gradients of OSR and SNH area within 2 km to analyze foraging distances and frequencies. SNH and OSR reduced foraging distance at different spatial scales and depending on season, with possible benefits for the performance of honey bee colonies. Frequency of pollen foragers per habitat type was equally high for SNH, grassland and OSR fields, but lower for other crops and forest. In landscapes with a small proportion of SNH a significantly higher density of pollen foragers on SNH was observed, indicating the limitation of pollen resources in simple agricultural landscapes and the importance of SNH. 6. Quantity and diversity of collected pollen can influence the growth and health of honey bee colonies, but little is known about the influence of landscape structure on pollen diet. In a field experiment we rotated 16 honey bee colonies across 16 agricultural landscapes (see also Chapter 5), used traps to get samples of collected pollen and observed the intra-colonial dance communication to gain information about foraging distances. Neither the amount of collected pollen nor pollen diversity were related to landscape diversity. The revealed increase of foraging distances with decreasing landscape diversity suggests that honey bees compensate for a lower landscape diversity by increasing their pollen foraging range in order to maintain pollen amount and diversity. 7. Our results show the importance of diverse pollen resources for honey bee colonies in agricultural landscapes. Beside the risk of exposure to pesticides honey bees face the risk of nutritional deficiency with implications for their health. By modifying landscape composition and therefore availability of resources we are able to contribute to the wellbeing of honey bees. Agri-environmental schemes aiming to support pollinators should focus on possible spatial and temporal gaps in pollen availability and diversity in agricultural landscapes.

I. Nowadays, tropical landscapes experience large-scale land use intensification and land conversion driven by increasing demand for resourses. Due to the continuously high demand for tropical timber and politically intended step increase in palm oil production, multiple rounds of logging and subsequent conversion to oil palm plantations became a regionally wide-spread land conversion pattern in Southeast Asia. Although many tree species and some animals are highly threatened by logging, a great number of species groups, such as birds or mammals, have been shown to persist in logged forests. Accordingly, many ecosystem services, such as dung removal, seed dispersal or the activity of scavengers, are functionally maintained in logged forests. In contrast, oil palm plantations have been shown to not only dramatically alter the species composition and reduce biodiversity, but also curtail many crucial biotic and abiotic ecosystem functions. The focus of this dissertation was to investigate the response of anuran species richness and community composition to logging and conversion to oil palm plantation in northern Borneo (chapter II). I analysed the diet of various frog species and their change with habitat degradation. Furthermore, I assessed the shift in the trophic position of the anuran community as well as the response of anuran phylogenetic, dietary, and functional diversity to logging and conversion to oil palm plantations (chapter III). Finally, the resilience of the predator-prey interaction between an ant-specialist toad and its ant prey was analysed using shifts in species-level interactions (chapter IV). II. This part of the study compares the species richness, relative abundance and community composition of stream anuran assemblages among primary forests, repeatedly logged forests and oil palm plantations. I used a highly standardised sampling setup applying transect-based sampling. Surprisingly, most of the anuran species native to primary forests were able to survive in logged forest streams. In contrast, on average only one third of the forest species richness was found in oil palm plantation streams. However, a high percentage of canopy cover above the plantation streams was able to mitigate this loss substantially. This study demonstrates the high conservation value of logged forests for Southeast Asian anurans. In contrast, the conversion to oil palm plantations leads to a dramatic decline of forest species. However, they have a mainly unused potential to contribute to the protection of parts of the regional anuran biodiversity if conservation-oriented management options are implemented. III. In this part, I analysed the shifts in trophic position and multiple diversity layers of Southeast Asian stream-dependent anuran species across a gradient of disturbance from primary forest through intensively logged forest to oil palm plantation. For this purpose, I identified the diet composition of 59 anuran species by means of stomach flushing. Furthermore, I use diet composition of frog species as well as species traits to calculate dietary and functional diversity, respectively. I found that the trophic position of the entire anuran community is elevated in heavily disturbed habitats. Furthermore, species diversity, phylogenetic species variation, dietary diversity, and functional diversity were reduced. However, beyond the effect of the decreased species richness, only phylogenetic species variability and functional diversity were significantly impacted by land conversion, indicating a non-random loss of phylogenetic groups and functionally unique species. Overall, the observed changes to species interactions and functional composition suggest a greatly modified role of anurans in altered habitats and major foodweb reorganisation. Such far-reaching changes to the way species groups interact are likely to threaten local biodiversity and ecosystem functioning in natural and particularly modified habitats. However, I could also show, that small-scale habitat quality, provided by riparian reserves, is able to mitigate the negative consequences of land conversion considerably. IV. Here I assess how logging of rain forest and conversion to oil palm plantations affect the populations of the ant-specialist giant river toad (Phrynoidis juxtaspera), and availability and composition of its ant prey. I measured canopy cover as an estimate for the degree of disturbance. I found that toad abundance decreased with increasing disturbance. At the same time, ant community composition was altered, and local ground-foraging ant species richness increased with disturbance. However, for a given amount of canopy cover, primary forest supported more ant species than altered habitats. Despite these changes, composition of ants consumed by toads was only weakly affected by habitat change, with the exception of the invasive yellow crazy ant (Anoplolepis gracilipes), which was positively selected in oil palm plantations. This suggests that predator-prey interactions can be mostly maintained with habitat disturbance despite shifts in community composition, and even that some predators are capable of exploiting new prey sources in novel ecosystems. V. I could show that anuran diversity and their trophic interaction is negatively impacted by logging and in particular by conversion to oil palm plantations. From species richness and community composition, my study expanded to phylogenetic, dietary and functional diversity. Furthermore, I investigated the interaction of a particular toad species with its preferred prey (ants), on species level. This increasing degree of detail in my study provided comprehensive results, beyond the detail of many related studies. Overall, conservation of the remaining forest in Southeast Asia is urgently required to protect anuran biodiversity and their trophic interactions.