Der Kartendienst stellt die Standorte der öffentlichen Landesverwaltung und der Kommunen dar.:Bibliotheken im Saarland (Quelle: Ministerium für Bildung und Kultur, Stand 06/2025).
Der Kartendienst (WFS-Gruppe) stellt die Standorte der öffentlichen Landesverwaltung und der Kommunen dar.:Bibliotheken im Saarland
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.
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.
Magnetic resonance tomography (MRT) on microcosm soil cores (200 mm Ø) used for CeMiX, comprising naturally stacked subsoil down to 700 mm plus topsoil from CeFiT, will be implemented at a laterally partially open Split 1.5 T magnet, with intended final in-plane spatial resolution of 200 Micro m. Three-dimensional biopore distributions and dynamics of their formation within the cores will be determined non-invasively and compared to complementing CT analyses of SP 2. One major aim is a non-invasive differentiation of the biopores into earthworm- and root system-originating ones and currently air-, water-, root- and earthwormfilled ones, based on NMR relaxation parameters. Attempts will additionally be made to classify different wall coatings of the biopores with regard to their water affinity. Dynamics of water distribution within the microcosm core and its biopore structures, starting from initial values taken from CeFiT (SP 3), will be documented with an in-plane resolution of 5 mm, in parallel to measurements of root growth dynamics for calculation of biomass and root surface area. Special emphasis will be put on the role of the plant root system for a re-distribution of water/D2O (and solutes) between different soil layers. Finally we will attempt MRT-controlled sample collection from the microcosm cores, to get - together with our research unit partners of SPs 4-8 - repeated access to minimally invasively acquired data on nutrient and microorganism distributions in concert with non-invasively collected water and root distribution data as a basis for dynamic modelling of water and solute circuits in SP 10. Beside the microcosm cores, flat rhizotrons as used in SP 3 will be employed to enable measurements of root and shoot hydrostatic pressure profiles with pressure probes, in addition to MRT measurements. In this way water distributions and corresponding driving forces and growth dynamics will be measured altogether in a minimally invasive manner.
In freshwater sediments, iron oxidation is dominated by phototrophic and chemotrophic (aerobic and nitrate-reducing) Fe(ll)-oxidizing microorganisms. Although these biogeochemical processes have been investigated in detail in laboratory studies, not much is known about their spatial distribution, interactions (e.g. competition) amongst each other, as well as their response towards environmental perturbations (i.e. temperature, geochemical variations (nutrient, organic matter input)). This research proposal aims to investigate the activity, abundance and resource competition between different chemotrophic (aerobic and (autotrophic/mixotrophic) anaerobic nitrate-reducing) and phototrophic ironoxidizing microorganisms. In order to better understand the spatial distribution of nitrate-reducing iron oxidizing bacteria, microbial nitrate-producing and competing, nitrate-depletion processes will also be studied throughout the sedimentary redox gradient. In addition, the activity and abundance of the ironoxidizing processes will be quantified with (geo)microbiological, molecular and novel spectral imaging techniques. Using high resolution geochemical measurements (microsensors) we will characterize the environmental conditions these bacteria experience in order to determine the role of spatial and functional niche competition in microbial iron oxidation and the interconnection to the N-cycle. Iron mineral formation will be investigated as a function of the microbial spatial and temporal activity, depending on environmental perturbations. The proposed research study will strongly improve the understanding of iron cycling, the interconnection to the N-cycle, as well as interactions and competition between phototrophic and chemotrophic metabolisms in aquatic environments.
Organische Aerosole (OA) sind wichtige Bestandteile atmosphärischer Partikel. Je nach Region können sie zwischen 20 und 90% der gesamten Submikron-Partikelmasse betragen. Dennoch sind organische Aerosolquellen, atmosphärische Prozesse und Ableitung sehr ungewiss. Vorrangiges Ziel dieses Antrages ist es, die Auswirkungen organischer Aerosole auf Luftqualität und Klima zu untersuchen. Dazu soll die Darstellung des Aerosolaufbaus und die Weiterentwicklung in einem globalen Klima-Chemie-Modell verbessert werden. Das geplante Vorhaben basiert auf einem rechnerisch effizienten Modul zur Beschreibung der Zusammensetzung und Entwicklung atmosphärischer Aerosole in der Atmosphäre (ORACLE), ein Teil des ECHAM5/MESSy (EMAC) Klima-Chemie-Modells. ORACLE wird unter Berücksichtigung aller auf Labor- und Feldmessungen basierenden neuesten Erkenntnissen und Entwicklungen aktualisiert werden, um den zunehmend oxidierenden, weniger flüchtigen und stärker hygroskopischen Charakter des organischen Aerosols während der atmosphärischen Alterung mittels Nachverfolgung ihrer beiden wichtigsten Parameter, Sättigungskonzentration und Sauerstoffgehalt, genauer darzustellen. Dieses Modellsystem soll eingesetzt werden, um die Unsicherheit hinsichtlich der Einflüsse organischer Aerosole auf die globale Luftqualität und den Strahlungsantrieb zu verringern, und zwar durch: i) Quantifizierung des relativen Beitrags der Bildung sekundärer organischer Aerosole (SOA) sowie Emissionen primärer organischer Aerosole (POA) auf den Gesamthaushalt organischer Aerosole in unterschiedlichen Umgebungen; ii) Quantifizierung des Beitrags von Biomasseverbrennung und Schadstoffemissionen sowie chemische Alterung und weiträumige Übertragung auf den Gesamthaushalt organischer Aerosole; iii) Ermittlung, inwieweit SOA Konzentrationen durch biogene und anthropogene Emissionen sowie photochemische Alterungsprozesse beeinträchtigt werden; iv) Untersuchung der Weiterentwicklung von SOA-Bildung aus natürlichen Quellen durch deren Interaktion mit anthropogenen Emissionen; v) Abschätzung der Auswirkungen photochemischer Alterungsprozesse auf die physikalisch-chemischen Eigenschaften organischer Aerosole (z.B. Hygroskopizität, Volatilität) und vi) Einschätzung der indirekten Auswirkungen organischer Aerosole auf das Klima. Vor allem aber wird der vorliegende Antrag der kommenden Generation von Chemie-Klimamodellen eine realistische Beschreibung der chemischen Entwicklung organischer Aerosole in der Atmosphäre liefern, was für die Reduzierung der Aerosol-Unsicherheiten in der Luftqualität und bei Klimasimulationen von wesentlicher Bedeutung ist. Es ist auch davon auszugehen, dass das Forschungsvorhaben wertvolle Informationen zu den Quellen und der Produktion von OA weltweit liefert, was derzeitige CCMs nicht leisten können und welche von Politikern zur Entwicklung zukünftiger wirksamer Emissionsminderungsstrategien genutzt werden können.
| Organisation | Count |
|---|---|
| Bund | 342 |
| Europa | 37 |
| Kommune | 32 |
| Land | 53 |
| Wirtschaft | 2 |
| Wissenschaft | 113 |
| Zivilgesellschaft | 154 |
| Type | Count |
|---|---|
| Daten und Messstellen | 1 |
| Förderprogramm | 324 |
| Repositorium | 3 |
| Text | 5 |
| unbekannt | 56 |
| License | Count |
|---|---|
| Geschlossen | 9 |
| Offen | 362 |
| Unbekannt | 18 |
| Language | Count |
|---|---|
| Deutsch | 265 |
| Englisch | 162 |
| Resource type | Count |
|---|---|
| Bild | 1 |
| Datei | 10 |
| Dokument | 4 |
| Keine | 306 |
| Unbekannt | 2 |
| Webdienst | 9 |
| Webseite | 69 |
| Topic | Count |
|---|---|
| Boden | 168 |
| Lebewesen und Lebensräume | 295 |
| Luft | 146 |
| Mensch und Umwelt | 389 |
| Wasser | 137 |
| Weitere | 383 |