In the last decades agricultural policy has gained increasingly in complexity. Nowadays it influences the food and agricultural sector from the global market down to the farm level. Widespread research questions, like the impact of the WTO negotiations on the farm structure, most often require comprehensive modeling frameworks. Thus, different types of models are utilized according to their comparative advantages and combined in a strategically useful way to more accurately represent micro and macro aspects of the food and agricultural sector. Consequently, in recent years we have seen an increase in the development and application of model linkages. Given this background, the overall objective of this subproject is a systematic sensitivity analysis of model linkages that gradually involves more and more characteristics of the linkage and the corresponding transfer of results between models. In addition, the project aims to answer the following specific question: How does structural change at the farm level influence aggregate supply and technical progress? Under which conditions is it possible to derive macro-relationships from micro-relationships? How does the aggregation level influence the model results and how can possible problems be overcome? This procedure is used to quantify the effects and to derive conditions for optimal interaction of the connected models. The analysis is based on the general equilibrium model GTAP (Global Trade Analysis Project) and the farm group model FARMIS (Farm Modelling Information System) which are employed in conjunction to analyze the effects of WTO negotiations on the farm level.
The decomposition of terrestrial organic material such as leaf litter represents a fundamental ecosystem function in streams that delivers energy for local and downstream food webs. Although agriculture dominates most regions in Europe and fungicides are applied widely, effects of currently used fungicides on the aquatic decomposer community and consequently the leaf decomposition rate are largely unknown. Also potential compensation of such hypothesised adverse effects due to nutrients or higher average water temperatures associated with climate change are not considered. Moreover, climate change is predicted to alter the community of aquatic decomposers and an open question is, whether this alteration impacts the leaf decomposition rate. The current projects follows a tripartite design to answer these research questions. Firstly, a field study in a vine growing region where fungicides are applied in large amounts will be conducted to whether there is a dose-response relationship between the exposure to fungicides and the leaf decomposition rate. Secondly, experiments in artificial streams with field communities will be carried out to assess potential compensatory mechanisms of nutrients and temperature for effects of fungicides. Thirdly, field experiments with communities exhibiting a gradient of taxa sensitive to climate change will be used to investigate potential climate-related effects on the leaf decomposition rate.
Three research questions of the project: 1. What global, European and Swiss climate GHG-policies will follow after 2012 and what will be their performance in the long run (up to 2050)? 2. What policies will foster mitigation in the transportation and building and real estate sectors, how can they be made acceptable and what is the role of voluntary approaches? 3. What will be the economic impacts of climate change on tourism and what are the opportunities for mitigation and adaptation?
During the first project period we developed a general approach to quantify soil pore structure based on X-ray micro-tomography Vogel et al. (2010) which is applicable at various scales to cover soil pores larger that 0.05 mm in a representative way. Based on this method we generated equivalent network models to numerically simulate flow and transport of dissolved chemicals. The existing network model was extended to handle reactive transport and infiltration processes which are especially critical for matter flux in soil. The results were compared to experimental findings. The original research question 'what does a particle see on its way through soil' could be answered quantitatively for various boundary conditions including steady state flux and infiltration. However, we identified various critical aspects of the proposed modeling concept which will be in the focus of the second period. This includes 1) the spatial arrangement of interfaces having different quality which is crucial for chemical interactions and pore scale water dynamics, 2) the realistic multiphase dynamics at the pore scale which need to reflect the dynamic pressure and movement of trapped non-wetting phase and 3) the parametrization of structural complexity which need to be developed beyond the measurement of continuous Minkowski functions to allow the development of quantitative relations between structure and function. These aspects will be explored in a joint experiments in cooperation with partners within the SPP.
Passatwindkumuli spielen eine essentielle Rolle im Strahlungshaushalt der Erde und sind verantwortlich für bis zu 20 % des tropischen Niederschlags. Noch ist nicht bekannt, wie Passatwindkumuli auf die globale Erwärmung reagieren werden. Durch Niederschlag verändern sich Wolkeneigenschaften, aber auch die Grenzschichtstruktur und -dynamik. Aufgrund der Vielzahl der beteiligten Prozesse ist die Niederschlagsentwicklung in Modellen ist unsicher. Die Konfiguration der Simulationen und Wahl der Parameterisierung, wie das Autokonversionsschema, beeinflussen Niederschlagsfluss, Wolkenstruktur und â€Ìorganisation. Bisher konnten Vergleiche mit Beobachtungen noch nicht zur Reduktion der Unsicherheit des Autokonversionsschemas beitragen. Radarreflektivität, die mit Standardmethoden aus bodengebundenen Messungen abgeleitet wird, erkennt Niederschlag erst in einem fortgeschrittenen Stadium, was es schwierig macht, die verschiedenen, den Regen verursachenden Faktoren zu entflechten. Durch die Verdunstung des Niederschlags unterhalb der Wolkenunterkante (WUK) bestimmt dieser die Stärke der Coldpools und ist so bedeutend für die Organisation von Konvektion und somit die Klimasensitivität: Daher ist es essentiell Verdunstungsraten zu bestimmen und deren räumlich-zeitliche Variabilität zu verstehen. Zwar gibt es Parameterisierungen der Verdunstung unterhalb der WUK, allerdings sind diese von der Größe der Regentropfen abhängig, welche jedoch schlecht direkt zu beobachten ist.Ziel dieses Antrages ist die Bestimmung von Faktoren, welche die Niederschlagsformation in Passatwindkumuli beeinflussen. Dazu werden neuartige Radarbeobachtungen dieser Prozesse zur genaueren Beschreibung der Niederschlagsentwicklung in Grobstruktursimulationen (LES) herangezogen. Die räumlich-zeitliche Verdunstungsverteilung wird unterhalb der WUK in den Passatwindkumuli untersucht und treibende Faktoren identifiziert. Das Forschungsvorhaben ergänzt die bevorstehende EUREC4A (A Field Campaign to Elucidate the Couplings Between Clouds, Convection and Circulation) Kampagne und nutzt die langjährige Datenreihe des Barbados Cloud Observatory (BCO).Die synergetischen bodengebundenen Beobachtungen und der neue Ansatz, Niederschlag in Wolken mit Hilfe höherer Momente des Wolkenradardopplerspektrums zu bestimmen, werden erstmalig zur Beobachtungen von Passatwindkumuli und der Charakterisierung des Niederschlagslebenszyklus zu angewendet. Damit wird es möglich die Niederschlagsentwicklung in den hochauflösenden ICON-LEM und DHARMA-LES Modellen zu evaluieren. Für einen statistischen Vergleich der Simulationen und der Beobachtungen wird der Vorwärtsoperator PAMTRA verwendet, so dass im Beobachtungsraum untersucht werden kann, inwiefern die Modelle die beobachteten, mittleren Werte und Abhängigkeiten reproduzieren können und systematischen Fehler identifiziert werden. Damit trägt das Vorhaben zum Grand Challenge on Cloud Circulation and Climate Sensitivity des Weltklimaforschungsprogramm WRCP bei.
Our long term activities aim at a functional understanding of alpine plant life. Overall our research shifted gradually from studying resource acquisition (e.g. photosynthesis) toward resource investment and questions of developement. As with treeline, sink activity seems to be the major determinant of growth. A common misconception associated with alpine plant life finds its expression in the use of the terms 'stress' and 'limitation'. See the critique in: Körner C (1998) Alpine plants: stressed or adapted? In: Press MC, Scholes JD, Barker MG (eds.) Physiological Plant Ecology. Blackwell Science , 297-311. Ongoing experimental work: The influence of photoperiod on growth and development in high elevation taxa (Ph.D. by Franziska Keller in cooperation with the Dept. of Geography, University of Fribourg). We test, whether and which species are responsive to earlier snow melt. It appears there exists a suite of different sensitivities, suggesting biodiversity shifts. We also tested the influence of nutrient addition on high elevation pioneer plants and run a longer term project on the interactive effect on sheep tramplng, nitrogen deposition and warming as part of the Swiss National Project NFP 48. A Europe-wide assessment of ground temperatures in alpine grassland is part of ALPNET (see associated organisations). The assessment provides a basis for comparing biodiversity in alpine biota from 69 to 37 degree of northern latitude. (Nagy et al. (2003) Ecological Studies, Vol. 167. 577 p. Springer, Berlin). A synthesis of research in functional ecology of alpine plants over the past 100 years was published in 1999.
Research question: Agri-environment schemes play an increasingly important role in European CAP (Common Agricultural Policy) to support biodiversity and environment in agricultural landscapes. They have been implemented since 1992 and now cost a yearly 1.7 billion Euro. Still, there is no conclusive evidence that these schemes actually do contribute to the conservation of particularly biodiversity. The primary objective of this project is to evaluate the (cost-) effectiveness of European agri-environment schemes in protecting biodiversity and to determine the primary processes that determine their effectiveness. This project furthermore aims to determine how CAP may be introduced in candidate EU-members without unacceptable loss of biodiversity. It will provide simple guidelines how researchers, governmental authorities may efficiently evaluate agri-environmental measures. Aim: Agri-environment schemes have been used to protect biodiversity and environment in agricultural areas since 1992. Their effectiveness has never been reliably evaluated. This project aims to evaluate the (cost-)effectiveness of agri-environment schemes with respect to biodiversity conservation in five European countries. It will determine the proper scales that have to be addressed for conservation efforts for a range of species groups. It will determine the most important environmental factors that influence the effectiveness of the schemes. Based on this, recommendations will be made how the effectiveness of schemes may be improved and simple guidelines will be produced how ecological effects of agri-environment schemes can be evaluated efficiently by governmental authorities or other institutions. The ecological effects of the introduction of CAP in a candidate EU-member will be investigated to reduce negative side effects of anticipated land-use changes Scientific methods: We will examine the effectiveness of agri-environment schemes by surveying pairs of fields: a field with an agri-environment scheme and a nearby field that is conventionally managed. In five countries, in each country in three areas, and in each area on seven pairs of fields the species richness of birds, plants and three insect groups (pollinators, herbivores, predators) will be determined. Effects of schemes on pollination efficiency and pest control will be examined using indicator communities. Correlative studies will examine the effects of landscape structure, land-use intensity and species pool on the effectiveness of agri-environmental measures. The spatial scale that is relevant to nature conservation efforts will be investigated via the spatial distribution of species groups. The results will be used to formulate recommendations how to improve the effectiveness of agri-environment schemes and to construct a set of simple guidelines how schemes can be evaluated efficiently yet reliably.
WMS zur Darstellung der historischen, digitalen Orthophotos der Jahre 2015 bis 2017 in Farbe (RGB), Color-Infrarot (CIR) und Graustufen (PAN). DOP sind in die Ebene entzerrte, georeferenzierte Luftbilder. Dabei erfolgt die Projektion der Luftbilder über ein Digitales Geländemodell (DGM) der Erdoberfläche. Sie besitzen eine Bodenauflösung von 0,20 m.
WMS zur Darstellung der historischen, digitalen Orthophotos der Jahre 2012 bis 2014 in Farbe (RGB). DOP sind in die Ebene entzerrte, georeferenzierte Luftbilder. Dabei erfolgt die Projektion der Luftbilder über ein Digitales Geländemodell (DGM) der Erdoberfläche. Sie besitzen eine Bodenauflösung von 0,20 m.
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.).
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