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Extracellular dissolved organic carbon (DOC) concentrations in axenic and xenic cultures of Thalassiosira gravida in response to varying temperatures and photoperiods

This dataset comprises dissolved organic carbon (DOC) concentrations from axenic and xenic cultures of Thalassiosira gravida that were cultivated at the Alfred-Wegener-Institute (Bremerhaven, Germany) in March, 2023. After a cell density of ~ 15.000 cells * mL-1 was reached, cultures were filtered through a 0.2 µm polycarbonate (PC) filter (Whatman) that was cleaned by soaking in 10 % hydrochloric acid (HCl, Merck suprapure) for at least 12 h and subsequently rinsing with ultrapure water (Merck Millipore MilliQ). DOC was quantified by high temperature catalytic oxidation with a Shimadzu TOC analyzer (VCPN-TOC, Shimadzu) according to Garzón-Cardona et al. 2024; doi: 10.1016/J.JMARSYS.2023.103893. Cultures were grown under two temperatures (9 °C, 13.5 °C) and two photoperiods (16:8 h, 24:0 h light:dark). The aim was to investigate responses of algal extracellular release and bacterial DOC transformation to marine heatwave-like conditions.

Dissolved organic matter (DOM) composition in axenic and xenic cultures of Thalassiosira gravida in response to varying temperatures and photoperiods

This dataset comprises dissolved organic matter (DOM) composition from axenic and xenic cultures of Thalassiosira gravida that were cultivated at the Alfred-Wegener-Institute (Bremerhaven, Germany) in March, 2023. After a cell density of ~ 15.000 cells * mL-1 was reached, cultures were filtered through a 0.2 µm polycarbonate (PC) filter (Whatman) that was cleaned by soaking in 10 % hydrochloric acid (HCl, Merck suprapure) for at least 12 h and subsequently rinsing with ultrapure water (Merck Millipore MilliQ). Cultures were grown under two temperatures (9 °C, 13.5 °C) and two photoperiods (16:8 h, 24:0 h light:dark). 2 mL of the sample were filtered through a 0.2 µm regenerated cellulose (RC)-membrane syringe filter (Sartorius) after defrosting. Molecular composition data were acquired with Fourier-transform ion cyclotron resonance mass spectrometry (FT-ICR-MS) coupled to a reversed-phase liquid chromatography (RPLC) with negative electrospray ionization (ESI) according to Lechtenfeld et al., 2024 (doi: 10.1021/acs.est.3c07219). Measurements were performed on on a solariX XR, Bruker Daltonics, Billerica, U.S.A. at the Helmholtz Centre for Environmental Research (UFZ; Leipzig, Germany). Molecular formulas were assigned and filtered using UltraMassExplorer (Leefmann et., 2019; doi: 10.1002/rcm.8315). If the Total ion chromatogram (TIC) was much higher and/or different in certain retention time windows compared to other samples of the same treatment, the sample was excluded from the dataset. The aim of this study was to investigate responses of algal extracellular release and bacterial DOM transformation to marine heatwave-like conditions.

Copper in sediment, water and suspended particulate matter of the tidal influenced part of the Elbe River sampled in April 2023 (LP20230402)

Legacy pollutants (e.g. Cu) are well studied and known to deposit in regions of sedimentation along rivers like the Elbe River located in northern Germany. However, in order to help authorities to maintain rivers as important economic transport routes numerical models are used to forecast possible pollution transportation after dredging or sediment relocation. To improve the precision of such models, valid data related to the pollution partitioning behavior and constant model validation is needed. Sediment, water and suspended particulate matter (SPM) were sampled during a sampling campaign in April 2023 and analyzed within the context of the cooperation project CTM-Elbe of BAW and Hereon. The sediment samples were taken by a box corer, homogenized, freeze-dried and wet-sieved to gain the <63 µm grain size fraction. The <63 µm grain size fraction was acid digested and measured by ICP-MS/MS for their (trace) metal mass fractions. The high-volume water samples were centrifuged with a continuous flow centrifuge (CFC) to separate the SPM from the water phase before the SPM samples were freeze-dried. The obtained SPM samples were treated analogously to the sieved sediment samples. The water samples were taken in metal-free GO-FLO sampling bottles and filtered over <0.45 µm polycarbonate filters in the laboratory before acidification with nitric acid. The filtrates were then measured for their (trace) metal concentrations with ICP-MS/MS coupled online to a seaFAST preconcentration and matrix removal system. This data set provides the Cu mass fractions in the fine grain sediment fraction of the SPM together with dissolved (<0.45 µm) Cu concentrations in the water.

Bioethanol to Acetone - Chemische und biotechnologische Prozessentwicklung zur Erschließung nachhaltiger Feedstocks, BETA - Bioethanol to Acetone - Chemische und biotechnologische Prozessentwicklung zur Erschließung nachhaltiger Feedstocks

TemBi 2014 mesocosm study: Summer storm impact on size-fractionated bacterial protein production and abundance of heterotrophic prokaryotes and picocyanobacteria

We simulated an experimental summer storm in large-volume (~1200 m³, ~16m depth) enclosures in Lake Stechlin (https://www.lake-lab.de) by mixing deeper water masses from the meta- and hypolimnion into the mixed layer (epilimnion). The mixing included the disturbance of a deep chlorophyll maximum (DCM) which was present at the same time of the experiment in Lake Stechlin and situated in the metalimnion of each enclosure during filling. Size-fractionated Bacterial Protein Production (BPP) of particle associated (PA, >3.0 µm) and free-living bacteria (FL, 0.2-3.0 µm) (14C-Leu incorporation) as well as abundances of PA (microscopy of DAPI stained cells on 3.0 µm polycarbonate filters) and FL heterotrophic prokaryotes and picocyanobacteria (flow cytometry of SYBR green I stained cells) were monitored for 42 days after the experimental disturbance event. Mixing increased bacterial abundance and production about 3 weeks after mixing, which was associated to a mixing-induced stimulation of phytoplankton growth in the mixed enclosures compared to the controls. Simultaneously, decreased abundances of picocyanobacteria could be observed in mixed enclosures.

Hochgeschwindigkeitsextrusion amorpher Polymere am Beispiel von Polycarbonat (PC) und Polymethylmethacrylat (PMMA)

Trace metal distribution for water samples of the cruise AT010

Offshore wind energy is a steadily growing sector contributing to the worldwide energy production. The impact of these offshore constructions on the marine environment, however, remains unclear in many aspects. In fact, little is known about potential emissions from corrosion protection systems such as organic coatings or galvanic anodes composed of Al and Zn alloys, used to protect offshore structures. In order to assess potential chemical emissions from offshore wind farms and their impact on the marine environment water and sediment samples were taken in and around offshore wind farms of the German Bight between 04.04.2022 and 14.04.2022 within the context of the Hereon-BSH project OffChEm II. The water samples were taken in metal-free GO-FLO sampling bottles, filtered over <0.45 µm polycarbonate filters into pre-cleaned LDPE bottles and acidified with nitric acid. The filtrates were then measured for their (trace) metal concentrations with ICP-MS/MS coupled online to a seaFAST preconcentration and matrix removal system.

Trace metal distribution for water samples of the cruise AT004

Offshore wind energy is a steadily growing sector contributing to the worldwide energy production. The impact of these offshore constructions on the marine environment, however, remains unclear in many aspects. In fact, little is known about potential emissions from corrosion protection systems such as organic coatings or galvanic anodes composed of Al and Zn alloys, used to protect offshore structures. In order to assess potential chemical emissions from offshore wind farms and their impact on the marine environment water and sediment samples were taken in and around offshore wind farms of the German Bight between 12.04.2021 and 23.04.2021 within the context of the Hereon-BSH project OffChEm II. The water samples were taken in metal-free GO-FLO sampling bottles, filtered over <0.45 µm polycarbonate filters into pre-cleaned LDPE bottles and acidified with nitric acid. The filtrates were then measured for their (trace) metal concentrations with ICP-MS/MS coupled online to a seaFAST preconcentration and matrix removal system.

Trace metal distribution for water samples of Atair cruise AT275

Offshore wind energy is a steadily growing sector contributing to the worldwide energy production. The impact of these offshore constructions on the marine environment, however, remains unclear in many aspects. In fact, little is known about potential emissions from corrosion protection systems such as organic coatings or galvanic anodes composed of Al and Zn alloys, used to protect offshore structures. In order to assess potential chemical emissions from offshore wind farms and their impact on the marine environment water and sediment samples were taken in and around offshore wind farms of the German Bight between 06.03.2019 and 24.03.2019 within the context of the Hereon-BSH project OffChEm. The water samples were taken in metal-free GO-FLO sampling bottles, filtered over <0.45 µm polycarbonate filters into pre-cleaned LDPE bottles and acidified with nitric acid. The filtrates were then measured for their (trace) metal concentrations with ICP-MS/MS coupled online to a seaFAST preconcentration and matrix removal system.

Trace metal distribution for water samples of Ludwig Prandtl cruise LP20200629

Offshore wind energy is a steadily growing sector contributing to the worldwide energy production. The impact of these offshore constructions on the marine environment, however, remains unclear in many aspects. In fact, little is known about potential emissions from corrosion protection systems such as organic coatings or galvanic anodes composed of Al and Zn alloys, used to protect offshore structures. In order to assess potential chemical emissions from offshore wind farms and their impact on the marine environment water and sediment samples were taken in and around offshore wind farms of the German Bight between 22.07.2020 and 25.07.2020 within the context of the Hereon-BSH project OffChEm. The water samples were taken in metal-free GO-FLO sampling bottles, filtered over <0.45 µm polycarbonate filters into pre-cleaned LDPE bottles and acidified with nitric acid. The filtrates were then measured for their (trace) metal concentrations with ICP-MS/MS coupled online to a seaFAST preconcentration and matrix removal system.

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