Refine
Has Fulltext
- yes (15)
Is part of the Bibliography
- yes (15)
Year of publication
Document Type
- Doctoral Thesis (11)
- Journal article (2)
- Complete part of issue (1)
- Working Paper (1)
Keywords
- Ökologie (15) (remove)
Institute
- Theodor-Boveri-Institut für Biowissenschaften (9)
- Graduate School of Life Sciences (2)
- Center for Computational and Theoretical Biology (1)
- Institut für Anatomie und Zellbiologie (1)
- Institut für Molekulare Infektionsbiologie (1)
- Institut für Politikwissenschaft und Soziologie (1)
- Julius-von-Sachs-Institut für Biowissenschaften (1)
- Universität Würzburg (1)
Sonstige beteiligte Institutionen
Inhaltsübersicht zum Schwerpunktthema: - Stress und Stressanpassung bei Pflanzen und Tieren - Biologisch aktive Naturstoffe aus tropischen Lianen - Blattschneiderameisen: Dominante Herbivoren in neotropischen Regenwäldern - Photosynthese von Gesteinsflechten unter extremen Bedingungen - Chemische Kriegsführung bei Flechten und Schwammen - Wie sich Pflanzen vor Austrocknung schlitzen - Großer Lauschangriff auf die Photosynthese der Pflanzen u.a.
Legionella pneumophila, der Erreger der Legionärskrankheit, ist ein Umweltkeim mit Verbreitung in aquatischen Habitaten. Die Keime sind in der Lage, sich intrazellulär in eukaryontischen Zellen, wie Makrophagen, Monozyten und Protozoen zu vermehren. Die erfolgreiche Besiedlung ökologischer Nischen, aber auch das Virulenzpotential des Keimes können dabei von Umweltfaktoren abhängen. Die Erforschung ökologischer Zusammenhänge kann daher für das Verständnis der bakteriellen Virulenz von großer Bedeutung sein. Ausgangspunkt dieser Arbeit ist die in der späten stationären Phase des Bakterienwachstums von L. pneumophila zu beobachtende intensive Pigmentierung des Kulturmediums. Für diesen Phänotyp ist das Legiolysin (Lly) verantwortlich. Es ist eines der wenigen bekannten Genprodukte von L. pneumophila, die einen Einfluß auf das Überleben des Keimes in der Umwelt haben. Legiolysin kann daher als Fitnessfaktor bezeichnet werden. Um die ökologischen Zusammenhänge der Pigmentgenerierung näher zu untersuchen, wurde das lly-positive Plasmid pEWL 1 subkloniert und sequenziert. Neben lly konnten in diesem Genabschnitt durch Sequenzvergleiche der abgeleiteten Aminosäuresequenzen sechs weitere Leseraster detektiert werden. Die drei unmittelbar benachbarten Gene von lly kodieren dabei für Proteine mit Funktionalität in Bezug zur lly-Determinante, während die drei upstream von lly liegenden Leseraster Homologien zu Proteinen aufweisen, die an Transportprozessen beteiligt sind. Die Länge des RNA-Transkripts von lly konnte im Northern-Blot mit ungefähr 1,8 kb bestimmt werden und läßt damit auf die gemeinsame Transkription des lly-Gens mit dem unmittelbar upstream liegenden Leseraster schließen. Durch Sequenzanalysen konnte aufgezeigt werden, daß das für diesen Phänotyp verantwortliche Legiolysin-Gen für eine p-Hydroxyphenylpyruvat-Dioxygenase (HPPD) kodiert. Dieses Enzym katalysiert die Umsetzung von p-Hydroxyphenylpyruvat zu Homogentisat (HGA). In Zusammenarbeit mit Prof. P. Proksch (Pharmazeutische Biologie, Würzburg) konnte im Vergleich zu lly-negativen L. pneumophila- und rekombinanten E. coli-Stämmen in den Kulturüberständen von lly-positiven Stämmen auf Basis einer Hochdruck-Flüssigkeits-Chromatographie (HPLC) HGA nachgewiesen werden. Es konnte somit gezeigt werden, daß das Legiolysin-Gen für ein Protein mit HPPD- Aktivität kodiert, und in die Degradation der aromatischen Aminosäuren Phenylalanin und Tyrosin involviert ist. Des weiteren wurden chromosomale Integrationsmutationen der aus L. pneumophila stammenden Gene lly und mip ("macrophage infectivity potentiator") in E. coli K-12 Stämmen erstellt. Diese wurden nachfolgend in ökologisch ausgerichteten Langzeitstudien eingesetzt. Die chromosomale Integration von lly erfolgte als ortsspezifische Rekombination in die l att - site von E. coli WM 2269. Die Integration von mip erfolgte in die fim-Region des E. coli K-12-Stammes AAEC 160. Der zweite Teil der vorliegenden Arbeit befaßt sich mit ökologischen Studien zur Persistenz von L. pneumophila in der Umwelt. Durch die Bestrahlung mit Licht über einen Verlauf von sieben Tagen konnte gezeigt werden, daß die Exprimierung von lly zu einer Persistenz unter Lichtstreß führt. Dieser Lichtschutz könnte in der Umwelt, aber auch bei der Sanierung von Wasserleitungssystemen mittels UV-Licht Relevanz aufweisen. Die Assoziation von L. pneumophila JR32 und JR32-1 (lly-negativ) mit dem Cyanobakterium Fischerella wurde in Mikrokosmen über einen Verlauf von sieben Tagen beobachtet. Dabei konnte gezeigt werden, daß Legionella in Assoziation mit Fischerella bzw. in dessen Überstand zu persistieren vermag, während dies den Bakterien in frischem Fischerella-Medium nicht möglich war. Wie die Coinkubation der Fischerellen mit L. pneumophila JR32-1 zeigte, spielt die Expression von lly dabei keine Rolle. Ein Wachstum der Bakterienkulturen konnte weder im Fischerella-Überstand, noch in Fischerella-Medium beobachtet werden. Durch Rasterelektronenmikroskopie konnte der adhäsive Charakter der Assoziation von L. pneumophila zu Fischerella dokumentiert werden. Durch Persistenzstudien von L. pneumophila und E. coli in Boden wurde die Überlebensfähigkeit der Mikroorganismen in suboptimaler Umgebung getestet. Für Legionella ist eine rapide Abnahme der Zellzahl schon nach kurzer Zeit zu detektieren. Nach sechs Tagen konnten keine Zellen mehr kultiviert werden. Die Defizienz der Pathogenitäts- und Umweltfaktoren Mip, Fla (Flagellin) und Lly hatte dabei keinen Einfluß auf die Persistenz der Bakterien im Boden. Zudem sind die zuvor generierten rekombinanten E. coli-Klone AAEC 160-1 und WM 2269-1 mit genomischer mip- bzw. lly-Integration eingesetzt worden. Innerhalb von vier Wochen konnte für diese Stämme eine kontinuierliche Reduktion der Zellzahlen beobachtet werden. Somit erwies sich keiner der Organismen als erfolgreicher Besiedler der Bodenprobe. Die Studien zum Verlust der Kultivierbarkeit von L. pneumophila und E. coli erfolgten in autoklaviertem Leitungswasser bzw. PBS und zwei unterschiedlich behandelten Varianten von Mainwasser. Neben sterilfiltriertem Mainwasser fand die Inokulierung der Organismen auch in einem Ansatz mit autoklaviertem Mainwasser statt. Es konnte gezeigt werden, daß L. pneumophila in Leitungswasser und Mainwasser außerordentlich gut zu persistieren vermochte. Zudem konnte dokumentiert werden, daß auch E. coli DH5a in ein lebensfähiges, aber nicht mehr kultivierbares Ruhestadium (viable but nonculturable, VBNC) eintreten kann. Parallel zur Ermittlung der CFU-Werte wurden während des Verlaufs der Experimente die Lebendzellzahlen durch Fluoreszenzfärbungen bestimmt. Der Übergang von L. pneumophila in das VBNC-Ruhestadium wurde zudem durch in situ - Hybridisierungen mit fluoreszenzmarkierten 16 S rRNA-Oligonukleotidsonden dokumentiert. Im Naturhaushalt spielt dieser Übergang zu VBNC-Stadien bei Umweltbakterien zur Überwindung ungünstiger Phasen eine große Rolle. Schließlich erfolgten Experimente zur Reaktivierung der VBNC-Ruhestadien. Diese Reaktivierung ist abhängig von speziesspezifischen Triggern und kann bei L. pneumophila durch Coinkubation mit Acanthamoeba castellanii erfolgen.
Distinct juvenile behaviour differences, changes in adult sizes and reproductive capacity and a long reproductive period triggered the working hypothesis of two alternative life-cycle strategies favouring aestivation or immediate reproduction. The hypothesis for the life-cycles of Hyperolius nitidulus that differed from the commonly assumed reproductive strategy for this species was confirmed by the results of this study. Aestivated juveniles start to mature at the beginning of the rainy season and reproduce subsequently. Their tadpoles grow until metamorphosis and either reproduce in this same season, in which case their offspring aestivates (one year - two generations), or they delay reproduction to the following year and aestivate themselves (one year - one generation). Juveniles trying to reproduce as fast as possible will invest in growth and differentiation and show no costly adaptations to aestivation, while juveniles delaying reproduction to the following rainy season will be well adapted to dry season conditions. Indirect evidence for the existence of a second generation was found in all three investigation years: adult size decreased abruptly towards the end of the rainy season, mainly due to the arrival of very small individuals, and clutch size decreased abruptly. Also at the end of the rainy season juveniles had two behavioural types: one hiding on the ground and clearly avoiding direct sunlight and another sitting freely above ground showing higher tolerance towards dry season conditions (high air temperatures and low humidity). Skin morphology differed between the types showing many more purine crystals in a higher order in the dry-season adapted juveniles. The final proof for the existence of a second generation came with the recapture of individuals marked as juveniles when they left the pond. The 45 recaptured frogs definitely came back to the pond to reproduce during the same season in 1999. Second generation frogs (males and females) were significantly smaller than the rest of all adults and egg diameter was reduced. Clutch size did not differ significantly. It was found that females did not discriminate against second generation males when coming to the ponds to reproduce. Second generation males had a similar chance to be found in amplexus as first generation males. Indirect and direct evidence for a second generation matched very well. The sudden size decrease in adults occurred just at the time when the first marked frogs returned. The observation that freshly metamorphosed froglets were able to sit in the sun directly after leaving the water led to the assumption that the decision whether to aestivate or to reproduce already happens during the frogs' larval period. Water chemistry and the influence of light was investigated to look for the factors triggering the decision, but only contaminated water increased the number of juveniles ready for aestivation. Whether the life history polymorphism observed in Hyperolius nitidulus is due to phenotypic plasticity or genetic polymorphism is still not known. Despite this uncertainty, there is no doubt that the optimal combination of different life histories is profitable and may be a reason for the wide range and high local abundance of Hyperolius nitidulus.
Based on queries of the phytosociological databank BERGWALD, a compilation of 3.504 forest vegetation plots from the Bavarian Alps, the ecological niche of Abies alba is re-assessed. The tree species occurs mostly admixed in mountain forests with Fagus and Picea rather than forming distinctive communities of its own. Climatically, Abies is widely distributed to the upper limit of the montane belt, but occurs only sparsely in subalpine forest. Analysis of Ellenberg indicator values based on total species composition yielded the following results: As a tolerant species Abies regeneration has a marked preference for shady forest, which in turn Abies tree layers themselves help create. It also has a clear preference for acidic topsoil conditions. Sites with low N-supply, such as early successional stages on raw carbonate soils, are rarely colonised by Abies. Also, dry and markedly wet forest sites in the region are avoided by Abies. Permutation-based indicator species analysis found a large number of common forest species as being significantly associated with Abies and its frequent companion Fagus sylvatica, whereas there is a negative relationship with more specialised Seslerion and Erico-Pinion species. As Abies alba has very few specific companion species not shared with either Fagus or Picea, the delimitation of Abietetum-syntaxa appears mostly motivated by ecological rather than phytosociological considerations. As a result of its susceptibility towards game browsing, Abies regeneration is an indicator of high woody species richness. The study broadly confirms Abies alba's status as a climax species intermediate between Fagus and Picea, and demonstrates the potential of large phytosociological databanks for niche modelling.
The optimal probability and distance of dispersal largely depend on the risk to end up in unsuitable habitat. This risk is highest close to the habitat’s edge and consequently, optimal dispersal probability and distance should decline towards the habitat’s border. This selection should lead to the emergence of spatial gradients in dispersal strategies. However, gene flow caused by dispersal itself is counteracting local adaptation. Using an individual based model we investigate the evolution of local adaptations of dispersal probability and distance within a single, circular, habitat patch. We compare evolved dispersal probabilities and distances for six different dispersal kernels (two negative exponential kernels, two skewed kernels, nearest neighbour dispersal and global dispersal) in patches of different size. For all kernels a positive correlation between patch size and dispersal probability emerges. However, a minimum patch size is necessary to allow for local adaptation of dispersal strategies within patches. Beyond this minimum patch area the difference in mean dispersal distance between center and edge increases linearly with patch radius, but the intensity of local adaptation depends on the dispersal kernel. Except for global and nearest neighbour dispersal, the evolved spatial pattern are qualitatively similar for both, mean dispersal probability and distance. We conclude, that inspite of the gene-flow originating from dispersal local adaptation of dispersal strategies is possible if a habitat is of sufficient size. This presumably holds for any realistic type of dispersal kernel.
Summary Timber harvesting is currently the most common commercial utilisation activity in tropical forests. Assessing the effects of logging on different aspects of biodiversity and general ecosystem properties is hence of prime importance if the few remaining areas of intact tropical forest are to be protected effectively and efficiently. Tropical amphibian communities are an appropriate model system for studies on the impacts of human-induced environmental changes on the dynamics of complex biological systems. This thesis elaborates on patterns of diversity changes in tropical forest amphibian communities facing habitat alterations associated with selective logging in two globally important eco-regions (Côte d’Ivoire, Upper Guinea, West Africa and Guyana, the Guiana Shield, northern South America). The thesis is organised along two main themes. After a general introduction, a section on general methodology and an introduction to the model systems studied, the first theme moves from general patterns to underlying processes. A second theme running through both chapters carries from undisturbed systems to disturbed systems. A final section integrates findings and addresses implications for conservation management of anthropogenically altered tropical forests. Several case studies at the species- population and community level are being presented and data on the direct and indirect impacts of anthropogenic habitat alteration on respective organizational levels are provided. A key statement that is stressed on throughout the studies is the fact that common measures of diversity, such as species richness and species-diversity only inadequately reflect processes of diversity change following anthropogenic disturbance. They also fail to describe actual impacts on the dynamics of complex biological systems. It is argued that commonly used measures produce an incoherent and insufficient picture of diversity patterns and the underlying processes that shape these patterns. Thus, an understanding of higher levels of diversity, such as β-diversity and functional diversity (and hence compositional patterns) appears to be the key to effectively mitigating the impacts of human-induced disturbance on amphibian communities. It is shown that the predictability of amphibian community composition depends on the respective level of anthropogenic disturbance imposed on a particular habitat. Hence, human activities that lead to changes in the structure of a forest, such as logging, not only alter simple system descriptors, such as the number of species in a given community, but rather alter the dynamics of the entire system. In this context, functional diversity is shown to be an important aspect underlying the actual mechanism that leads to the observed change of predictability patterns. Functional differences between species, rather than number of species per se appear to be the decisive factor in sustaining desirable ecosystem states and thus in maintaining important ecosystem services. Because biological diversity appears to play a substantial role in ecosystem resilience required to safeguard essential ecosystem functions in the face of environmental change, the thesis calls for a critical revision of common diversity assessments approaches. The studies advocate the reconsideration of the uncritical use of widespread measures and descriptors of biodiversity on grounds of inconsistent patterns found throughout numerous studies, including those presented herein.
Amphibian communities of the dry forest of Western Madagascar : taxonomy, ecology and conservation
(2006)
The amphibian fauna of the Kirindy dry forest in western Madagascar Abstracts of chapter 5 and 6 Living apart together – patterns of tadpole communities in a western Madagascan dry forest Whether communities are established in a deterministic or in a stochastic manner depends to a large degree on the spatial scale considered. In this study we use a tadpole community in the dry forest of western Madagascar to show that when within-site habitat diversity is considered, communities may also differ in two community parameters (species composition and species richness) within one geographic scale. Forest ponds and riverbed ponds are two types of breeding habitat that are both used by anurans but that differ generally in their temporal availability, predation pressure, and environmental characteristics. In forest ponds, tadpole communities were very predictable by the physical properties of the ponds and by their vegetation characteristics. In contrast, the riverbed communities were not predictable. We offer two hypotheses to explain this phenomenon. This study clearly demonstrates differing patterns in community organization in two natural habitats within one site, and therefore, highlights the importance of considering local conditions and within-site habitat diversity in community studies. Modeling the habitat use of an endangered dry-forest frog from Western Madagascar A crucial factor for the successful reproduction and thus conservation of an amphibian species is the availability of suitable waters as breeding sites. In this chapter, we examine the use of breeding sites of an endangered, local endemic frog of Western Madagascar, Aglyptodactylus laticeps, over a three year period. Logistic regression was used to model the relationship between the species’ breeding habitat use and environmental variables. This model was aimed to be predictive, rather than explanatory, and only environmental variables were included that are assessable in a time and cost effective manner, and that can therefore be used as an easy-to-use management tool in applied conservation. On the local scale of the Kirindy concession, A. laticeps is restricted to forest with a relatively low degree of disturbance and closed canopy cover. The model identified three environmental variables that suffice to satisfactorily predict the use of respective breeding sites, namely leaf litter, vegetation coverage and surface water plants. Based on these results, we present recommendations for the conservation management of this frog. Furthermore, the presence or absence of this species within its natural range indicates the relative degree of environmental integrity of its habitat, and we therefore consider this species as a suitable indicator species of temporary aquatic habitats within the dry forest that are characterized by a low water permanency and high leaf litter coverage. This study demonstrates that models constructed from basic ecological knowledge of relevant species may serve as valuable management tools in applied conservation.
Leonia cymosa (Violaceae) is a small tree from the under story of the Amazonian rain forest. I investigated the seed dispersal ecology of L. cymosa in plots of old growth terra firme forest located within the Cuyabeno Faunistic Reserve in north-eastern Ecuador. This species offered good conditions to examine the variation of traits of individual trees and the way they are linked with fruit removal from each tree. With this study I aimed to address the question whether frugivores exert selection pressures on fruits and the fruiting regime of fleshy fruited plants. The mean height of a fruiting L. cymosa was 6.6 m (range: 2 - 12.6 m). The median tree density was 11.8 trees per hectare. Trees grew in clusters consisting of different numbers of trees of different heights. L. cymosa flowered two times a year, in late February to March and in October. The respective fruiting seasons occurred in August/September and between March and May. The fruit pulp of L. cymosa contained the sugars fructose, glucose, and sucrose, the total soluble sugar being the first important nutritional compound of the fruit pulp. The second important compound was proteins. No lipids were found in the fruit pulp. The variation of nutritional quality of the fruits was high within trees. Nonetheless, significant differences were found among trees in all nutrient constituents studied. The maximum of ripe fruits produced per season by a single tree was 427. Median productivity of the trees was 45 ripe fruits throughout the fruiting season in 1999 (n=57) and 36 ripe fruits in 2000 (n=92). The maximum standing crop of fruits in a tree was 324 fruits (counted in 2000). Black mantle tamarins, Saguinus nigricollis (Callitrichidae), and squirrel monkeys, Saimiri sciureus (Cebidae), and possibly an unknown nocturnal frugivore consumed the fruits of L. cymosa at my study site. Green-rumped acouchis (Myoprocta pratti, Dasyproctidae) consumed fallen fruits and seeds underneath the trees. Black mantle tamarins and squirrel monkeys differed widely in their effectiveness as seed dispersers. Black mantle tamarins swallowed the seeds together with the fruit pulp and defecated intact seeds far away from the mother tree. Squirrel monkeys opened the fruits to suck and gnaw on the fruit pulp, and then dropped seeds to the forest floor below the tree crowns. Each of my study plots fell into the core home range of one group each of S. nigricollis and S. sciureus. Thus, the frugivore assemblage is small and disperser availability is limited for the individual tree of L. cymosa. In a sample of 6 trees of comparable and high fruit crop size, the total of ripe fruits removed from a tree throughout the whole fruiting season by the reliable seed disperser S. nigricollis was neither significantly correlated with the content of any of the nutrients measured in the fruit pulp (fructose, glucose, sucrose, total protein; pulp does not contain lipids), nor with total metabolisable energy, seed to pulp weight ratio, or water content of the fruit pulp. Feeding preferences for single sugars determined by other laboratory studies were not confirmed by this field study. The reliable seed disperser S. nigricollis does not seem to exert selective pressure on the nutrient content of the fruits of L. cymosa. Seasonal fruit crop size was the main predictor of all aspects of fruit removal by the effective disperser of L. cymosa, Saguinus nigricollis, as well as by the non-disperser, Saimiri sciureus. Trees with larger seasonal fruit crop size had a higher probability to have fruits removed by the disperser than those with small seasonal fruit crop sizes. They also had a higher number of fruits removed by the seed disperser. However, the proportion of fruits removed by the disperser decreased with increasing seasonal fruit crop size. In contrast, probability of fruit removal, the number of fruits removed, and the proportion of fruits removed by the non-disperser increased with increasing seasonal fruit crop sizes. The observed differences between disperser and non-disperser are due to differences in feeding capacity, group size and foraging behavior. Tamarins were less likely to harvest Leonia trees that were not or less completely covered by surrounding vegetation. This probably reflects a behavior to avoid predation by forest raptors. At high con-specific fruit abundance in the neighborhood, the proportion of fruits removed by tamarins was reduced. This suggests competition of trees for the disperser. My study revealed selection of the disperser on seasonal fruit crop size of L. cymosa. My results are consistent with the “fruit crop size hypothesis”. FCSH appears to constitute a valid framework also in the monkey-dispersed L. cymosa. My findings also show that factors beyond the tree’s control influenced fruit removal from Leonia trees. Disperser-mediated selection may be constrained (yet not impeded) by neighborhood conditions.
Die oberirdischen Oberflächen von Pflanzen sind von komplexen mikrobiellen Konsortien besiedelt deren Zusammensetzung von verschiedenen Faktoren abhängig ist. In der vorliegenden Promotionsarbeit wurden zwei Eigenschaften pflanzlicher Oberflächen auf mögliche Auswirkungen auf ihre bakterielle Besiedelung hin untersucht. Dazu wurden Wildtyplinien und Mutanten von Arabidopsis thaliana eingesetzt. Zunächst wurde die bakterielle Besiedelung von A. thaliana Wildtyplinien in kultivierungsbasierten Experimenten untersucht. Es wurde hierbei ein Überblick über die kultivierbare Diversität auf Pflanzen, die unter kontrollierten Bedingungen im Klimaschrank gewachsen waren und Pflanzen, die einen Freilandaufenthalt durchlaufen hatten, gewonnen. Der Einfluss von nicht-drüsigen Trichomen von A. thaliana auf die Quantität und Diversität der bakteriellen Besiedelung wurde am A. thaliana Col-0-Wildtyp mit normaler Behaarung und der trichomlosen gl1-Mutante untersucht. Mithilfe von DAPI-Färbungen und nachfolgender Zellzählung wurden die bakteriellen Gemeinschaften der beiden Pflanzenlinien quantifiziert. Dabei zeigten sich keine pflanzenlinienspezifischen Unterschiede. Durch die Amplifizierung der bakteriellen 16S rRNA-Gene der Gemeinschaft und den nachfolgenden Einsatz der Denaturierenden Gradientengelelektrophorese (DGGE) wurde ein Überblick über die Diversität der vorherrschenden Bakteriengruppen gewonnen. Obwohl Trichome als bevorzugte Siedlungsplätze von Bakterien gelten, wurden hier auch hinsichtlich der Diversität der bakteriellen Gemeinschaften keine Unterschiede zwischen den untersuchten Pflanzenlinien gefunden. Als weiteres artspezifisches Merkmal von Pflanzenoberflächen wurde die Zusammensetzung der kutikulären Wachse als Einflussfaktor untersucht. Dafür wurden vier eceriferum-Mutanten (cer) von A. thaliana in Landsberg erecta (Ler) Wildtyp-Hintergrund eingesetzt, die sich hinsichtlich der kutikulären Wachszusammensetzung ihrer Blätter unterschieden. Zur Untersuchung der Diversität der bakteriellen Besiedelung wurde zunächst ein DGGE-Screening durchgeführt. Hier zeigten sich deutliche pflanzenlinienspezifische Unterschiede, die vor allem die Gemeinschaften der cer9- und der cer16-Mutante betrafen. Zur genaueren Charakterisierung der bakteriellen Gemeinschaften der fünf Pflanzenlinien wurde die Amplicon-Pyrosequenzierung eingesetzt. Hierbei stellte sich die bakterielle Diversität auf allen Pflanzenlinien entsprechend des Phyllosphärenhabitats moderat divers und ungleich verteilt dar. Die Identifizierung der sequenzierten Phylotypen ließ eine bakterielle Kerngemeinschaft erkennen. Weiterhin wurden 35 Phylotypen identifiziert, die differenziell auf einzelnen Pflanzenlinien auftraten. Hier handelte es sich um den pflanzenlinienspezifischen Teil der bakteriellen Gemeinschaften. Die statistische Analyse zeigte deutlich divergente Muster für die analysierten Bakteriengemeinschaften der fünf Pflanzenlinien. Vor allem die Gemeinschaften der cer6-, cer9- und cer16-Linie konnten in einer UniFrac-basierten Clusteranalyse von den anderen Pflanzenlinien abgegrenzt werden. Diese Ergebnisse zeigen klar, dass die Mutationen in der Wachsbiosynthese zu divergenten bakteriellen Gemeinschaften führten.
Insects are responsible for the major part of the ecosystem services pollination and natural pest control. If insects decline, these ecosystem services can not longer be reliably delivered. Agricultural intensification and the subsequent loss and fragmentation of habitats has among others been identified to cause insect decline. Ecological intensification aims to promote alternative and sustainable management practices in agricultural farming, for example to decrease the use of external inputs such as pesticides. Agri-environment schemes make amends for farmers if they integrate ecologically beneficial measures into their farming regime and can therefore promote ecological intensification. There is a wide variety of agri-environment schemes, but the implementation of sown flower fields on crop fields is often included. Flower fields offer foraging resources as well as nesting sites for many different insect species and should be able to support insect populations as well as to increase ecosystem services to adjacent fields. However, the potential of flower fields to exhibit these effects is depending on many factors. Among others, the age and size of the flower field can influence if and how different insects profit from the measure. Additionally, the complexity of the surrounding landscape and therefore the existing biodiversity is influencing the potential of flower fields to increase ecosystem services locally. The goal of this study is to disentangle to which degree these factors influence the ecosystem services pollination and natural pest control and if these factors interact with each other. Furthermore, it will be examined if and how flower fields and ecosystem services influence crop yield. Additional factors examined in this study are distance decay and pesticide use. The abundance of beneficial insects can decrease strongly with increasing distance to suitable habitats. Pesticide use in turn could abrogate positive effects of flower fields on beneficial insects.
To examine these different aspects and to be able to make recommendations for flower field implementation, field experiments were conducted on differently composed sown flower fields and adjacent oilseed rape fields. Flower fields differed in their age and continuity as well as in their size. Additionally, flower and oilseed rape fields were chosen in landscapes with different amounts of semi-natural habitat. Oilseed rape fields adjacent to calcareous grasslands and conventional crop fields served as controls. Pollinator observations and pollen beetle and parasitism surveys were conducted in the oilseed rape fields. Additionally, different yield parameters of the oilseed rape plants were recorded. Observations were conducted and samples taken in increasing distance to the flower fields to examine distance decay functions. Spray windows were established to inspect the influence of pesticides on ecosystem services and crop yields. Linear mixed models were used for statistical analysis.
The results show, that newly established flower fields with high amounts of flower cover are very attractive for pollinators. If the flower fields reached a certain size (> 1.5ha), the pollinators tended to stay in these fields and did not distribute into the surroundings. High amounts of semi-natural habitat in the surrounding landscape increased the value of small flower fields as starting points for pollinators and their subsequent spillover into crop fields. Additionally, high amounts of semi-natural habitat decreased the decay of pollinators with increasing distance to the flower fields. Based on these results, it can be recommended to establish many small flower fields in landscapes with high amounts of semi-natural habitat and large flower fields in landscapes with low amounts of semi-natural habitat. However, it is mentionable that flower fields are no substitute for perennial semi-natural habitats. These still must be actively conserved to increase pollination to crop fields.
Furthermore, the lowest amount of pollen beetle infestation was found on oilseed rape fields adjacent to continuous flower fields aged older than 6 years. Flower fields and calcareous grasslands in general increased pollen beetle parasitism in adjacent oilseed rape fields compared to conventional crop fields. The threshold for effective natural pest control could only be reached in the pesticide free areas in the oilseed rape fields adjacent to continuous flower fields and calcareous grasslands. Parasitism and superparasitism declined with increasing distance to the adjacent fields in pesticide treated areas of the oilseed rape fields. However, they remained on a similar level in spray windows without pesticides. Large flower fields increased parasitism and superparasitism more than small flower fields. Flower fields generally have the potential to increase pollen beetle parasitism rates, but pesticides can abrogate these positive effects of flower fields on natural pest control.
Last but not least, effects of flower fields and ecosystem services on oilseed rape yield were examined. No positive effects of pollination on oilseed rape yield could be found. Old and continuous flower fields increased natural pest control in oilseed rape fields, which in turn increased seed set and total seed weight of oilseed rape plants. The pesticide treatment had negative effects on natural pest control, but positive effects on crop yield. Pollination and natural pest control decreased with increasing distance to the field edge, but fruit set slightly increased. The quality of the field in terms of soil and climatic conditions did not influence the yield parameters examined in this study. Yield formation in oilseed rape plants is a complex process with many factors involved, and it is difficult to disentangle indirect effects of flower fields on yield. However, perennial flower fields can promote ecological intensification by increasing crop yield via natural pest control. This study contributes to a better understanding of the effects of differently composed flower fields on pollination, natural pest control and oilseed rape yield.