Die Hangneigung entspricht dem sogenannten Hangneigungswinkel und ist die Neigung der Geländeoberfläche gegenüber der Horizontalen entlang einer Falllinie (maximaler Neigungswinkel des Geländes). Die Karte stellt die Hangneigung in den zwei Klassen "kleiner gleich 20 Prozent" und "größer 20 Prozent" mit einer Rasterauflösung von 5 m dar. Sind mehr als 30% der Fläche eines Grünlandschlages oder eines Ackerschlages mit mehrschnittigem Feldfutterbau in der Klasse "größer 20 Prozent", ist der Schlag von den Vorgaben des § 6 Abs. 3 Satz 2 DüV, wonach flüssige organische und flüssige organisch-mineralische Düngemittel, einschließlich flüssiger Wirtschaftsdünger, mit wesentlichem Gehalt an verfügbarem Stickstoff oder Ammoniumstickstoff auf Grünland und auf Ackerflächen mit mehrschnittigem Feldfutterbau ab dem 01. Februar 2025 nur noch streifenförmig auf den Boden aufgebracht oder direkt in den Boden eingebracht werden dürfen, befreit.
Larvae of marine species with complex life cycles with wide latitudinal distribution ranges can differ not only in their thermal tolerance, but also in responses to temperature, such as growth rates and carbon or nitrogen accumulation. To assess population-specific growth rates, based on dry mass and carbon and nitrogen contents, we studied larval growth rates of the European shore crab Carcinus maenas across an environmental temperature gradient. We measured larval growth (day-1) from hatching to metamorphosis to megalopa at seven constant temperature treatments (9-27 °C, in 3 °C increments). Data represent experimental observations of larval dry mass, carbon and nitrogen contents under laboratory conditions and are reported at the level of replicates by females of each population. Replication was performed on two levels: 5 **10 larvae were reared per female, and 4 to 6 females were used per population. Larvae originated from berried females collected from populations at the southern and northern parts of the native European distribution (Vigo, Spain; Bergen and Trondheim, Norway). The data were collected during one reproductive period in 2022. Growth rates were low at low temperatures and increased with temperature, reaching a plateau at 21 °C. This increase in growth coincided with a reduction in duration of development, leading to similar body mass at metamorphosis across temperature treatments. Contrastingly, at the high temperature treatments 24°C and 27°C, reductions in duration of development did not coincide with increased growth rates, hence larvae metamorphosed with reduced body mass.
This dataset provides information on soil chemistry and soil bulk density as part of the Grassworks project, which investigates the restoration of species-rich grasslands in Germany. Grasslands are globally threatened ecosystems, and the project aims to identify factors that contribute to successful restoration, focusing on ecological complexity and stakeholder engagement. Data was collected from 187 grassland sites across three regions in North, Central, and South Germany, each with distinct socio-economic and ecological characteristics. Sampling occurred between 2022 and 2023 and included 40–41 restored grassland sites and 20–25 reference sites (10–12 positive, 10–13 negative) per region. At each site in March or early April at each vegetation plot, we took soil samples (pooled from six soil cores, 20 mm diameter) that were further pooled into one sample per site and analyzed for total soil organic carbon (SOC), total nitrogen content, pH, and soil texture as well as microbial biomass (carbon based). Additionally, soil bulk density was measured at vegetation plots per site, to enable future assessment of carbon sequestration over time. Soil and bulk density samples were taken at two depths: 0–10 and 10–30 cm.
To characterise slicks chemically and biologically, on 13th, 16th and 18th of June 2024, slicks and underlying water (depth 1m) were sampled at a total of 9 closely clustered stations in the Baltic Sea off the coast of Warnemünde, Germany. On 13.06. and 16.06. samples were taken in the evening, on the 18.06. samples were taken in the morning. On site, salinity (portable Total Dissolved Solids (TDS)-meter CO-330), water temperature (portable Total Dissolved Solids (TDS)-meter CO-330), wind speed (hand-held anemometer model MS6252A) and light intensity (Galaxy Sensors phone app v.1.10.1) were measured. Slick samples were taken with a glass plate sampler (), samples of the underlying water were taken by a syringe connected to a weighted hose. The samples were fixed as needed and analysed for dissolved organic carbon (DOC) concentration, total dissolved nitrogen (TDN) concentration, surfactant (SAS) concentration, viral particle concentration and cellular abundance of phytoplankton in different size classes (pico-, nano- and microphytoplankton). DOC and TDN concentrations were analysed by high temperature catalytic combustion, SAS concentrations by the voltametric technique with a hanging mercury drop electrode (Ćosović and Vojvodić 1998; Rickard et al. 2019). The concentrations of viral particles and phytoplankton were assessed by flowcytometry (BD Accuri C6 flow cytometer).
Four sediment cores from the Mayschoß floodplain (Ahr) were analysed for grain size, carbonates and soil organic parameters. For this purpose, the freeze-dried samples were sieved (2 mm) to remove large organic matter and the samples were separated into fine (< 2mm) and coarse (> 2 mm) fractions. For the grain size analysis, the fine fraction (< 2 mm), sieved samples (10 g) were left overnight in 35% hydrogen peroxide (H2O2). The samples were then heated to remove organic matter. In addition, the samples were dispersed by a 10 ml solution of 0.4 N sodium pyrophosphate (Na4P2O7) and ultrasonicated (45 min). The sand fraction was separated by dry sieving (classes: coarse sand: 2000 - 630 µm, medium sand: 630 - 125 µm, find sand: 200 - 125 µm and finest sand: 125 - 63 µm). X-ray granulometry (XRG, SediGraph III 5120, Micromeritics) was used to measure the fine fraction (coarse silt: 63 - 20 µm, medium silt: 20 - 6.3 µm, fine silt: 6.3 - 2.0, coarse clay: 2.0 - 0.6 µm, medium clay: 0.6 - 0.2 and fine clay < 0.2 µm). The coarse fraction was divided into two classes (2-10 mm, > 10 mm) by dry sieving. The roundness of gravels (> 10 mm) was also determined (> 10 mm rounded, > 10 mm sub-rounded, > 10 mm angular). The carbonate content of the fine fraction was determined using the Scheibler method. A pre-test is therefore carried out to determine the sample quantity. The more carbonate is contained, the smaller the required sample quantity. During the measurement, a defined amount of 10 % hydrochloric acid (HCL) is then added to the sample and the outgassing of the resulting CO2 is measured. The amount of HCL can be used to calculate the amount of dissolved calcium carbonate (CaCO3). For further geochemical analysis, the samples were pulverised and homogenised using the Retsch vibrating mill MM 200. The content of total carbon, nitrogen and sulphur of the fine fraction was analysed using the vario EL cube (Elementar). For this purpose, the ground fine soil sample was mixed with tungsten oxide (WO3) in a ratio of 1:3 and wrapped in tin foil for analysis. Due to the higher accuracy, the sulphur values of the X-ray fluorescence spectrometry (XRF) were included in the data set. The samples (8 g) were pressed into uniform pills with a carbon-based binder using a Vaneox press at 20 t for 2 min. Elemental analysis was performed in a He atmosphere using a Spectro Xepos energy dispersive XRF spectrometer. The complete XRF dataset including errors, reproducibility and security of the measurement is also available on Pangaea. Finally, the inorganic and organic carbon as well as the C/N and C/S ratios were calculated. The surface elevation was extracted from Brell et al. (2023).
The here presented data time-series are connected to the publication "Environmental parameters of shallow water habitats in the SW Baltic Sea" (Franz, M. et al. 2019b). Since 2019 a number of stations were added, and, hence, new time-series started. Every year a new dataset will be published including both, old and new stations. The following abstract is revised from Franz, M. et al. (2019b): The coastal areas of the Baltic Sea represent highly variable environments. In order to record the environmental conditions in shallow water habitats of the SW Baltic Sea, a monitoring program was established. The monitoring sites are located along the Baltic Sea coast of Schleswig-Holstein, Germany. Along the coast, 23 stations were established, where samplings for dissolved inorganic nutrient concentrations are conducted. Here, twice per month, water samples are collected in a water depth of 0.5 m. The samples are analysed for the concentration of dissolved inorganic nutrients (total oxidized nitrogen, nitrite, ammonia, phosphate and silicate) by UV/VIS spectroscopy using a continuous flow analyser (type QuAAtro 30; comp. SEAL Analytical, Hamburg, Germany. The system is equipped with a SEAL XY-2 autosampler). Quality control for nutrient measurements is ensured by certified reference material (CRM) by KANSO TECHNOS CO, LTD, Osaka, Japan. Additionally, at four shallow water stations (Booknis Eck, Bülk, Behrensdorf and Katharinenhof) temperature, salinity and dissolved oxygen are continuously logged at 2-3 m depth by self-contained data loggers. These are: (I) MiniDOT loggers (Precision Measurement Engineering; http://pme.com; ±10 µmol L-1 or ±5 % saturation) including antifouling copper option (copper plate and mesh) to measure dissolved oxygen concentration and (II) DST CT salinity & temperature loggers (Star-Oddi; http://star-oddi.com; ±1.5 mS cm-1) to record the conductivity. Both sensor types additionally record water temperature with an accuracy of ± 0.1 °C. The sampling interval was set to 30 minutes for all parameters. Another seven stations for continuous recordings of environmental parameters (again: temperature, salinity, dissolved oxygen) with the same two types of sensors were installed at 4-6 m depth in the context to the long-term monitoring project RegLocDiv (Regional-Local-Diversity) by M. Wahl (Franz, M. et al. 2019a) and included into this data set. These stations are at: Falshoeft, Booknis Eck, Schoenberg, Westermakesdorf, Staberhuk, Kellenhusen and Salzhaff (abandoned in 2023). Since 2021, in the context of implementing a reef monitoring to fulfil obligations by the EU Habitats Directive, step-by-step, eleven further stations were installed at reefs in the Schleswig-Holstein Baltic Sea. These are at: Platengrund (14 m depth) and Mittelgrund (8 m) (both since 2021), at Walkyriengrund (9 m), Brodtener Ufer (8 m), Außenschlei (11 m), Kalkgrund (8 m), Stollergrund (7.5 m) and Flueggesand (10 m) (all since 2022), as well as at Gabelsflach (10 m), Sagasbank (8.5 m) and Stabehuk (11.5 m) (all since 2023). Again, at all of these 11 stations, temperature, salinity and dissolved oxygen are continuously logged by self-contained data loggers: Conductivity (and temperature) is logged by HOBO® Salt Water Conductivity/Salinity Data Logger (Onset Computer Corporation, Bourne, MA, USA; https://www.onsetcomp.com) using the U2X protective housing to prevent fouling on the sensors. The same MiniDOT loggers (Precision Measurement Engineering) as at the above mentioned more shallow stations (including antifouling copper plate and mesh) are used to measure dissolved oxygen concentration. Dissolved oxygen concentration data measured by the MiniDOT loggers are corrected for a depth of 5 m (or 2,5 m on the shallow stations) using the software provided by the manufacturer. Additionally, a manual compensation for salinity was calculated (see details in Franz, M. et al. 2019b). Quality control was carried out by spike and gradient tests, following recommendations of SeaDataNet quality control procedures (see https://seadatanet.org/Standards/Data-Quality-Control). All data values were flagged according to applied quality checks using the following flags: 1 = Pass, 2 = Suspect, 3 = Fail, 4 = Visually suspect, 5 = Salinity compensation fail (further explanations can be found in Franz, M. et al. 2019b). The project is funded by the LfU (Landesamt für Umwelt, Schleswig-Holstein, Germany). Main responsible persons are C. Hiebenthal, C. Lieberum, F. Weinberger and R. Karez. Responsible for the nutrient analysis: N. Stärck; Responsible for taking the water samples: C. Lieberum and D. Bürger.
We analyzed concentrations of dissolved and particulate trace metals, including iron (Fe), manganese (Mn), vanadium (V), molybdenum (Mo), thallium (Tl), and rare earth elements (REE), during a mesocosm-based phytoplankton summer bloom mimicking the intertidal zone of the southern North Sea (Jade Bay). The studies aimed to identify key drivers controlling their biogeochemical cycling in dynamic, high-productivity coastal environments. Our results highlight the tidally influenced coastal zone as a critical interface that alters the behavior of supposedly conservative elements such as Mo and Tl (Mori et al., 2021) as well as natural and anthropogenic REE (incl., lanthanum, samarium, and gadolinium) (Mori et al., under review). Trace metal concentrations and shale-normalized REE patterns, determined by quadrupole inductively coupled plasma–mass spectrometry (ICP-MS) and inductively coupled plasma–optical emission spectrometry (ICP-OES), were combined with biogeochemical bulk parameters and pigment-based assessments of phytoplankton growth and community composition (Mustaffa et al., 2020). Trace metal and REE cycling were evaluated in relation to phytoplankton dynamics, particulate organic matter composition (C, N, P), dissolved organic carbon, total dissolved nitrogen, and macronutrient concentrations (nitrate, ammonium, silicate, and inorganic phosphate). The dataset was obtained during a Planktotron-based mesocosm experiment conducted within the framework of the Coastal Ocean Darkening project (Mustaffa et al., 2020).
Taken from the methods of https://doi.org/10.1016/j.agee.2020.107237: The effect of rare arable plants on soil nutrient concentration was measured by taking soil samples in the 1st and 2nd study year (March 2018 and August 2019). One soil sample per plot was taken to a 20 cm depth and analyzed by the AGROLAB Group (Landshut, Germany) for soil organic matter [%] and nitrogen concentration [%] (DIN EN 15936; 2012 and DIN EN 16168; 2012-11).
Die Hangneigung entspricht dem sogenannten Hangneigungswinkel und ist die Neigung der Geländeoberfläche gegenüber der Horizontalen entlang einer Falllinie (maximaler Neigungswinkel des Geländes). Die Karte stellt die Hangneigung in den zwei Klassen "kleiner gleich 20 Prozent" und "größer 20 Prozent" mit einer Rasterauflösung von 5 m dar. Sind mehr als 30% der Fläche eines Grünlandschlages oder eines Ackerschlages mit mehrschnittigem Feldfutterbau in der Klasse "größer 20 Prozent", ist der Schlag von den Vorgaben des § 6 Abs. 3 Satz 2 DüV, wonach flüssige organische und flüssige organisch-mineralische Düngemittel, einschließlich flüssiger Wirtschaftsdünger, mit wesentlichem Gehalt an verfügbarem Stickstoff oder Ammoniumstickstoff auf Grünland und auf Ackerflächen mit mehrschnittigem Feldfutterbau ab dem 01. Februar 2025 nur noch streifenförmig auf den Boden aufgebracht oder direkt in den Boden eingebracht werden dürfen, befreit.
Die Hangneigung entspricht dem sogenannten Hangneigungswinkel und ist die Neigung der Geländeoberfläche gegenüber der Horizontalen entlang einer Falllinie (maximaler Neigungswinkel des Geländes). Die Karte stellt die Hangneigung in den zwei Klassen "kleiner gleich 20 Prozent" und "größer 20 Prozent" mit einer Rasterauflösung von 5 m dar. Sind mehr als 30% der Fläche eines Grünlandschlages oder eines Ackerschlages mit mehrschnittigem Feldfutterbau in der Klasse "größer 20 Prozent", ist der Schlag von den Vorgaben des § 6 Abs. 3 Satz 2 DüV, wonach flüssige organische und flüssige organisch-mineralische Düngemittel, einschließlich flüssiger Wirtschaftsdünger, mit wesentlichem Gehalt an verfügbarem Stickstoff oder Ammoniumstickstoff auf Grünland und auf Ackerflächen mit mehrschnittigem Feldfutterbau ab dem 01. Februar 2025 nur noch streifenförmig auf den Boden aufgebracht oder direkt in den Boden eingebracht werden dürfen, befreit.
| Organisation | Count |
|---|---|
| Bund | 623 |
| Europa | 29 |
| Kommune | 5 |
| Land | 72 |
| Weitere | 19 |
| Wirtschaft | 3 |
| Wissenschaft | 346 |
| Zivilgesellschaft | 20 |
| Type | Count |
|---|---|
| Daten und Messstellen | 122 |
| Förderprogramm | 596 |
| Text | 28 |
| unbekannt | 25 |
| License | Count |
|---|---|
| Geschlossen | 38 |
| Offen | 728 |
| Unbekannt | 5 |
| Language | Count |
|---|---|
| Deutsch | 615 |
| Englisch | 228 |
| Resource type | Count |
|---|---|
| Archiv | 48 |
| Bild | 6 |
| Datei | 85 |
| Dokument | 20 |
| Keine | 500 |
| Unbekannt | 1 |
| Webdienst | 2 |
| Webseite | 156 |
| Topic | Count |
|---|---|
| Boden | 590 |
| Lebewesen und Lebensräume | 738 |
| Luft | 496 |
| Mensch und Umwelt | 771 |
| Wasser | 574 |
| Weitere | 763 |