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For her own habilitation Monika Wulf investigated 232 plots (vegetation releves) in 63 mixed broadleaf forests from 1996 to 1999. The 232 plots (100-400 m2) represent alder-ash dominated stands on wet and moist sites, oak-hornbeam forests on fresh soils, and beech dominated forests on moderately fresh soils. In each plot the abundance of all vascular plants per stratum (first and second tree layer, shrub and herb layer) was estimated using the scale of Barkman. Bryophytes were noted as presence/absence data. The location of each plot was drawn in topographical maps at scale 1:25,000 with an average deviance of 100-200 m. Additionally sketches with positions of the main tree and shrub species within the plot and at the plot boundaries were drawn. It is planned for 2010 or latest 2011 to relocate plots exactly and fixing their positions by means of GPS. In a selected number of 151 plots from 55 forests soil samples were taken at three different horizons (0-5 cm, 5-10 cm, and 10-20 cm). At each plot 10 sub-samples were taken with a soil auger of 5 cm diameter, and were mixed separately for the three horizons to one sample. The soil samples were used to estimate the pH using a CaCl2-standard solution, and to determine the amount of the plant available cations Ca, K, Mg and P using an ammoniumacetate-solution. Determination of the cation concentrations were made with a spectral photometer and an atom-absorptionsspectrometer (AAS), respectively. For at least 80% of all plots site nutrient and moisture regime as well as humus nutrient and moisture regime were compiled from maps of the forest site inventories of the 1950s and 1960s. This report describes the available content in the vegetation Database Temperate Deciduous Forests of the Prignitz Region (GIVD ID EU-DE-006).

Monika Wulf investigated 499 plots (vegetation releves) in 66 mixed broadleaf forests from 1992 to 2007. The 499 plots (100–400 m2) represent alder-ash dominated stands on wet and moist sites, oak-hornbeam forests on fresh soils, beech dominated forests on (moderately) fresh soils and some mixed deciduous-coniferous forests. In each plot the abundance of all vascular plants per stratum (first and second tree layer, shrub and herb layer) was estimated using the Barkman scale. Bryophytes were noted as presence/absence data, but not on all plots. The location of each plot was drawn in topographical maps at scale 1:25,000 with an average deviance of 100-200 m. Additionally sketches with positions of the main tree and shrub species within the plot and at the plot boundaries were drawn. For 157 plots exact positions were recorded by means of GPS with an average deviance of 5 -10 m. It is planned to do this also for about 150 plots in 2010 or 2011. In a selected number of 180 plots from 31 forests soil samples were taken at three different horizons (0-5 cm, 5-10 cm, and 10-20 cm). At each plot 10 sub-samples were taken with a soil auger of 5 cm diameter, and were mixed separately for the three horizons to one sample. The soil samples were used to estimate the pH using a CaCl2-standard solution, and to determine the amount of the plant available cations Ca, K, Mg and P using an ammonium-acetatesolution. Determination of the cation concentrations were made with a spectral photometer and an atom-absorptions-spectrometer (AAS), respectively. For at least 50% of all plots site nutrient and moisture regime as well as humus nutrient and moisture regime were compiled from maps of the forest site inventories of the 1950s and 1960s. This report describes the available content in the Database Temperate Deciduous Forests of the Uckermark Region (GIVD ID EU-DE-007).

For her own PhD, Monika Wulf investigated 415 plots (vegetation releves) in 77 mixed broadleaf forests from 1986 to 1989. The 415 plots (100-400 m2) represent alder forests on wet soils, ash dominated stands on wet, moist and moderately moist sites, oak-hornbeam forests on fresh soils, and beech dominated forests on moderately fresh soils. In each plot the abundance of all vascular plants per stratum (first and second tree layer, shrub and herb layer) was estimated using the scale of Barkman. Bryophytes were noted as presence/absence data. The latitude and the longitude of maps at scale 1:25,000 (exact coordinates with an average deviance of 1020 m) were determined for each plot. Additionally, locations of the plots were drawn on maps at scale 1:10,000 and sketches with positions of the main tree and shrub species within the plot and at the plot boundaries were drawn. In a selected number of 127 plots from 30 forests soil samples were taken at three different horizons (0-5 cm, 5-10 cm, and 10-20 cm). At each plot 10 sub-samples were taken with a soil auger of 5 cm diameter, and were mixed separately for the three horizons to one sample. The soil samples were used to estimate the pH using a CaCl2-standard solution, and to determine the amount of the plant available cations Ca, K, Mg and P using an ammonium-acetate-solution. Determination of the cation concentrations were made with a spectral photometer and an atomabsorptions-spectrometer (AAS), respectively. In 2007 and 2008 nearly all plots (380 of 415) have been exactly relocated and their positions were fixed by means of GPS. They can, together with the manual sketches, be easily relocated in the future. The purpose for relocation was to detect changes in the herb layer after 20 years. To test hypothesis of biotic homogenization at the regional level a subset of 175 independent plots were investigated by Tobias Naaf in 2008 and 2009 to carry out his PhD. These studies were founded by the German Research Foundation (DFG). This report describes the available content in the Database Temperate Deciduous Forests of the Elbe-Weser Region (GIVD ID EU-DE-005).