Die landesweite Waldzustandserhebung wird jährlich im bundesweiten Stichprobennetz (16x16 km) und nach einer abgestimmten Methodik durchgeführt. In Thüringen wurde das Stichprobennetz auf 4x4 km verdichtet, um flächenrepräsentative Aussagen für die Hauptbaumarten zu erhalten. Ziel der Waldzustandserhebung ist die langfristige Überwachung des Waldzustandes unter dem Einfluss abiotischer Einflüsse (z.B. Klima/Witterung, Luftschadstoffe) und biotischer Faktoren (z.B. Insektenkalamitäten). Der jährliche Waldzustandsbericht für Thüringen ist unter www.tmil.info zu finden.
Der Melde-Michel stellt in der Freien und Hansestadt Hamburg einen Mängelmeldedienst für Bürger und Unternehmen im Rahmen einer Webanwendung zur Verfügung. Die Meldung von Mängeln ist ebenfalls telefonisch über den Telefonischen HamburgService (Telefonnummer 115) möglich. Hierbei werden Infrastruktur-Mängel z. B. Schlaglöcher, beschädigte Verkehrslichter, Schäden beim städtischen Grün und mehr auf einfache Weise an die jeweils zuständige Dienststelle oder das jeweils beauftragte Unternehmen übermittelt. Bei der Nutzung via Smartphone kann die Lokalisierung mittels Standortermittlung erfolgen. Zusätzlich zur auszuwählenden Schaden-Kategorie können optional weitere Informationen, z.B. Beschreibung, Kontaktdaten und Fotos mitgegeben werden.
Die Mängelmeldungen der Bürger und Unternehmen wie z.B. Schlaglöcher oder beschädigte Verkehrszeichen werden in einer Datenbank gespeichert und bereitgestellt und im Melde-Michel sichtbar dargestellt.
Der WebFeatureService (WFS) stellt die gemeldeten "Online-Anliegen" der Bürger und Unternehmen, wie z.B. Schlaglöcher oder beschädigte Verkehrslichter, im Melde-Michel dar. Zur genaueren Beschreibung der Daten und Datenverantwortung nutzen Sie bitte den Verweis zur Datensatzbeschreibung.
Das Projekt "Significance of xylem translocated sulfate in early responses of stomata to drought in poplar plants" wird vom Umweltbundesamt gefördert und von Universität Freiburg, Institut für Forstbotanik und Baumphysiologie durchgeführt. Water deficiency, sensed by the root, is supposed to be signaled via xylem transport from the root to the shoot by chemical as well as hydraulic signals. In response to these signals stomatal conductance is reduced to prevent excessive water loss. The chemical signal mostly responsible for stomatal closure in response to drought is thought to be the photohormone abscisic acid (ABA). However, the origin of the ABA involved in this process is still a matter of debate, since it can be synthesized in roots and the shoot. Recent experiments indicated that increasing sulfate con-centrations in the xylem constitute an early response to drought; therefore, it has been hypothesized that xylem-borne sulfate accelerates the ABA signal for stomatal closure and that enhanced ABA in the leaves in response to drought does not necessarily originate from synthesis in roots; acceleration of stomatal closure by sulfate is thought to be achieved by activating malate efflux channels of guard cells. To test this hypothesis, (i) mass transport of ABA and sulfate in the xylem, (ii) its sources and the sinks during drought, (iii) drought mediated regulation of expression of sulfate transporters / anion channels, and (iv) the effects of sulfate and ABA on malate efflux from isolated guard cells will be studied. Experiments will be performed with wild type and transgenic poplar lines with altered expression of sulfate transporters, enhanced sulfate use for reduction, and in ABA insensitive mutants.
Das Projekt "SP 1.2 Optimisation of soil organic matter management under intensive cropping in the North China Plain" wird vom Umweltbundesamt gefördert und von Universität Hohenheim, Institut für Kulturpflanzenwissenschaften (340), Fachgebiet Düngung und Bodenstoffhaushalt (340i) durchgeführt. Intensive maize-wheat double cropping is a common plant production system at the North China Plains. More than 600 kg N/ha as mineral N fertiliser are applied annually while only 300 to 350 kg N/ha are removed with plant products. Despite of this extraordinarily high level of N-fertilisation, the yield potential in the common wheat-maize cropping system is by far not fully taped yet. Beside low N utilization efficiencies (partly less than 30 percent), frequent lodging and environmental pollution including leaching and gaseous losses of N are the results of the excessive use of fertiliser-N. Within this study, different N-fertilisation, tillage and cropping strategies shall be investigated with their potential to maintain high levels of SOM and to guaranty high and stable yields in the long term in the North China Plain. Future developments like climate change and increasing demand for energy production from plant residues shall be considered. Special emphasis will be put on the fate of (fertilised) N which preferably should be available for plant uptake and built up of organic matter but may also disappear by leaching and gaseous losses. A combination of lab experiments, existing and newly established long term field experiments combined with computer modelling shall be used to extrapolate short and medium term findings into the future and up to a regional scale.
Das Projekt "Estimation of willingness-to-pay to reduce risks of exposure to heavy metals and cost-benefit analysis for reducing heavy metals occurence in Europe (ESPREME)" wird vom Umweltbundesamt gefördert und von Universität Stuttgart, Institut für Energiewirtschaft und Rationelle Energieanwendung durchgeführt. Heavy metals from different sources accumulate in the environment. From a policy point of view, it has been difficult to tackle the environmental problems due to heavy metals partly because the problem has been viewed from different policy domains (air, water, soils etc.). Thus, it is not guaranteed that the policy mix applied under environmental regulation is optimal. A systems analysis would be required to define the sources of heavy metals, how they are dispersed in the environment and which adverse effects they might cause on human and ecosystems health. From a policy point of view, it is also important to identify what kinds of policy responses would be most cost-effective to reduce the impacts of heavy metals. Such information is required for carrying out cost-benefit analyses of reducing the occurrence of heavy metals in our society. Identifying the benefits would include a monetary valuation of the impacts with contingent valuation (CV) approaches (e.g. assessing the willingness-to-pay, WTP). The focus of the work described will be on priority metals, which are mercury, cadmium, chrome, nickel, arsenic and lead. Core aim of the research is to carry out cost effectiveness (CEA) and cost-benefit analyses (CBA) for reducing the heavy metals occurrence, in the EU Member States and candidate countries, including damage assessment to the environment and human health in the long term following the impact pathway analysis which assesses the impacts and damages of pollutants from their emissions over their dispersion to exposure and impacts. Finally, a feasibility study will be conducted to identify the potentials, strengths and weaknesses and uncertainties of currently available macro-economic models to identify further research needs in this field.
Das Projekt "SP 1.1 A combined BaPS-13C stable isotope technique to study the interaction between C and N turnover in alkaline agricultural soils of the North China Plain" wird vom Umweltbundesamt gefördert und von Universität Hohenheim, Institut für Bodenkunde und Standortslehre, Fachgebiet Biogeophysik durchgeführt. In the intensively managed double-cropping production system of the North China Plain, the excessive use of nitrogen (N) fertilizer has resulted in adverse environmental impacts such as leaching of nitrate to shallow groundwater or gaseous losses of the greenhouse gas N2O. An understanding of N cycling in soil is essential for deriving sustainable fertilization strategies. Nitrogen transformations in soil are closely linked to the carbon (C) cycle. All heterotrophic decomposing micro organism simultaneously assimilate C and N during decomposing plant residues or soil organic matter. An understanding of this linkage is important, for example, for assessing the feedback of a changed N fertilization practice on the soil organic matter pool. To study and quantify the C and N fluxes in soil, we need a set of reliable and accurate methods. During the last decade a novel method, the Barometric Process Separation, has been used to measure gross nitrification rates in soil. Recently, it has been shown that the use of the BaPS method becomes problematic at soil pH greater than 6. At pH values above 6 the BaPS calculation is strongly affected by the CO2,aq term, i.e. the dissolution of gaseous CO2 during incubation. So far, no methods are available to accurately quantifying this term. In our study, we aim at developing a novel combined Barometric Process Separation (BaPS)-13C stable isotope technique, which allows an accurate quantification of the CO2,aq term. In parallel, we will study to which extent the incorporation of plant residues of different quality immobilises surplus soil nitrate and its potential to reduce nitrate leaching in soils with a nitrate-dominated mineral N pool. Moreover, we will study the mid- and short term interaction of C and N turnover at the process-level to get a better understanding on the feedback mechanism between both matter cycles.
Das Projekt "B 2.3: Transport of agrochemicals in a watershed in Northern Thailand - Phase 3" wird vom Umweltbundesamt gefördert und von Universität Hohenheim, Institut für Bodenkunde und Standortslehre, Fachgebiet Biogeophysik durchgeführt. Land use changes of the last decades in the mountainous regions of Northern Thailand have been accompanied by an increased input of agrochemicals, which might be transferred to rivers by surface and/or subsurface flow. Where the river water is used for household consumption, irrigation and other purposes, agrochemical losses pose a serious risk to the environment and food safety. In the first and the second phase, subproject B2 collected data on and gained knowledge of the vertical and lateral transport processes that govern the environmental fate of selected agrochemicals at the plot and the hillslope scale (Ciglasch et al., 2005; Kahl et al., 2006). In the third phase, B2.3 will turn from the hillslope to the watershed scale. For simulation of water flow and pesticide transport the SWAT model (Neitsch et al., 2002b) will be adapted and used. The study area will be the Mae Sa watershed (138 km2), which includes the Mae Sa Noi subcatchment where B2 carried out detailed investigations during the last two phases. The specific focus of the subproject will be the parameterization and calibration of the SWAT model and its integration into the model network of the SFB. The SFB database has been established and can be used for model parameterization. In addition, high-quality geo-data are available from the Geoinformatic and Space Technology Development Agency (GISTDA) in Chiang Mai. For model calibration, discharge measurements are available for the Mae Sa Noi subcatchment (12 km2) and for the neighboring Mae Nai subcatchment (18 km2). To collect data on the Mae Sa watershed discharge, at the very beginning of the third phase gauging stations will be established in a midstream position and at the outlet of the watershed. Pesticide fluxes will be measured at each gauging station as well as in the Mae Sa Noi subcatchment, where B2.2 has operated two flumes equipped with automatic discharge-proportional water samplers since 2004. Rainfall distribution and intensity will be monitored with a net of automatic rain gauges. Hydrograph separation will be performed using soil and river temperatures (Kobayashi et al., 1999). Within the watershed temperature loggers will be installed at different soil depths to measure the temperature of the different discharge components. Already at the beginning of the second year of the third phase we will start to couple the SWAT model with land use and farm household models of the SFB and to use the model to assess the effect of land use and land management changes on the loss of pesticides to surface waters.
Das Projekt "Element cycles in mountain regions under various land use" wird vom Umweltbundesamt gefördert und von Universität Bayreuth, Fachgruppe Geowissenschaften, Bayreuther Zentrum für Ökologie und Umweltforschung (BayCEER), Lehrstuhl für Agrarökosystemforschung durchgeführt. Research question: What is the role of agricultural land use in changes of nutrient cycles and losses dependingon surface slope and climate? Approach: Annual balance of main nutrients for 3-4 main agricultural farms based on fertilizer input, partitioning of nutrients in above and below ground plant parts, output with harvest, losses with DOM and erosion (in collaboration with other TP). The balances will be done depending on agricultural practices in Eger and Haean Catchment and will be compared with adjacent grassland and forest. Obtained element cycles will be upscaled from farm area to the level of both catchments basins depending on specific land use, surface slope and climate. Research question: Can we reconstruct previous erosion and nutrient losses and separate them under forest and under agricultural use? Approach: Undisturbed sediment cores (7 for Eger and 7 for Haean) will be taken from the lakes and soils of landscapes subordinated to agricultural fields. Three radiocarbon data of wood particles at increasing depth for each sediment core will be used as references. The age of the bottom sediment layer should be less than 1000 years. The total content of C, N, P, K, Mg, Ca, Si will be analyzed in individual laminae or sediment layers. Conclusions will be drawn based on the thickness of the laminae, their elements content and the ratio between nutrients and Si. The conclusions will be proven by 13C (vegetation change) and 15N (N input by fertilizers) of individual laminae. Research question: What are the best management practices for sloping uplands? Approach: Measured element cycles and losses under various agriculture practice will be analysed and practices with the least nutrient losses and erosion will be selected. The best management practices for landscapes with different slopes will be elaborated.
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