In the Earth, the dynamo action is strongly linked to core freezing. There is a solid inner core, the growth of which provides a buoyancy flux that drives the dynamo. The buoyancy in this case derives from a difference in composition between the solid inner core and the fluid outer core. In planetary bodies smaller than the Earth, however, this core differentiation process may differ - Fe may precipitate at the core-mantle boundary (CMB) rather than in the center and may fall as iron snow and initially remelt with greater depth. A chemical stable sedimentation zone develops that comprises with time the entire core - at that time a solid inner core starts to grow. The dynamics of this system is not well understood and also whether it can generate a magnetic field or not. The Jovian moon Ganymede, which shows a present-day magnetic dipole field, is a candidate for which such a scenario has been suggested. We plan to study this Fe-snow regime with both a numerical and experimental approach. In the numerical study, we use a 2D/3D thermo-chemical convection model that considers crystallization and sinking of iron crystals together with the dynamics of the liquid core phase (for the 3D case the influence of the rotation of the Fe snow process is further studied).The numerical calculations will be complemented by two series of experiments: (1) investigations in metal alloys by means of X-ray radioscopy, and (2) measurements in transparent analogues by optical techniques. The experiments will examine typical features of the iron snow regime. On the one hand they will serve as a tool to validate the numerical approach and on the other hand they will yield important insight into sub-processes of the iron snow regime, which cannot be accessed within the numerical approach due to their complexity.
In soils and sediments there is a strong coupling between local biogeochemical processes and the distribution of water, electron acceptors, acids, nutrients and pollutants. Both sides are closely related and affect each other from small scale to larger scale. Soil structures such as aggregates, roots, layers, macropores and wettability differences occurring in natural soils enhance the patchiness of these distributions. At the same time the spatial distribution and temporal dynamics of these important parameters is difficult to access. By applying non-destructive measurements it is possible to overcome these limitations. Our non-invasive fluorescence imaging technique can directly quantity distribution and changes of oxygen and pH. Similarly, the water content distribution can be visualized in situ also by optical imaging, but more precisely by neutron radiography. By applying a combined approach we will clarify the formation and architecture of interfaces induces by oxygen consumption, pH changes and water distribution. We will map and model the effects of microbial and plant root respiration for restricted oxygen supply due to locally high water saturation, in natural as well as artificial soils. Further aspects will be biologically induced pH changes, influence on fate of chemicals, and oxygen delivery from trapped gas phase.
The biogeochemical interface (BGI) in this project is defined as the organo-mineral surface of soil particles colonized by microorganisms. In the preceding project it was demonstrated that the different soil particle size fractions were associated with specifically structured microbial communities, a characteristic amount of soil organic carbon, and a specific capacity for adsorption of the organic chemicals phenol and 2,4-dichlorophenol, respectively. While the diversity of the microbial community was responsive to fertilization-determined additional organic soil carbon in the larger particle size fractions, it was unaffected in clay. Stable isotope probing with 13C-labelled phenol and 2,4-dichlorophenol revealed that the soil organic carbon in the BGIs also affected the diversity of microorganisms involved in the degradation of these chemicals. All these results are yet only based on studying one soil with three organic carbon variants (Bad Lauchstädt) and only two organic compounds. The objective of this 2nd phase project is to apply the innovative technology developed in the 1st phase for studying the BGI processes with soil organic carbon variants from another soil (Ultuna, SPP 1315 site) and with the chiralic anilide Fungicide metalaxyl as an additional compound. This 2nd phase SPP 1315 project will also, in a collaborative effort with two other SPP 1315 partners, investigate (1) the importance of BGIs for the entantio-selective degradation of metalaxyl and (2) the role of soil microorganisms in the formation of bound residues, respectively. Furthermore, the project will utilize stable isotope probing and next-generation DNA sequencing to link the structural and functional diversity of the microbial communities responsible for metabolism of organic chemicals in the different BGIs determined by particle size fractions and soil organic carbon variants.
Irrigation in the Yanqi Basin, Sinkiang, China has led to water table rise and soil salination. A model is used to assess management options. These include more irrigation with groundwater, water saving irrigation techniques and others. The model relies on input data from remote sensing.The Yanqi Basin is located in the north-western Chinese province of Xinjiang.This agriculturally highly productive region is heavily irrigated with water drawn from the Kaidu River. The Kaidu River itself is mainly fed by snow and glacier melt from the Tian Mountain surrounding the basin. A very poor drainage system and an overexploitation of surface water have lead to a series of environmental problems: 1. Seepage water under irrigated fields has raised the groundwater table during the last years, causing strongly increased groundwater evaporation. The salt dissolved in the groundwater accumulates at the soil surface as the groundwater evaporates. This soil salinization leads to degradation of vegetation as well as to a loss of arable farmland. 2. The runoff from the Bostan Lake to the downstream Corridor is limited since large amount of water is used for irrigation in the Yanqi Basin. Nowadays, the runoff is maintained by pumping water from the lake to the river. The environmental and ecological system is facing a serious threat.In order to improve the situation in the Yanqi Basin, a jointly funded cooperation has been set up by the Institute of Environmental Engineering, Swiss Federal Institute of Technology (ETH) , China Institute of Geological and Environmental Monitoring (CIGEM) and Xinjiang Agricultural University. The situation could in principle be improved by using groundwater for irrigation, thus lowering the groundwater table and saving unproductive evaporation. However, this is associated with higher cost as groundwater has to be pumped. The major decision variable to steer the system into a desirable state is thus the ratio of irrigation water pumped from the aquifer and irrigation water drawn from the river. The basis to evaluate the ideal ratio between river and groundwater - applied to irrigation - will be a groundwater model combined with models describing the processes of the unsaturated zone. The project will focus on the following aspects of research: (...)
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.
Der Ozean im Westpazifik ist mit Temperaturen von ganzjährig 30°C der wärmste Ozean der Welt. Im tropischen Westpazifik ist die Lufttemperatur der Grenzschicht weltweit am höchsten und die Ozonkonzentration am niedrigsten. Aufgrund der allgemeinen Advektion der Luftmassen in der unteren und mittleren Troposphäre aus dem Osten durch die Walker-Zirkulation über den Pazifik befindet sich die Luft über dem tropischen Westpazifik für längere Zeit in einer sauberen, warmen und feuchten Umgebung. Der Abbau von reaktiven Sauerstoff- und Ozonvorläufern wie NOx findet daher länger als anderswo in den Tropen, was zu sehr niedrigen Ozonkonzentrationen führte. Dies erhöht die Lebensdauer von kurzlebigen biogenen und anthropogenen Spurengasen. Darüber hinaus begünstigen hohe Meeresoberflächentemperaturen eine starke Konvektion im tropischen Westpazifik, was zu niedrigen Ozonmischungsverhältnissen in den konvektiven Ausflussgebieten in der oberen Troposphäre führen kann. Der Warmpool im Westpazifik ist auch eine wichtige Quellregion für stratosphärische Luft. Daher fallen die Region, in der die Lebensdauer kurzlebiger Spurengase erhöht ist, und die Quellregion der stratosphärischen Luft zusammen. Somit bestimmt die Zusammensetzung der troposphärischen Atmosphäre in dieser Region in hohem Maße auch die globale stratosphärische Zusammensetzung.Ozon ist aufgrund von Rückkopplungsprozessen zwischen Temperatur, Dynamik und Ozon ein wichtiges Spurengas in der Klimaforschung. Da der Warmpool im Westpazifik die Hauptquellenregion für stratosphärische Luft ist, ist die Kenntnis von Ozon und anderen kurzlebigen Spurengasen auch wichtig, um den Transport von Spurengasen in die Stratosphäre zu verstehen.Ziel unseres Projektes ist die Messung des Tagesgangs von Ozon und anderen Spurengasen mit Hilfe der hochauflösenden solaren Absorptions-FTIR-Spektroskopie. Die Messungen liefern die Gesamtsäulendichten von bis zu 20 Spurengasen. Für einige Spurengase erlaubt die Analyse der Spektrallinienform die Ableitung der Konzentrationsprofile in bis zu etwa vier atmosphärischen Höhenschichten. Ergänzt werden die Beobachtungen durch Ozonballonsondierungen, kontinuierliche Messungen der UV-Strahlung, und Modellrechnungen mit einem Chemie-Transport-Modell. Die Messungen sind für den Zeitraum August bis Oktober 2022 geplant, die Auswertung und Interpretation von November 2022 bis Januar 2023.
Die Asian Tropopause Aerosol Layer (ATAL), eine Schicht mit erhöhtem Aerosolgehalt, tritt jedes Jahr von Juni bis September in 14-18 km Höhe in einem Gebiet auf, das sich vom Mittelmeer bis zum westlichen Pazifik erstreckt. Hinsichtlich der Zusammensetzung der Partikel, sowie ihrer Bedeutung für die Strahlungsbilanz in dieser klimasensitiven Höhenregion bestehen große Unsicherheiten. Die bisher einzigen Flugzeugmessungen aus dem Zentrum der ATAL wurden 2017 im Rahmen der StratoClim Kampagne von Kathmandu aus gewonnen. Dabei entdeckten wir mit Hilfe des Infrarotspektrometers GLORIA auf dem Forschungsflugzeug Geophysica, dass feste Ammoniumnitrat (AN) â€Ì Partikel einen beträchtlichen Teil der Aerosolmasse ausmachen. Diese zählen zu den effizientesten Eiskeimen in der Atmosphäre. Zudem zeigte die gleichzeitige Messung von Ammoniakgas (NH3) durch GLORIA, dass dieses Vorläufergas durch starke Konvektion in die obere Troposphäre verfrachtet wird. Im Rahmen der PHILEAS-Kampagne schlagen wir eine gemeinsamen Betrachtung von atmosphärischen Modellsimulationen und Messungen vor, um die Zusammensetzung, Ursprung, Auswirkungen und Verbleib der ATAL-Partikel zu untersuchen â€Ì insbesondere im Hinblick auf ihre Prozessierung sowie ihren Einfluss auf die obere Troposphäre und die untere Stratosphäre der nördlichen Hemisphäre. Messungen von monsunbeeinflussten Luftmassen über dem östlichen Mittelmeer sowie über dem nördlichen Pazifik werden es uns erlauben, Luft mit gealtertem Aerosol- und Spurengasgehalt zu analysieren und damit die StratoClim-Beobachtungen aus dem Inneren des Monsuns zu komplementieren. Um dabei die wahrscheinlich geringeren Konzentrationen an Aerosol und Spurengasen zu quantifizieren, schlagen wir vor, die GLORIA-Datenerfassung von NH3 und AN u.a. durch die Verwendung neuartiger spektroskopischer Daten zu verbessern. Ferner werden wir die Analyse der GLORIA-Spektren auf Sulfataerosole sowie deren Vorläufergas SO2 auszudehnen. Auf der Modellseite werden wir das globale Wetter- und Klimamodellsystem ICON-ART weiterentwickeln, um die ATAL unter Einbeziehung verschiedener Aerosoltypen (Nitrat, Ammonium, Sulfat, organische Partikel, Staub) zu simulieren â€Ì unter Berücksichtigung der hohen Eiskeimfähigkeit von festem AN. Modellläufe werden durchgeführt, um einerseits einen globalen Überblick über die Entwicklung der ATAL 2023 zu gewinnen und zudem detaillierte, auf die relevanten Kampagnenperioden zugeschnittene, wolkenauflösende Informationen über die Aerosol-Wolken-Strahlungs-Wechselwirkungen zu erhalten. Über die direkte Analyse der PHILEAS-Kampagne hinausgehend wird diese Arbeit die Grundlage für eine verbesserte Analyse von Aerosolparametern aus GLORIA-Beobachtungen früherer und zukünftiger HALO-Kampagnen sowie aus Satellitenbeobachtungen legen. Darüber hinaus wird sie ICON-ART, einem der zentralen Klimamodellsysteme in Deutschland die Simulation von Aerosolprozessen sowie Aerosol/Wolken-Wechselwirkungen im Zusammenhang mit der ATAL ermöglichen.
Biogeochemical interfaces shape microbial community function in soil. On the other hand microbial communities influence the properties of biogeochemical interfaces. Despite the importance of this interplay, basic understanding of the role of biogeochemical interfaces for microbial performance is still missing. We postulate that biogeochemical interfaces in soil are important for the formation of functional consortia of microorganisms, which are able to shape their own microenvironment and therefore influence the properties of interfaces in soil. Furthermore biogeochemical interfaces act as genetic memory of soils, as they can store DNA from dead microbes and protect it from degradation. We propose that for the formation of functional biogeochemical interfaces microbial dispersal (e.g. along fungal networks) in response to quality and quantity of bioavailable carbon and/or water availability plays a major role, as the development of functional guilds of microbes requires energy and depends on the redox state of the habitat.To address these questions, hexadecane degradation will be studied in differently developed artificial and natural soils. To answer the question on the role of carbon quantity and quality, experiments will be performed with and without litter material at different water contents of the soil. Experiments will be performed with intact soil columns as well as soil samples where the developed interface structure has been artificially destroyed. Molecular analysis of hexadecane degrading microbial communties will be done in vitro as well as in situ. The corresponding toolbox has been successfully developed in the first phase of the priority program including methods for genome, transcriptome and proteome analysis.
During microbial turnover of organic chemicals in soil, non-extractable residues (NER) are formed frequently. Studies on NER formation usually performed with radioisotope labelled tracer compounds are limited to localisation and quantitative analyses but their chemical composition is left unknown. Recently, we could show for 2,4-dichlorophenoxyacetic acid and ibuprofen that during microbial turnover in soil nearly all NER were derived from microbial biomass, since degrading bacteria use the pollutant carbon for their biomass synthesis. Their cell debris is subsequently stabilised within soil organic matter (SOM) forming biogenic NER (bioNER). It is still unknown whether bioNER are also formed during biodegradation of other, structurally different compound classes of organic contaminants. Therefore, agricultural soil will be incubated with labelled compounds of five classes of commonly used and emerging pesticides: organophosphate, phenylurea, triazinone, benzothiadiazine and aryloxyphenoxypropionic acid. The fate of the label will be monitored in both living and non-living SOM pools and the formation of bioNER will be quantified for each compound over extended periods of time. In addition, soil samples from long-term lysimeter studies with 14C-labelled pesticide residues (e.g. triazine, benzothiazole and phenoxypropionic acid group) will be also analysed for bioNER formation. The results will be summarised to identify the metabolic conditions of microorganisms needed for bioNER formation and to develop an extended concept of risk assessment including bioNER formation in soils.
Organotin and especially butyltin compounds are used for a variety of applications, e.g. as biocides, stabilizers, catalysts and intermediates in chemical syntheses. Tributyltin (TBT) compounds exhibit the greatest toxicity of all organotins and have even been characterized as one of the most toxic groups of xenobiotics ever produced and deliberately introduced into the environment. TBT is not only used as an active biocidal compound in antifouling paints, which are designed to prevent marine and freshwater biota from settlement on ship hulls, harbour and offshore installations, but also as a biocide in wood preservatives, textiles, dispersion paints and agricultural pesticides. Additionally, it occurs as a by-product of mono- (MBT) and dibutyltin (DBT) compounds, which are used as UV stabilizer in many plastics and for other applications. Triphenyltin (TPT) compounds are also used as the active biocide in antifouling paints outside Europe and furthermore as an agricultural fungicide since the early 1960s to combat a range of fungal diseases in various crops, particularly potato blight, leaf spot and powdery mildew on sugar beet, peanuts and celery, other fungi on hop, brown rust on beans, grey moulds on onions, rice blast and coffee leaf rust. Although the use of TBT and TPT was regulated in many countries world-wide from restrictions for certain applications to a total ban, these compounds are still present in the environment. In the early 1970s the impact of TBT on nontarget organisms became apparent. Among the broad variety of malformations caused by TBT in aquatic animals, molluscs have been found to be an extremely sensitive group of invertebrates and no other pathological condition produced by TBT at relative low concentrations rivals that of the imposex phenomenon in prosobranch gastropods speaking in terms of sensitivity. TBT induces imposex in marine prosobranchs at concentrations as low as 0,5 ng TBT-Sn/L. Since 1993, for the littorinid snail Littorina littorea a second virilisation phenomenon, termed intersex, is known. In female specimens affected by intersex the pallial oviduct is transformed of towards a male morphology with a final supplanting of female organs by the corresponding male formations. Imposex and intersex are morphological alterations caused by a chronic exposure to ultra-trace concentrations of TBT. A biological effect monitoring offers the possibility to determine the degree of contamination with organotin compounds in the aquatic environment and especially in coastal waters without using any expensive analytical methods. Furthermore, the biological effect monitoring allows an assessment of the existing TBT pollution on the basis of biological effects. Such results are normally more relevant for the ecosystem than pure analytical data. usw.
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