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Finalised projects

AMBER - Assessment and Modelling Baltic Ecosystem Response

BIOACID - Biological Impact of Ocean Acidification

COCOA -Nutrient COcktails in COAstal zones of the Baltic Sea

FONIP - Transfer of diazotrophic nitrogen into the pelagic food web: the role of essential and non-essential aminoacids

HYPER - HYPoxia mitigation for Baltic Sea Ecosystem Restoration

NIQSI - Nitrate source identification and quantification in the euphotic zone of the Baltic Proper using nitrogen and oxygen stable isotopes (N Sources Baltic Proper)

N - Sinks Baltic - Quantification of Nitrogen sinks of the Baltic Sea and dependence on various environmental parameters

SOPRAN - Surface Ocean Processes in the Anthropocene

TRACES - Ocean- Atmosphere- Land Impacts On Tropical Atlantic Ecosystems

Vietnam - project - Pelagic processes and nitrogen cycle in coastal waters off southern central Vietnam: mesocosm experiments, field work and modelling

Assessment and Modelling Baltic Ecosystem Response (AMBER )

(2009-2012)

The general aim of AMBER is the implementation and application of the Ecosystem Approach to Management (EAM) to the Baltic Sea with a focus on the coastal ecosystem (CE). The first step of AMBER is the separation of climate from anthropogenic signals in the CE by means of a combinatorial variation in model’s boundary conditions using the output of existing regional climate change scenarios and the output of a watershed model simulating changes in land use.
     
The second step of AMBER is the application of models for future projections. To reduce the problem of model uncertainties, the ensemble method will be applied. The resulting projections are milestones for the development of EAM tools.
 
To implement the EAM concept successfully requires the best available scientific information as a basis for integrated management. Therefore, retrospective analyses on long‐term data sets, intensive modeling with different types of models and selected measurements of biogeochemical transformation processes in the near coastal area and the groundwater will be applied and integrated into a sound scientific basis for supporting the development of EAM tools such as risk assessment, mitigation strategies, and Ecological Quality Objectives. Finally, cost‐effective indicators will be developed to improve monitoring strategies and to guide management decision making. EAM with its tools will be the core of science based advice for integrated management.

Contact: Dr. Maren Voß, Frederike Korth

BIOACID III: Verbundprojekt: BIOACID Synthese - Biologische Auswirkungen der Ozeanversauerung; Vorhaben: Einfluss der Ozeanversauerung auf pelagische Stickstoffkreisläufe

Biological impacts of ocean acidification (phase II)
Subproject 1.4 Diazotrophic nitrogen fixation and nitrogen cycling within the plankton community.

(2012-2015)

We aim to better understand the uptake of nitrogen by primary producers (especially diazotrophic cyanobacteria), as well as the release of nitrogenous compounds under different pCO2 concentrations. Community specific uptake will be done using stable isotope tracer addition and mass spectrometry analysis. Different nitrogenous tracer will be used (15N2 gas, 15N-amino acids) to address different aspects of nitrogen cycling. Cell specific nitrogen uptake and processing as well as cell specific metabolic rates can be investigated using the IOW facility of the NanoSIMS. This method will help to understand cell specific differences based upon changes in the specific genome making specific genotypes more efficient within one species.

Moreover, the time depended transfer of diazotrophic nitrogen into the bacterial community or towards higher trophic levels will be analysed using stable isotope tracer addition.

Furthermore, the impact of ocean acidification on toxin production (mainly Nodularin and Microscystin) will be determined using HPLC and ELISA techniques.

Two joint Mesocosm experiments will be carried out by the whole Consortium 1 (Pelagic ecosystems under ocean acidification: ecological, biogeochemical, and evolutionary responses) at which our subproject participates. KOSMOS I (Kiel Offshore Mesocosms for Future Ocean Simulation) will take place in 2013 in Gullmar Fjord near Kristineberg, Sweden , KOSMOS II 2014 at Gran Canary.

 

We propose to test the following hypotheses:

  • Does the theory of reduction of carbon concentration mechanism hold true to explain the mechanisms of increased primary production and N2 fixation in cyanobacteria as a response to ocean acidification and temperature increase?
  • Will the rate and stoichiometry of organic matter turn-over and nutrient cycling become affected? What are the tipping points?
  • Can relationships between environmental constraints e.g. OA and toxicity be developed?
  • Do microbes (autotrophs and heterotrophs) respond to OA along gradients of natural variability as typical for the Baltic Sea (alkalinity, DIC, CO2, T, nutrients)?
  • Is the community composition of cyanobacteria blooms sensitive to OA?

contakt: Nicola Wannicke

Biological Impact of Ocean Acidification (BIOACID)
Subproject 1.2 Turnover of organic matter

(2009-2012)

Numbers and facts

BIOACID deals with consequences of ocean acidification on chalk building processes, growth and activity of marine organisms. Altogether 14 institutes are engaged nationwide for the next three years in this BMBF funded project (8.5 Mio Euro). The coordination of the 5 subprojects is done by the Leibniz Institute of Marine Sciences, Kiel (IFM-GEOMAR). At the Leibniz Institute for Baltic Sea research 3 PhD students and one PostDoc are employed.
The overarching goal of BIOACID is to identify a potential threshold associated with ocean acidification as a guard rail for political decision- maker.

Background

Since the beginning of industrialization the atmospheric CO2 pressure rose from 280 to 380 ppm. Annually, one third of CO2 emerging from the burning of fossil fuels is dissolves in oceanic waters. As a consequence of the dissolution the concentration of carbonic acid increases, while carbonate decreases, leading to an overall reduction of the pH value within the oceans. This is already measurable. Since 1980 the pH value decreased by 0.06 units. Projecting this trend to the year 2100 (if the status quo is assumed), the ph will drop from now 8.14 to 7.7 (6% decrease)-Figure 1.

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This number does not sound dramatic, but it has to be remembered that organisms have a pH optimum. The most sensible organisms are chalk building species like corals and bivalves, which are impeded in the formation of skeleton properties, because of the altered water chemistry. Subsequently, a sort of domino effect can occur, where competition between chalk species and non-chalk species is altered leading to differences in matter flow and biodiversity changes from bacteria to other trophic level. Furthermore, the increased availability of carbon will affect primary production, which is dominated in the Baltic Sea in summer time by dinitrogen (N2) fixing cyanobacteria. The interplay of ocean acidification and carbon availability, primary production, N2 fixation and coupling with other trophic level (microbial loop) will be studied in this sub-project (1.2)
The overarching question is, “What consequences does ocean acidification have on the productivity of single trophic level (primary producer, bacteria) and the turnover of organic matter produced? Our hypothesis is, that ocean acidification will lead to an increase in primary production and nitrogen fixation, altering the C:N:P ration of particulate organic biomass (POM) and dissolved organic matter (DOM, TEP). These qualitative and quantitative differences in the stöchiometry influence the bacterial degradation of DOM/TEP (Figure 2).

 

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Kontakt: Nicola Wannicke

Insights into the biogeochemistry work of the COCOA project: from the water column to the sediment, from the field to the lab. Secrets of the coastal filter and a life in aquatic sciences.

Nutrient COcktails in COAstal zones of the Baltic Sea

WP 2 - Microbial transformation processes

(2013-2017)

The overall strategy of COCOA is to obtain detailed information on nutrient and organic matter cycling from a few well-selected and well-studied learning sites supplemented with new measurements. We will use this information to extrapolate to all coastal sites in order to assess the different management options for the coastal zone as well as the open Baltic Sea through an improved description of coastal nutrient retention. The learning sites have been chosen to represent four specific types of coastal ecosystems for the Baltic Sea (river-dominated estuaries, lagoons, embayments with restricted water exchange, and archipelagos). The learning sites have been selected because 1) they are believed to be representative of the given coastal type, 2) an extensive monitoring program is already in place and long-term monitoring data sets are available, 3) they have been studied previously and research data are available, and 4) field sampling can be carried out more frequently and at a lower cost, since the sites are close to partner institutions.

The work in COCOA is organised around seven scientific work packages (WP1-7) with links as shown in Fig. 3 and one WP for the management of the consortium (WP8). Details of the work to be carried out are given in the WP descriptions below.

The general flow of information between WPs in COCOA. Field-sampling WPs are in blue, modelling WPs are in orange and WP7 addresses the potential application of the results for managing coastal as well as open waters of the Baltic Sea.

Contakt: Dr. Maren Voß

FONIP

Transfer of diazotrophic nitrogen into the pelagic food web: the role of essential and non-essential amino acids

What is the quality of nitrogen from N2-fixation by cyanobacteria (diazotroph nitrogen) for the marine ecosystem once it has been transformed into bioavailable molecules like amino acids? The annual input of nitrogen by nitrogen fixation has been estimated to be 110 Tg for the global ocean (Gruber and Sarmiento 1997, Capone 2001). Depending on the pathway and bioavailable form by which diazotroph nitrogen enters the food web, it may facilitate autotrophic or hetreotrophic growth and thus cause a carbon export from the euphotic zone, or bacterial production and respiration in the euphotic zone (Fig. 1, Mulholland 2007). A compound specific isotope analysis (CSIA) allows to track the qualitative and quantitative   „end-to-end“ transfer of 15N marked N2 into the amino acids of cyanobacteria and further into the essential and non-essential amino acids of their grazers by gaschromatography-combustion-isotope ratio mass spectrometry (GC-C-IRMS).
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Fig. 1: Pathways of diazotrophic nitrogen into the heterotrophic food web. In the FONIP Project we investigate the primary uptake of diazotroph nitrogen by heterotrophs like copepods.

Besides field investigations we do controlled laboratory experiments with ecologically relevant model-organisms like the cyanobacterium Nodularia spumigena and its grazer the copepod Eurytemora affinis. For the first time we can quantify the transfer of newly formed amino acids from nitrogen fixation from the cyanobacteria into their grazers as well as detect the quality of the diazotrophic nitrogen for the zooplankton. The identification of the quality of diazotroph nitrogen as well as the quantification of its pathways into the marine ecosystem are fundamental prerequisites to predict the effects of increased or decreased diazotrophy in the context to global change like ocean acidification.

Literature
Capone, D. G., 2001. Current Opinion in Microbiology 4 (3): 341 – 348.
Gruber, N. and Sarmiento, J. L., 1997. Global Biogeochemical Cycles 11 (2): 235 – 266.
Mulholland, M. R., 2007. Biogeosciences, 4, 37–51.

HYPER

NIQSI

Nitrate source identification and quantification in the euphotic zone of the Baltic Proper using nitrogen and oxygen stable isotopes (N Sources Baltic Proper)

Nitrate sources of the Baltic Proper will be identified and quantified by means of nitrogen and oxygen stable isotopes. The Baltic Sea is strongly influenced by the catchment (covering 4 times the area of the sea itself) and the anthropogenic activity there. In particular nitrate and phosphorus inputs via rivers, point sources, and atmospheric deposition cause eutrophication which aggravate anoxia in bottom waters. An additional source is nitrogen fixation by cyanobacteria in the euphotic zone. Potential nitrate sources are largely known. However, there are still substantial uncertainties regarding their quantity and relative importance for the primary production in the euphotic zone of the Baltic Proper. The denitrifier method, which enables measurement of both nitrogen and oxygen isotopes of nitrate, will be applied for the first time in this region. The isotope signature makes it possible to distinguish between different nitrogen sources and processes affecting the nitrate concentration in the euphotic layer. Potential sources (nitrate pool, atmospheric deposition plus for the first time dissolved organic nitrogen) will be analyzed. Additional experimental studies will help to determine the relative importance of different nitrogen forms (inorganic and organic) supporting the primary production. A nitrate budget for the euphotic layer in the central Baltic Sea will be established.

tl_files/staff/fellerho/nitrate saisonalitaet fuer Website.jpg

Figure: Schematic diagram of seasonality of nitrate concentration in the water column of the Baltic Proper; numbers indicate various nitrate sources/sinks: 1: degraded phytoplankton, 2: atmospheric input, 3: riverine input, 4: N2 fixation, 5: DON, 6: watercolumn nitrification/denitrification, 7: sedimentary nitrification/ denitrification. The diagram is a compilation of own previous findings (see chapter “preliminary work”).

N sinks Baltic

"Quantification of Nitrogen sinks of the Baltic Sea and dependence on various environmental parameters" (N sinks Baltic), DFG funded (2007-2009)

The Baltic Sea is the largest brackish water body of the world and because of its enclosed position and the hydrographical conditions very sensible to nutrient inputs. Whereas the main sources of nitrogen are well known (nitrogen fixation and atmospheric deposition for the central Baltic; direct and riverine inputs for the coastal areas) there is still a lack of knowledge about the losses of reactive nitrogen via processes like denitrification and anaerobic ammonium oxidation (anammox; fig. 1). The microbial processes in the water column and the sediments are manifold and still less understood.
The DFG funded project "N sinks Baltic" deals with the quantification of these N losses. By means of the isotope pairing method the rates of denitrification and anammox are measured in different sediment types (mud, silt, sand) and the water column. The investigations are carried out at different seasons. Additional determinations of nutrient and oxygen profiles in the water column and the sediment as well as other sediment parameters should provide further information about the controlling factors.
By means of sediment maps the measured rates should be extrapolated to the whole area of the Baltic Sea.

Stickstoffkreislauf
Fig. 1: Simplified N-cycle with the major microbial pathways denitrification (blue arrows), nitrification (red arrows), and anaerobic ammonium oxidation (black arrows). Redrawn after Jetten (2001) and Altabet (2001)

Surface Ocean Processes in the Anthropocene

Logo Sopran

Surface Ocean Processes in the Anthropocene , BMBF funded (2007 - 2010)
Theme 2: Effect of Anthropocene CO2 levels on marine ecosystems and sea-to-air gas fluxes The atmosphere's composition determines the Earth's climate and habitability. This composition is, in turn, strongly determined by biological, physical and chemical processes occurring within the oceans. Increasingly, mankind is altering the composition of the atmosphere and therefore altering the interplay between the physical climate system and biogeochemistry. Such changes impact, in turn, the atmospheric composition, ocean ecosystems and climate via feedback processes. The SOPRAN (Surface Ocean Processes in the ANthropocene) project addresses three aspects of this interaction:

  • How changing atmospheric composition (e.g. increased CO2, dust) affects the surface ocean ecosystem ?
  • How climate-related changes in surface ocean processes (upwelling, mixing, light, biology) alter oceanic emissions to the atmosphere ?
  • The mechanisms and rates of ocean-atmosphere material exchanges.

SOPRAN's focus is on processes operating within and close to the surface ocean, and their potential changes over the next century. The project is an integrated study of surface ocean response to global change, combining the insight of marine and atmospheric chemists, biological and physical oceanographers, as well as modelling on a range of scales. Shared activities include technological development and use of new floating mesocosms for studying global change effects on marine ecosystems, extension of physical modelling capabilities to study key biological and chemical processes in the surface layer, and the use of a new climate and biogeochemistry observatory in the Cape Verde Islands (in collaboration with UK, EU and Cape Verde investigators). The programme will deliver a better understanding of the role of the ocean in the climate system and an improved description of the effects of global change on the sensitive marine ecosystem. SOPRAN will furthermore:

The project involves 42 investigators from 12 partner institutions from all over Germany working in 23 sub-projects. The sub-projects are allocated to 4 inter-related Themes:

  • the oceanic response to atmospheric dust
  • effect of high CO2 on marine ecosystems and sea-toair gas fluxes
  • production and emission of radiatively and chemically active gases in the Tropical Oceans
  • inter-phase transfer at the sea surface.

These Themes are further interlinked by "Over-Arching Activities".Field work is concentrated in the Baltic Sea and the Eastern Tropical North Atlantic.

TRACES Ocean- Atmosphere- Land Impacts On Tropical Atlantic Ecosystems

Logo Traces

WGL-Network: "TRACES Ocean- Atmosphere- Land Impacts On Tropical Atlantic Ecosystems", funded by the Leibniz Institutes (2006-2008)

TRACES is a joint research project investigating interactions within the ecosystem Atlantic Ocean (an area that reacts critically towards global changes). Special focus is put on the exchange of matter (in particular carbon an nitrogen fluxes) between land, ocean and atmosphere within the tropical Atlantic Ocean. This region is of special importance for the global nitrogen balance, because here the commonly occurring nitrogen fixation is fuelled by the input of its limiting nutrients iron and phosphorous coming from terrestrial sources (dust and riverine input).
Aspects of the Tropical Atlantic Ocean network could focus on, or promote an exchange of ideas:

  • theme 1: Carbon fluxes in Amazonia. Impact of climate variability and terestrial CO2 - emission on the carbon budget.
  • theme 2: Transport and conversion processes in the atmosphere of the tropical Atlantic Ocean. Dust transport and climate Photochemistry of tropospheric aerosols and the barrier of the ozon layer
  • theme 3: Abiotic influences on the ecosystem of the Atlantic Ocean.
    Control of nitrogen fixation by external input of trace metals and macro nutrients
    Transfer of recently fixed nitrogen within the food web

Vietnam project

Logo Vietnam

Pelagic processes and nitrogen cycle in coastal waters off southern central Vietnam: mesocosm experiments, field work and modelling" , DFG funded (2006 - 2008)

The DFG - project "Pelagic processes and biogeochemical fluxes in the South China Sea (SCS) off southern central Vietnam" is part of a German - Vietnamese Cooperation in Marine Science. The focus of our work is on the pelagic nitrogen cycle in the upwelling area off the Vietnamese coast. Seasonal changes in the relative importance of different N-nutrient sources for primary production (upwelling, input by Mekong-river, and biological fixation of atmospheric N2) and their impact on pelagic system dynamics are investigated. Since 2003 planktological and biogeochemical investigations were carried out jointly with our partner Institute of Oceanography Nha Trang (ION), the work of which is funded by Ministry of Science and Technology (MOST), Hanoi. We also work in close collaboration with the physical-oceanographic projects of University Hamburg (IfM) and of ION which elucidated hydrodynamics as the prime forcing of nutrient supply in our joint investigation area.

With a modified approach the project will be continued until 2008. Whereas field sampling on expeditions with large research vessels characterized the first project phase, emphasis is now on land-based mesocosm experiments in which upwelling and Mekong inflow will be simulated by mixing water from the different pelagic systems (Mekong plume, upwelling water, oligotrophic surface water). Our goal is to better understand pelagic production regimes typically encountered seasonally and regionally, regarding the contributions by different plankton (nitrogen fixing organisms and other functional groups), their response to upwelling and admixture of river water, and the impact of this on the overall nitrogen- and carbon cycles in the SCS. The experiments provide the opportunity to closely follow trends in primary production, uptake of different nitrogen species (NO3-, NH4+, N2), and succession as the plankton community responds to changing nutrient conditions. The mesocosm experiments are combined with ecosystem modelling of key processes in the N-cycle, results of which will be tested against field results and can be implemented in circulation models. Field studies using small ships in the Mekong river plume and the upwelling region will document in situ conditions of pelagic systems which provide the source material for the experiments and further link our work to partner projects.

We start the second phase of the project with the following hypotheses:

  • The nutrient concentration and N/P ratios in the upwelling water drive the production and the species selection in the upwelling region off Vietnam.
  • Mekong and other River water may act as additional driver of the production and of species selection through nutrient, silica, and DOM input
  • A nitrogen cycle model can constrain the driving factors of productivity and species selection.