Im Mittelpunkt der Arbeit der Fachberatungsstellen steht die Beratung für von sexualisierter Gewalt betroffene Kinder und Jugendliche sowie für junge Erwachsene, die in ihrer Kindheit und Jugend sexualisierte Gewalt erlebt haben. Beratungen werden auch für Bezugspersonen und Fachkräfte angeboten. Die Beratungen sind kostenlos, vertraulich, anonym und freiwillig. Neben Beratungen leisten die Fachberatungsstellen auch Präventionsarbeit sowie Vernetzungs- und Öffentlichkeitsarbeit. Die Fachberatungsstellen werden gem. §§ 11 Abs. 3 Nr. 6, 8 Abs. 3, 8b und 16 des SGB VIII (Kinder- und Jugendhilfe) tätig. Durch die Beratung und Begleitung durch die Fachberatungsstellen haben die Betroffenen die Möglichkeit, über die erlebte sexuelle Gewalt zu sprechen und die Gewalterfahrungen zu verarbeiten und so eine Stabilisierung zu erfahren. Sie bieten Unterstützung dabei Ängste und psychosomatische Beschwerden zu überwinden und dienen dem Abbau der durch sexualisierte Gewalt hervorgerufenen Entwicklungsstörungen und Verhaltensweisen. Bezugspersonen betroffener Kinder und Jugendlicher werden bei der Bewältigung von Erziehungs- und Beziehungsproblemen mit betroffenen Kindern und Jugendlichen unterstützt, sodass auch diese die Kinder und Jugendlichen gut unterstützen können. Fachkräfte, Auszubildende und Ehrenamtliche im Kinder- und Jugendbereich werden durch fachliche Beratung in die Lage versetzt, in ihrem jeweiligen Arbeitsfeld präventiv tätig zu werden und z. B. bei Verdachtsmomenten im Einzelfall weitere Schritte zu planen und kompetente Ansprechpartnerinnen für betroffene Kinder und Jugendliche zu sein. Die Arbeit des Kinderschutzzentrums ist auf die Vorbeugung jeder familialen Gewalt – Kindesvernachlässigung, körperlicher und psychischer Gewalt sowie sexueller Gewalt gegen Kinder – sowie auf die Linderung der Folgen von dieser gerichtet. Dazu wird die Eltern-Kind-Beziehung gestärkt und Mütter, Väter sowie Kinder können Kompetenzen entwickeln, mit Konflikten konstruktiv umzugehen und ohne Gewaltanwendung miteinander zu kommunizieren. Auch Personen aus dem Umfeld von Gewalt betroffenen Familien und Fachkräfte, die Kinder und ihre Familien betreuen, erhalten Beratung und Unterstützung im Kinderschutzzentrum. Zudem wird die (fachliche) Öffentlichkeit über die Hintergründe von Gewalt gegen Kinder, über Präventions- und Hilfsmöglichkeiten für Eltern und Kinder aufgeklärt. Die Arbeit findet auf Grundlage der §§ 11 Abs. 3 Nr. 6, 8 Abs. 3, 8a, 8b, 16 des SGB VIII und § 4 KKG statt.
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Das Projekt "B 5.1: Fate of agrochemicals in integrated farming systems in Son-La province, Northern Vietnam" wird vom Umweltbundesamt gefördert und von Universität Hohenheim, Institut für Bodenkunde und Standortslehre, Fachgebiet Biogeophysik durchgeführt. In Son La province, Northern Vietnam, many irrigated farming systems include ponds in which small-scale farmers raise fish to produce additional food and income. The main field crops in this area are paddy rice and maize. Often, irrigation water is first used in paddy fields, before it flows to the fishponds. Because farmers regularly apply considerable amounts of agrochemicals, mainly insecticides, to field crops fish production suffers. Moreover, agrochemicals may enter the human food chain. Subproject B5.1 will study the fate of agrochemicals applied in two subcatchments near Yen Chau, Son La province. Investigations will be carried out in close collaboration with A1.3, B4.1, C4.1, D5.2, and G1.2. In the two subcatchments, fishponds have been investigated by D5.1 since 2003. We will carry out a survey of the subcatchments with special emphasis on the water distribution systems (fields, ponds, canals, brooks). The data will be linked to the GIS (Geographical Information System) set up by B4.1. In one subcatchment, B5.1 will install a weather station as well as five TDR (time do-main reflectometry) probes and tensiometers. Water flow through the system will be recorded by means of water meters and V-shaped (Thompson) weirs equipped with automatic pressure sensors. Soil and water samples from selected fields sites, pond inflows, and ponds will be regularly screened for agrochemicals using the procedure developed by B2.1 (Ciglasch et al., 2005; see below). Soil and sediment characteristics that determine water regime and soil-agrochemical interaction, e.g. texture, organic carbon content, hydraulic conductivity, partitioning coefficients, and half-life times will be measured in laboratory and field experiments in cooperation with B4.1. In preparation for the next phase, discharge will be assessed and agrochemical concentrations monitored in the main catchment.
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.
Das Projekt "Effect of weed management strategies on the risk of enteric pathogen transfer into the food chain and lettuce yield and quality" wird vom Umweltbundesamt gefördert und von Universität Bonn, Institut für Organischen Landbau durchgeführt. The risk of pathogen transfer from soil to plant, here: lactuca sativa var. capitata, under organic farming conditions is to be investigated within the scope of the QLIF project. When brute fertilisers are applied during production, a health risk by consuming raw eadibles, as e.g. lettuce, is often discussed because of the demanding high standard of sanitation. The type of fertiliser might promote transfer of Enterobacteriaceae, and among these possibly human pathogens. Splash-effects during rainfall and irrigation as well as transfer of soil particles during mechanical weed control. Risks of the pathogen transfer into lettuce will be examined by use of different fertilisation and weed control management strategies, the latter being compared regarding their effectiveness in reducing pathogen transfer. Different field trials with organic fertilisation will be performed in 2006 and 2007. The contents of Enterobacteriaceae, coliforms and E. coli are used as sanitation indicators for the assessment of the effectivity of weed control strategies. Therefore, the contents will be measured in soil as well as in plants. Furthermore, the quality of lettuce will be acquired by analyses of nutrient composition and morphological measurements.
Das Projekt "Grey water treatment in upflow anaerobic sludge blanket (UASB) reactor" wird vom Umweltbundesamt gefördert und von Technische Universität Hamburg-Harburg, Institut für Abwasserwirtschaft und Gewässerschutz B-2 durchgeführt. In ecological sanitation, the wastewater is considered not only as a pollutant, but also as a resource for fertiliser, water and energy and for closing water and nutrients cycles (Otterpohl et. al., 1999; Otterpohl et. al., 2003; Elmitwalli et al. 2005). The ecological sanitation based on separation between grey and black water (and even between faeces and urine), is considered a visible future solution for wastewater collection and treatment. Grey water, which symbolises the wastewater generated in the household excluding toilet wastewater (black water), represents the major volume of the domestic wastewater (60- 75 percent) with low content of nutrients and pathogens (Otterpohl et. al., 1999; Jefferson et al., 1999; Eriksson et al., 2002). Most of grey-water treatment plants include one or two-step septic-tank for pre-treatment (Otterpohl et al., 2003). The grey-water treatment needs both physical and biological processes for removal of particles, dissolved organic-matters and pathogens (Jefferson et al., 1999). Recently, many researchers have studied the grey-water treatment either by application of high-rate aerobic systems, like rotating biological contactor (Nolde, 1999), fluidised bed (Nolde, 1999), aerobic filter (Jefferson et al., 2000), membrane bioreactor (Jefferson et al., 2000), or by application of low-rate systems, like slow sand filter (Jefferson et al., 1999), vertical flow wetlands (Otterpohl et. al., 2003). Although high-rate anaerobic systems, which are low-cost systems, have both physical and biological removal, no research has been done until now on grey water in these systems. The grey water contains a significant amount (41 percent) of chemical oxygen demand (COD) in the domestic wastewater (Otterpohl et al., 2003) and this amount can be removed by the highrate anaerobic systems. Although high-rate anaerobic systems have been successfully operated in tropical regions for domestic wastewater treatment, the process up till now is not applied in lowtemperature regions. The COD removal is limited for domestic wastewater treatment in high-rate anaerobic systems at low temperatures and, therefore, a long HRT is needed for providing sufficient hydrolysis of particulate organic (Zeeman and Lettinga, 1999; Elmitwalli et al. 2002). The grey water has a relatively higher temperature (18-38 degree C), as compared to the domestic wastewater (Eriksson et al. 2002), because the grey water originates from hot water sources, like shower (29 degree C), kitchen (27-38 degree C) and laundry (28-32 degree C). Therefore, high-rate anaerobic systems might run efficiently for on-site grey water treatment, even in low-temperature regions. The upflow anaerobic sludge blanket (UASB) reactor is the most applied system for anaerobic domestic waster treatment. Accordingly, the aim of this research is to study the feasibility of application of UASB reactor for the treatment of grey water at low and controlled (30 degree C) temperatures.