Most soils develop distinct soil architecture during pedogenesis and soil organic carbon (SOC) is sequestered within a hierarchical system of mineral-organic associations and aggregates. Permafrost soils store large amounts of carbon due to their permanently frozen subsoil and a lack of oxygen in the active layer, but they lack complex soil structure. With permafrost thaw more oxidative conditions and increasing soil temperature presumably enhance the build-up of more complex units of soil architecture and may counterbalance, at least partly, SOC mineralization. We aim to explore the development of mineral-organic associations and aggregates under different permafrost impact with respect to SOC stabilization. This information will be linked to environmental control factors relevant for SOC turnover at the pedon and stand scale to bridge processes occurring at the aggregate scale to larger spatial dimensions. We will combine in situ spectroscopic techniques with fractionation approaches and identify mechanisms relevant for SOC turnover at different scales by multivariate statistics and variogram analyses. From this we expect a deeper knowledge about soil architecture formation in the transition of permafrost soils to terrestrial soils and a scale-spanning mechanistic understanding of SOC cycling in permafrost regions.
The proposal addresses the potential of subsoil to contribute to K nutrition of crops. More specifically we will address the processes controlling release of K from interlayer of 2:1 clay minerals as this is expected to be the dominant K fraction in the subsoil. While it has been shown in the past that this so called 'non-exchangeable' K can be released due to root activity, there are controversial results concerning the role of soil solution K concentration in the rhizosphere required to trigger the process. Likewise little information is available about the concentration dynamics of other cations (NH4, Ca) in the rhizosphere and their impact on K release and vermiculitization supposed to be associated with this process. Model studies with substrate from the central field trial will be conducted in compartment systems equipped with micro suction cups. The measurement of dynamic changes of soil solution composition with increasing distance from the root surface will be combined with investigations of changes in mineralogy by XRD, TEM and SEM-EDX. Changes of mineralogy as a result of plant induced K release from interlayer will also be studied on bulk soil and rhizosphere samples collected within the central field and the central microcosm experiment and with mineral bags exposed in the field during a cropping cycle. Finally, X-ray CT will be used to access changes in soil texture, i.e. clay distribution around roots and the temporal spread of roots in biopores which is a prerequisite for K uptake from such structures.
Mikroplastik wird zwischen Land- und Wasseroberflächen und der Atmosphäre ausgetauscht und kann luftgetragen über weite Strecken transportiert werden, bevor die Mikroplastikpartikel wieder aus der Atmosphäre entfernt und abgelagert werden. Obwohl diese Transportprozesse für die Verteilung und die wirksamen Abbaumechanismen von Mikroplastik sehr wichtig sind, gibt es bislang keine systematischen Untersuchungen zum atmosphärischen Transport von Mikroplastik. Der luftgetragene Transport von Mikroplastik wird im vorliegenden Teilprojekt in einem Windkanal als idealisiertem Modellsystem experimentell untersucht und mit einem strömungsauflösenden Transportmodell numerisch simuliert, um die grundlegenden Prozesse verstehen und quantifizieren zu können.
The nature of the microbial communities inhabiting the deeper soil horizons is largely unknown. It is also not clear why subsurface microorganisms do not make faster use of organic compounds under field conditions. The answer could be provided by a reciprocal soil transfer experiment studying the response of transferred soils to fluctuations in microclimate, organic inputs, and soil biota. The subproject P9 will be responsible for the establishment of reciprocal transfer experiments offering a strong link between subgroups interested in organic matter quality, transport of organic substances, as well as functions of the soil microbial community. A single, high molecular weight substrate (13C labelled cellulose) will be applied at two different levels in the pre-experiment to understand the dose-dependent reaction of soil microorganisms in transferred surface and sub-soils. Uniformly 13C labelled beech roots - representing complex substrates - will be used for the main reciprocal soil transfer experiment. We hypothesize that transferring soil cores between subsoil and surface soil as well as addition of labelled cellulose or roots will allow us to evaluate the relative impact of surface/subsurface habitat conditions and resource availability on abundance, function, and diversity of the soil microbial community. The second objective of the subproject is to understand whether minerals buried within different soil compartments (topsoil vs. subsoil) in the field contribute to creation of hot spots of microbial abundance and activity within a period of two to five years. We hypothesize that soil microorganisms colonize organo-mineral complexes depending on their nutritional composition and substrate availability. The existence of micro-habitat specific microbial communities could be important for short term carbon storage (1 to 6 years). The third objective is to understand the biogeography and function of soil microorganisms in different subsoils. Parent material as well as mineral composition might control niche differentiation during soil development. Depending on size and interconnectedness of niches, colonization and survival of soil microbial communities might be different in soils derived from loess, sand, terra fusca, or sandstone. From the methodological point of view, our specific interest is to place community composition into context with soil microbial functions in subsoils. Our subgroup will be responsible for determining the abundance, diversity, und function of soil microorganisms (13C microbial biomass, 13C PLFA, enzyme activities, DNA extraction followed by quantitative PCR). Quantitative PCR will be used to estimate total abundances of bacteria, archaea and fungi as well as abundances of specific groups of bacteria at high taxonomic levels. We will apply taxa specific bacterial primers because classes or phyla might be differentiated into ecological categories on the basis of their life strategies.
The vegetation of East and South African savannahs has been shaped by the complex interaction of geo-biophysical processes and human impact. For both regions a controversial discussion is pertinent, as to whether massive degradation threatens the sustainability of livelihoods in these regions. Rangeland vegetation is mainly affected by environmental conditions (soil and climate) and by livestock management. Extent and interaction of these drivers are not well understood but have profound impacts on the resilience and vulnerability of these systems to be shifted toward unfavourable degraded or bush encroached states. The project aims to analyse and model rangeland vegetation in response to range management including livestock, soil quality and climatic conditions and to assess the impacts of changes in these conditions on the resilience and vulnerability of rangeland systems. Field measurements, remote sensing of vegetation patterns and dynamics and simulation modelling will be used to understand the dynamics of rangeland vegetation. We will use the 'fast' or 'state' variables potential of pastures to produce palatable biomass, the variability of this production, and the system's potential to recover from disturbance impact as indicators of resilience. 'slow' variables that control (or drive) the 'fast' variables such as management, climate and soil variables are recorded in cooperation with other subprojects as with A1 for soil variables. Results of the project will show which management activities are most favourable for individual regions to sustain plant production in the long term.
Populations of P. fortinii from allover Europe are examined using microsatellites to construct gene genealogies and infer evolutionary history. The tree-root endophyte Phialocephala fortinii s.l. (mitosporic Ascomycota) is the dominant colonizer of conifer root systems in forests in the northern hemisphere. P. fortinii s.l. is genetically highly diverse and forms a complex of several cryptic species. Recombination occurs or has occurred within cryptic species and to some extent also among them (introgression). Cryptic species occur sympatrically and they can form large thalli, but it remains unclear whether the observed patterns of spatial distribution reflect local climax situations or are the results of recent gene and genotype flow. One of the key objectives will be to estimate population genetic parameters (eg. migration rates, genotype flow, recombination) within and among populations of cryptic species in forests where man-mediated genotype flow can be excluded. Other key objectives are the determination of the number, frequency, distribution and evolutionary history of the cryptic species in Europe and to identify the driving forces for speciation. The approach will be multidisciplinary and will include standard mycological and microbiological methods as well as molecular genetic techniques such as microsatellite fingerprinting and DNA sequencing. The evolutionary history of haplotypes at both the population and species level will be reconstructed and the results will be compared with known patterns of pleistocenic glaciations and postglacial recolonization of host trees. The project will be a significant contribution to the understanding of the population and evolutionary genetics of a versatile and ecologically extremely successful fungal genus and it will shed light on the effects of pleistocenic and postglacial climatic changes on fungal speciation.
Die große Sauerstoffkatastrophe (Great Oxidation Event - GOE) kennzeichnet den starken Anstieg von molekularem Sauerstoff (O2) in der Atmosphäre während der Frühgeschichte der Erde, was flächendeckende Habitabilität ermöglicht und komplexes Leben auf der Erde erlaubt. Viele Fragen sind diesbezüglich weiterhin offen. Was dazu führte, dass sich Sauerstoff in der Atmosphäre anreicherte, der Zeitpunkt und das Ausmaß sind nicht gut bestimmt. Erst jetzt ist es möglich die komplizierten Wechselwirkungen zwischen atmosphärischen, biologischen und geologischen Prozessen zu identifizieren. Das sich daraus ergebende Absterben methanogener Lebensformen und das Auftreten eines sogenannten Schneeball-Erden-Zustandes sind Beispiele für die extremen Auswirkungen des GOE. Eine zentrale Frage, die wir untersuchen, ist ob der GOE in einem linearen oder, aufgrund einer möglichen Bistabilität von Sauerstoff, in einem sprungweisen Anstieg von O2 erfolgte. Des Weiteren studieren wir den Einfluss des Kohlenstoffzyklus und des Klimas auf die Charakteristika und den Zeitpunkt des GOE. Wir wenden unsere Erfahrung in eindimensionalen (1D) und 3D Klimamodellierungen an, um die Auswirkung unterschiedlicher Klima auf den GOE zu ermitteln. Um dies zu erreichen entwickeln und verwenden wir unser einzigartiges Atmosphärenmodell mit detailliertem Sauerstoffzyklus (inklusive zum Beispiel Verwitterungsprozesse, atmosphärische Photochemie) welches die Atmosphäre, Biosphäre und Geosphäre umfasst. Ein wichtiges Ziel ist die Analyse der Kernprozesse für den GOE unter der Berücksichtigung jüngster Ergebnisse geologischer Untersuchungen (zu zum Beispiel Oberflächendruck, atmosphärischen Treibhausgases, usw.).
Durum wheat is mainly grown as a summer crop. An introduction of a winter form failed until now due to the difficulty to combine winter hardiness with required process quality. Winter hardiness is a complex trait, but in most regions the frost tolerance is decisive. Thereby a major QTL, which was found in T. monococcum, T.aestivum, H. vulgare and S.cereale on chromosome 5, seems especially important. With genotyping by sequencing it is now possible to make association mapping based on very high dense marker maps, which delivers new possibilities to detect main and epistatic effects. Furthermore, new sequencing techniques allow candidate gene based association mapping. The main aim of the project is to unravel the genetic architecture of frost tolerance and quality traits in durum. Thereby, the objectives are to (1) determine the genetic variance, heritability and correlations among frost tolerance and quality traits, (2) examine linkage disequilibrium and population structure, (3) investigate sequence polymorphism at candidate genes for frost tolerance, and (4) perform candidate gene based and genome wide association mapping.
Neben Studien zur Diversität von Gefäßpflanzen in ausgewählten Untersuchungsflächen wurde der Erforschung der endemischen Palmenart Normanbya normanbyi besondere Aufmerksamkeit gewidmet. Im Mittelpunkt stehen Studien zur Blüten- und Fruchtökologie. Dabei wurde u.a. eine bisher unbeschriebene Gattung der Gallmücken entdeckt. Der interdisziplinäre Forschungsansatz soll wesentliche Erkenntnisse über Tier-Pflanze-Interaktionen in Regenwäldern liefern. Hauptaugenmerk liegt auf der Erfassung der Blüten- und Fruchtphänologie eines tropischen Tieflandregenwaldes in Nordostqueensland. Das Projekt beinhaltet die Erfassung der Phänologie aller Unterwuchsarten, Lianen und Baumarten in einer 1 ha großen Untersuchungsfläche. Weiterführend wird die Blühphänologie einer ausgewählten Palmenart Normanbay normanbyi erfasst und mit Hilfe molekulargenetischer Methoden im Zusammenhang mit der Verwandtschaftsstruktur ausgewählter Populationen betrachtet. Die Feldarbeiten für das 2003 begonnene Projekt wurden im Juli 2005 abgeschlossen.
Especially during the last decades, the natural forests of Ethiopia have been heavily disturbed by human activities. Some forests have been totally cleared and converted into fields for agricultural use, other suffered from different influences, such as heavy grazing and selective logging. The ongoing research in the Shashemane-Munessa-study area (Gu 406/8-1,2) showed clearly that, in spite of interdiction and control, forests continue to be cleared and degraded. However, it is not yet sufficiently known, how and why these processes are still going on. Growing population pressure and economic constraints for the people living in and around the forests contribute to the actual situation but allow no final answers to the complex situation. Concerning a sustainable management of the forests there is to no solid basis for recommendations from the socioeconomic and socio-cultural view. Therefore, a comprehensive analysis of the traditional needs and forms of forest use, including all forest products, is necessary. The objective of this project is, to achieve this basis by carrying out intensive field observations, the consultation of aerial photographs, satellite imagery and above all semi-structured interviews with the population in the study area in order to contribute to the recommendations for a sustainable use of the Munessa Shasemane forests.
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