In forest ecosystems ectomycorrhizal fungi are responsible for the mobilization of mineral nutrients from soil organic matter (SOM) resulting in a marked increase in productivity of their symbiotic host plants. In return the fungi obtain a significant amount of photosynthetic products from these plants, allowing the formation of an extensive hyphal system. These hyphae constitute a major part of soil biomass and, ultimately, a major source for SOM formation. While plant-fungal nutrient exchange has been analyzed extensively, this proposal is focused on the fungal contribution to SOM formation and on the processes leading to the acquisition of nutrients by the fungi. These two processes will be studied separately and in a quantitative way using isotopic labeling in soil bioreactors. Analysis of the fate of 13C labeled fungal material (Laccaria bicolor) in soil bioreactors will tell how fast and to what extent the various fractions of hyphal biomass are transformed into non-living SOM. As potential molecular or structural markers for SOM formation from fungal hyphae we will analyze characteristic remnants of fungal hyphae in SOM using scanning electron microscopy, DNAfragments using a PCR approach for the fungal rRNA internal transcribed spacerregions and biochemical markers like fatty acids and ergosterol. The impact of ectomycorrhizal mycelia supported by Pinus sylvestris plantlets on 13C- and 15N-labeled SOM and on microbial biomass will be analyzed in separate soil bioreactor experiments.
Chromium (Cr) is introduced into the environment by several anthropogenic activities. A striking ex-ample is the area around Kanpur in the Indian state of Uttar Pradesh, where large amounts of Cr-containing wastes have been recently illegally deposited. Hexavalent Cr, a highly toxic and mobile contaminant, is present in significant amounts in these wastes, severely affecting the quality of sur-roundings soils, sediments, and ground waters. The first major goal of this study is to clarify the solid phase speciation of Cr in these wastes and to examine its leaching behavior. X-ray diffraction and synchrotron-based X-ray absorption spectroscopy techniques will be employed for quantitative solid phase speciation of Cr. Its leaching behavior will be studied in column experiments performed at un-saturated moisture conditions with flow interruptions simulating monsoon rain events. Combined with geochemical modeling, the results will allow the evaluation of the leaching potential and release kinetics of Cr from the waste materials. The second major goal is to investigate the spatial distribution, speciation, and solubility of Cr in the rooting zone of chromate-contaminated soils surrounding the landfills, and to study the suitability of biochar as novel soil amendment for mitigating the deleterious effects of chromate pollution. Detailed field samplings and laboratory soil incubation studies will be carried out with two agricultural soils and biochar from the Kanpur region.
In structured soils, the interaction of percolating water and reactive solutes with the soil matrix is mostly restricted to the surfaces of preferential flow paths. Flow paths, i.e., macropores, are formed by worm burrows, decayed root channels, cracks, and inter-aggregate spaces. While biopores are covered by earthworm casts and mucilage or by root residues, aggregates and cracks are often coated by soil organic matter (SOM), oxides, and clay minerals especially in the clay illuviation horizons of Luvisols. The SOM as well as the clay mineral composition and concentration strongly determine the wettability and sorption capacity of the coatings and thus control water and solute movement as well as the mass exchange between the preferential flow paths and the soil matrix. The objective of this proposal is the quantitative description of the small-scale distribution of physicochemical properties of intact structural surfaces and flow path surfaces and of their distribution in the soil volume. Samples of Bt horizons of Luvisols from Loess will be compared with those from glacial till. At intact structural surfaces prepared from soil clods, the spatial distribution (mm-scale) of SOM and clay mineral composition will be characterized with DRIFT (Diffuse reflectance infrared Fourier transform) spectroscopy using a self-developed mapping technique. For samples manually separated from coated surfaces and biopore walls, the contents of organic carbon (Corg) and the cation exchange capacity (CEC) will be analyzed and related to the intensities of specific signals in DRIFT spectra using Partial Least Square Regression (PLSR) analysis. The signal intensities of the DRIFT mapping spectra will be used to quantify the spatial distribution of Corg and CEC at these structural surfaces. The DRIFT mapping data will also be used for qualitatively characterizing the small scale distribution of the recalcitrance, humification, and microbial activity of the SOM from structural surfaces. The clay mineral composition of defined surface regions will be characterized by combining DRIFT spectroscopic with X-ray diffractometric analysis of manually separated samples. Subsequently, the spatial distribution of the clay mineral composition at structural surfaces will be determined from the intensities of clay mineral-specific signals in the DRIFT mapping spectra and exemplarily compared to scanning electron microscopic and infrared microscopic analysis of thin sections and thin polished micro-sections. The three-dimensional spatial distribution of the total structural surfaces in the volume of the Bt horizons will be quantified using X-ray computed tomography (CT) analysis of soil cores. The active preferential flow paths will be visualized and quantified by field tracer experiments. These CT and tracer data will be used to transfer the properties of the structural surfaces characterized by DRIFT mapping onto the active preferential flow paths in the Bt horizons.
Soil microorganisms can mobilize and immobilize phosphorus (P), and therefore strongly affect the availability of P to plants. In this project we hypothesize that the ratio of labile P to microbial P increases during the transition from acquiring to recycling ecosystems. Microbial and plant P uptake will be studied with 33P that will be quantified in microbial and plant biomass as well as in lipids. To what extent microorganisms immobilize and mobilize P during decomposition of soil organic matter will be explored with a 14C/33P labeled monoester. Seasonal dynamics of actual and potential P mineralization (33P dilution and phosphatase activity), and microbial P immobilization will be studied with soils of the transition from acquiring to recycling ecosystems. The contribution of litter-derived P will be explored in a litter exclusion experiment in the field. Spatial patterns of microbial and plant P mineralization in the rhizosphere will be explored by analyses of areas of high acid and alkaline (=microbial-derived) phosphatase activity by soil zymography, and their relations with areas of high rhizodeposition (14C imaging). In conclusion, we will analyse mechanisms of actual and potential microbial P mineralization and immobilization, localization, and consequences for P uptake by plants.
In subsoils, organic matter (SOM) concentrations and microbial densities are much lower than in topsoils and most likely highly heterogeneously distributed. We therefore hypothesize, that the spatial separation between consumers (microorganisms) and their substrates (SOM) is an important limiting factor for carbon turnover in subsoils. Further, we expect microbial activity to occur mainly in few hot spots, such as the rhizosphere or flow paths where fresh substrate inputs are rapidly mineralized. In a first step, the spatial distribution of enzyme and microbial activities in top- and subsoils will be determined in order to identify hot spots and relate this to apparent 14C age, SOM composition, microbial community composition and soil properties, as determined by the other projects within the research unit. In a further step it will be determined, if microbial activity and SOM turnover is limited by substrate availability in spatially distinct soil microsites. By relating this data to root distribution and preferential flow paths we will contribute to the understanding of stabilizing and destabilizing processes of subsoil organic matter. As it is unclear, at which spatial scale these differentiating processes are effective, the analysis of spatial variability will cover the dm to the mm scale. As spatial segregation between consumers and substrates will depend on the pore and aggregate architecture of the soil, the role of the physical integrity of these structures on SOM turnover will also be investigated in laboratory experiments.
Sekundäre Partikelneubildung ist eine Hauptquelle für atmosphärische Partikel mit wichtigen Folgen für das Klima und die menschliche Gesundheit. Dieses Vorhaben untersucht die Rolle von Luft Ionen bei der sekundären Partikelneubildung in Flussreaktor- und Aerosolkammer-Experimenten unter kontrollierten Laborbedingungen. Trotz beträchtlicher Fortschritte in der Messtechnik zur Untersuchung der atmosphärischen Nukleation und des Partikelwachstums bestehen weiterhin Verständnislücken hinsichtlich der grundlegenden physikalischen und chemischen Prozesse. Insbesondere die möglichen Effekte von Ionen-Partikel-Wechselwirkungen und von Ionenchemie auf die Partikelneubildung werden kontrovers diskutiert. In Ergänzung zu bestehenden Forschungsprogrammen hinsichtlich der Rolle von Ionen im initialen Nukleationsschritt wird vorgeschlagen, Ionen-Partikel-Wechselwirkungen während des anschließenden Partikelwachstums zu untersuchen und sich dabei auf direkte Messungen des Ladungszustands, der Wachstumsraten und der chemischen Zusammensetzung von sekundärem organischem Aerosol zu konzentrieren. Hierzu werden der Ladungszustand und die Wachstumsraten von Partikelpopulationen mit einem modifizierten Mobilitätspartikelspektrometer unter wohldefinierten Randbedingungen in Laborexperimenten quantifiziert. In einem nächsten Schritt werden die neuartigen Messmöglichkeiten unseres Aerosol-Massenspektrometers CAChUP voll ausgeschöpft, um den Beitrag verschiedener organischer Vorläufergase zur chemischen Zusammensetzung von sekundärem organischen Aerosol bei variierenden Ladungszuständen zu quantifizieren. Schließlich werden die Ergebnisse dieser Experimente durch Messungen zur sekundären organischen Partikelbildung bei wohldefinierten Ionenkonzentrationen an einer Aerosolkammer überprüft. Die vorgeschlagene Forschungsagenda ist somit darauf abgestimmt, mögliche ladungs-katalysierte chemische Mechanismen bei der sekundären Aerosolbildung besser einzuordnen.
Existing models of soil organic matter (SOM) formation consider plant material as the main source of SOM. Recent results from nuclear magnetic resonance analyses of SOM and from own incubation studies, however, show that microbial residues also contribute to a large extent to SOM formation. Scanning electron microscopy showed that the soil mineral sur-faces are covered by numerous small patchy fragments (100 - 500 nm) deriving from microbial cell wall residues. We will study the formation and fate of these patchy fragments as continuously produced interfaces in artificial soil systems (quartz, montmorillonite, iron oxides, bacteria and carbon sources). We will quantify the relative contributions of different types of soil organisms to patchy fragment formation and elucidate the effect of redox con-ditions and iron mineralogy on the formation and turnover of patchy fragments. The develop-ment of patchy fragments during pedogenesis will be followed by studying soil samples from a chronosequence in the forefield of the retreating Damma glacier. We will characterize chemical and physical properties of the patchy fragments by nanothermal analysis and microscale condensation experiments in an environmental scanning electron microscope. The results will help understanding the processes at and characteristics of biogeochemical interfaces.
Ziel dieses Projektes ist die Beschreibung von Strömungsmustern über ästuarinen Bodenformen anhand von Rinnenexperimenten und numerischen Simulationen. Bodenformen (Riffel und Dünen) sind weitverbreitete Bestandteile von Flüssen, Ästuaren, Küstengewässern- und Tiefseegebieten. Bodenformen liefern Hinweise auf Richtung und Stärke von Sedimenttransportprozessen, haben einen starken Einfluss auf die über ihnen liegende Strömung und sind zudem von großer sozioökonomischer Bedeutung, z. B. hinsichtlich ihrer Auswirkungen auf die Schiffbarkeit der Gewässer. In vielen Ästuaren bilden sich aufgrund der starken Hydrodynamik und der hohen Verfügbarkeit von sandigen Sedimenten große Bodenformfelder. Die Strömung über diesen Bodenformfeldern unterscheidet sich grundlegend von der Strömung über den bekannten, dreieckigen Bodenformen mit einem Neigungswinkel von 30°, die bisher im Fokus von Labor- und numerischen Modellierungsstudien standen. Ästuarine Bodenformen sind hauptsächlich flachgeböschte Dünen mit mittleren Luvwinkeln von 5 bis 20°. Die Strömungseigenschaften über derartigen, flachen Winkeln sind derzeit nicht genau bekannt. So ist zum Beispiel der Zusammenhang zwischen der Neigung der Leeböschung und dem Vorhandensein oder Fehlen einer intermittierenden oder permanenten Strömungsablösung noch nicht ausreichend verstanden. Außerdem haben ästuarine Dünen ein relativ flaches Tal und steile Böschungen in der Nähe des Kammes, während Flussdünen einen flachen Kamm und in der Nähe des Tals steile Böschungen haben. Die Auswirkungen dieses Unterschieds in der Dünenmorphologie auf die Strömung sind derzeit noch unbekannt. Darüber hinaus wurde der Zusammenhang zwischen einer sich in der Richtung ändernden Gezeitenströmung und der natürlichen Morphologie von Dünen, einschließlich der dreidimensionalen Variationen, noch nicht im Detail untersucht.Im Rahmen der vorgeschlagenen Studie werden mehrere Versuchsreihen in einer großen Laborrinne durchgeführt, um die Strömungseigenschaften (Geschwindigkeit und Turbulenz) über an Ästuardünen angelehnten Modelldünen aus Beton zu charakterisieren. Basierend auf Feldmessungen von Bodenformen in der Weser werden drei Dünenformvarianten untersucht: Steilgeböschte asymmetrische Dünen, flachgeböschte asymmetrische Dünen und flachgeböschte symmetrische Dünen. Darüber hinaus werden hochauflösende numerische Simulationen der Strömung über dreidimensionalen Bodenformfeldern die Rinnenexperimente ergänzen. Mithilfe der Modellsimulationen ist es möglich, die Geschwindigkeitsstrukturen der Gezeitenströmung und die Turbulenzstrukturen über natürlichen, in der Weser vorkommenden Dünenfeldern zu bestimmen. Die Ergebnisse dieses Projekts tragen zu einem besseren Verständnis der komplexen Wechselwirkungen zwischen ästuarinen Dünen und der Gezeitenströmung bei und erlauben eine bessere Parametrisierung der kleinräumigen Prozesse in großräumigen hydro- und morphodynamischen Modellen.
Recent and predicted increases in extremely dry and hot summers emphasise the need for silvicultural approaches to increase the drought tolerance of existing forests in the short-term, before adaptation through species changes may be possible. We aim to investigate whether resistance during droughts, as well as the recovery following drought events (resilience), can be increased by allocating more growing space to individual trees through thinning. Thinning increases access of promoted trees to soil stored water, as long as this is available. However, these trees may also be disadvantaged through a higher transpirational surface, or the increased neighbourhood competition by ground vegetation. To assess whether trees with different growing space differ in drought tolerance, tree discs and cores from thinning experiments of Pinus sylvestris and Pseudotsuga menziesii stands will be used to examine transpirational stress and growth reduction during previous droughts as well as their subsequent recovery. Dendroecology and stable isotopes of carbon and oxygen in tree-rings will be used to quantify how assimilation rate and stomatal conductance were altered through thinning. The results will provide crucial information for the development of short-term silvicultural adaptation strategies to adapt forest ecosystems to climate change. In addition, this study will improve our understanding of the relationship between resistance and resilience of trees in relation to extreme stress events.
Salinity reduces the productivity of cucumber (Cucumis sativus L.) through osmotic and ionic effects. For given atmospheric conditions we hypothesize the existence of an optimal canopy structure at which water use efficiency is maximal and salt accumulation per unit of dry matter production is minimal. This canopy structure optimum can be predicted by integrating physiological processes over the canopy using a functional-structural plant model (FSPM). This model needs to represent the influence of osmotic stress on plant morphology and stomatal conductance, the accumulation of toxic ions and their dynamics in the different compartments of the system, and their toxic effects in the leaf. Experiments will be conducted to parameterize an extended cucumber FSPM. In in-silico experiments with the FSPM we attempt to identify which canopy structure could lead to maximum long-term water use efficiency with minimum ionic stress. The results from in-silico experiments will be evaluated by comparing different canopy structures in greenhouses. Finally, the FSPM will be used to investigate to which extent the improvement of individual mechanisms of salt tolerance like reduced sensitivity of stomatal conductance or leaf expansion can contribute to whole-plant salt tolerance.
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