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380-kV-Leitung Bertikow-Neuenhagen 481/482 (Uckermarkleitung) – 4. Planänderung (Änderung Kompensationsmaßnahmen LBP)

Die 50Hertz Transmission GmbH beantragte beim Landesamt für Bergbau, Geologie und Rohstoffe mit Schreiben vom 24.01.2024 die 4. Planänderung (PÄ) für die „Errichtung und den Betrieb der 380-kV-Freileitung Bertikow - Neuenhagen 481/482 (Uckermarkleitung) – sowie der damit im Zusammenhang stehenden Leitungsabschnitte“. Die 4. PÄ beinhaltet ausschließlich eine Anpassung der Kompensationsmaßnahmen aus dem landschaftspflegerischen Begleitplan (LBP). Da für das o. g. Vorhaben eine Umweltverträglichkeitsprüfung (UVP) durchgeführt wurde, ist für die 4. PÄ nach § 9 Abs. 1 Nr. 2 UVPG eine allgemeine Vorprüfung (VP) zur Feststellung der UVP-Pflicht vorzunehmen. Die UVP-VP war dafür speziell für folgende neue Ausgleichsmaßnahmen vorzunehmen: - A88: Erstaufforstung Schmölln - A89: Anpflanzen einer Baumreihe nordwestlich Gartz (Oder) - A90: Anpflanzen einer Baumreihe südlich Tantow - A91: Pflanzung von Hochstämmen westlich Serwest - A95: Pflanzung von zweireihigen Obstbaumreihen/ -alleen westlich Tuchen-Klobbicke Die übrigen im Rahmen der 4. PÄ zusätzlich geplanten Kompensationsmaßnahmen wurden bereits umgesetzt. Sie stellen entweder zertifizierte Flächenpoolmaßnahmen dar oder wurden von den zuständigen Naturschutzbehörden grundsätzlich für eine naturschutzfachliche Anerkennung als geeignete Kompensationsmaßnahmen bewertet. Da von diesen bereits umgesetzten Maßnahmen kein physischer Eingriff in die Umwelt mehr ausgeht, waren diese auch nicht Bestandteil der UVP-VP. Im Ergebnis der allgemeinen Vorprüfung stellte Das LBGR fest, dass sich aufgrund der zu erwartenden Auswirkungen des Vorhabens keine Pflicht zur Durchführung einer Umweltverträglichkeitsprüfung ergibt.

Physical oceanography during RV HEINCKE cruise HE660

Conductivity-temperature-depth profiles were measured using a Seabird SBE 911plus CTD during RV HEINCKE cruise HE660. The CTD was equipped with duplicate sensors for temperature (SBE3plus), conductivity (SBE4) and oxygen (SBE43). Additional sensors such as a WET Labs C-Star transmissometer, a WET Labs ECO-AFL fluorometer and an altimeter (PSA-916 Teledyne (Benthos)) were mounted to the CTD. Temperature, conductivity and oxygen sensors are calibrated by the manufacturer once a year before being mounted in January. They are used throughout the year and no post-cruise or in-situ calibration is applied. All other sensors are calibrated irregularly. Data were connected to the station book of the specific cruise as available in the DSHIP database. Processing of the data including removal of obvious outliers followed the procedures described in CTD Processing Logbook of RV HEINCKE (hdl:10013/epic.47427). The processing report for this dataset is linked below.

Physical oceanography during RV HEINCKE cruise HE658

Conductivity-temperature-depth profiles were measured using a Seabird SBE 911plus CTD during RV HEINCKE cruise HE658. The CTD was equipped with duplicate sensors for temperature (SBE3plus), conductivity (SBE4) and oxygen (SBE43). Additional sensors such as a WET Labs C-Star transmissometer, a WET Labs ECO-AFL fluorometer and an altimeter (PSA-916 Teledyne (Benthos)) were mounted to the CTD. Temperature, conductivity and oxygen sensors are calibrated by the manufacturer once a year before being mounted in January. They are used throughout the year and no post-cruise or in-situ calibration is applied. All other sensors are calibrated irregularly. Data were connected to the station book of the specific cruise as available in the DSHIP database. Processing of the data including removal of obvious outliers followed the procedures described in CTD Processing Logbook of RV HEINCKE (hdl:10013/epic.47427). The processing report for this dataset is linked below.

Physical oceanography during RV HEINCKE cruise HE656

Conductivity-temperature-depth profiles were measured using a Seabird SBE 911plus CTD during RV HEINCKE cruise HE656. The CTD was equipped with duplicate sensors for temperature (SBE3plus), conductivity (SBE4) and oxygen (SBE43). Additional sensors such as a WET Labs C-Star transmissometer, a WET Labs ECO-AFL fluorometer and an altimeter (PSA-916 Teledyne (Benthos)) were mounted to the CTD. Temperature, conductivity and oxygen sensors are calibrated by the manufacturer once a year before being mounted in January. They are used throughout the year and no post-cruise or in-situ calibration is applied. All other sensors are calibrated irregularly. Data were connected to the station book of the specific cruise as available in the DSHIP database. Processing of the data including removal of obvious outliers followed the procedures described in CTD Processing Logbook of RV HEINCKE (hdl:10013/epic.47427). The processing report for this dataset is linked below.

Physical oceanography during RV HEINCKE cruise HE655/2

Conductivity-temperature-depth profiles were measured using a Seabird SBE 911plus CTD during RV HEINCKE cruise HE655/2. The CTD was equipped with duplicate sensors for temperature (SBE3plus), conductivity (SBE4) and oxygen (SBE43). Additional sensors such as a WET Labs C-Star transmissometer, a WET Labs ECO-AFL fluorometer and an altimeter (PSA-916 Teledyne (Benthos)) were mounted to the CTD. Temperature, conductivity and oxygen sensors are calibrated by the manufacturer once a year before being mounted in January. They are used throughout the year and no post-cruise or in-situ calibration is applied. All other sensors are calibrated irregularly. Data were connected to the station book of the specific cruise as available in the DSHIP database. Processing of the data including removal of obvious outliers followed the procedures described in CTD Processing Logbook of RV HEINCKE (hdl:10013/epic.47427). The processing report for this dataset is linked below.

Physical oceanography during RV HEINCKE cruise HE659

Conductivity-temperature-depth profiles were measured using a Seabird SBE 911plus CTD during RV HEINCKE cruise HE659. The CTD was equipped with duplicate sensors for temperature (SBE3plus), conductivity (SBE4) and oxygen (SBE43). Additional sensors such as a WET Labs C-Star transmissometer, a WET Labs ECO-AFL fluorometer and an altimeter (PSA-916 Teledyne (Benthos)) were mounted to the CTD. Temperature, conductivity and oxygen sensors are calibrated by the manufacturer once a year before being mounted in January. They are used throughout the year and no post-cruise or in-situ calibration is applied. All other sensors are calibrated irregularly. Data were connected to the station book of the specific cruise as available in the DSHIP database. Processing of the data including removal of obvious outliers followed the procedures described in CTD Processing Logbook of RV HEINCKE (hdl:10013/epic.47427). The processing report for this dataset is linked below.

Physical oceanography during RV HEINCKE cruise HE654/1

Conductivity-temperature-depth profiles were measured using a Seabird SBE 911plus CTD during RV HEINCKE cruise HE654/1. The CTD was equipped with duplicate sensors for temperature (SBE3plus), conductivity (SBE4) and oxygen (SBE43). Additional sensors such as a WET Labs C-Star transmissometer, a WET Labs ECO-AFL fluorometer and an altimeter (PSA-916 Teledyne (Benthos)) were mounted to the CTD. Temperature, conductivity and oxygen sensors are calibrated by the manufacturer once a year before being mounted in January. They are used throughout the year and no post-cruise or in-situ calibration is applied. All other sensors are calibrated irregularly. Data were connected to the station book of the specific cruise as available in the DSHIP database. Processing of the data including removal of obvious outliers followed the procedures described in CTD Processing Logbook of RV HEINCKE (hdl:10013/epic.47427). The processing report for this dataset is linked below.

Soil- moisture and temperature from the PhytOakmeter plot DKr (Kreinitz, Germany) from 2025

As part of PhytOakmeter (www.phytoakmeter.de), time-domain transmission, soil moisture and -temperature sensors with custom-made logger systems were used to measure time series of soil state variables. The aim of these investigations was to provide data on environmental properties used in a cross-disciplinary approach. The measurement device consisted of two sensors at three different depths. The dataset contains the values of time (UTC), relative permittivity, soil moisture (in % vol) derived from permittivity and soil temperature (in °C). Determination of soil moisture was done using the formula of Topp et al. (1980). As sensors, the SMT100 soil moisture sensors with integrated temperature measurement were used. All sensors were installed within the upper 50cm below ground. The exact depths for each sensor are listed in the dataset and parameter comment.

Neubau 110-kV-Freileitung Lauchstädt-Querfurt-Reinsdorf, Anschluss Umspannwerk Querfurt im Saalekreis (Mitteldeutsche Netzgesellschaft Strom mbH)

Die Mitteldeutsche Netzgesellschaft Strom mbH (MITNETZ STROM) plant im Auftrag der envia Mitteldeutsche Energie AG zwischen dem Mast 57 der 110-kV-Freileitung Lauchstädt-Reinsdorf und dem nördlich der BAB A38 geplanten Umspannwerk (UW) Querfurt, den Neubau einer ca. 6,7 km langen 110-kV-Freileitung. Im Raum Esperstedt, nordöstlich der Stadt Querfurt, plant die MITNETZ STROM gemeinsam mit dem Übertragungsnetzbetreiber 50Hertz Transmission GmbH Berlin (50Hertz) den Neu-bau eines HöS/HS-UW als Netzverknüpfungspunkt (NVP) zum Übertragungsnetz.

Understanding the ecology and virulence of Legionella spp. populations in freshwater systems in Germany, Palestine and Israel

Bacteria of the genus Legionella cause waterborne infections resulting in severe pneumonia. In Europe, 70Prozent of the cases of the so-called Legionnaires disease (LD) originate from strains of L. pneumophila serogroup (Sg) 1, 20Prozent from other L. pneumophila serotypes and 10Prozent from other Legionella species. In contrast, in the Middle East most legionella infections are due to L. pneumophila Sg3. The overall objective of this project is to advance current knowledge on the ecology of legionella in freshwater systems, the environmental factors affecting their occurrence, virulence potential and infectivity and to understand their transmission to humans. We will analyze the major environmental factors regulating the abundance of legionella, such as grazing and assimable dissolved organic carbon, because the occurrence of these heterotrophic bacteria in aquatic habitats is highly dependent on these factors. We will use an integrated molecular approach based on highresolution diagnostics of environmental samples and clinical isolates to determine the abundance, activity and virulence potential of Legionella populations in-situ. Combining environmental and molecular epidemiological data, we aim at understanding the link between ecology and population dynamics of legionella and cases of LD. The project will result in a novel understanding of the molecular epidemiology of legionella and provide new surveillance tools and strategies to prevent LD.

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