Der Verlauf der atmosphärischen CO2-Konzentrationen während der vergangenen Klimazyklen ist durch ein Sägezahnmuster mit Maxima in Warmzeiten und Minima in Kaltzeiten geprägt. Es besteht derzeit Konsens, dass insbesondere der Süd Ozean (SO) eine Schlüsselfunktion bei der Steuerung der CO2-Entwicklung einnimmt. Allerdings sind die dabei wirksamen Mechanismen, die in Zusammenhang mit Änderungen der Windmuster, Ozeanzirkulation, Stratifizierung der Wassersäule, Meereisausdehnung und biologischer Produktion stehen, noch nicht ausreichend bekannt. Daten zur Wirkung dieser Prozesse im Wechsel von Warm- und Kaltzeiten beziehen sich bislang fast ausschließlich auf den atlantischen SO. Um ein umfassendes Bild der Klimasteuerung durch den SO zu erhalten muss geklärt werden, wie weit sich die aus dem atlantischen SO bekannten Prozesswirkungen auf den pazifischen SO übertragen lassen. Dies ist deshalb von Bedeutung, da der pazifische SO den größten Teil des SO einnimmt. Darüber hinaus stellt er das hauptsächliche Abflussgebiet des Westantarktischen Eisschildes (WAIS) in den SO dar. Im Rahmen des Projektes sollen mit einer neu entwickelten Proxy-Methode Paläoumwelt-Zeitreihen an ausgewählten Sedimentkernen von latitudinalen Schnitten über den pazifischen SO hinweg gewonnen werden. Dabei handelt es sich um kombinierte Sauerstoff- und Siliziumisotopenmessungen an gereinigten Diatomeen und Radiolarien. Es sollen erstmalig die physikalischen Eigenschaften und Nährstoffbedingungen in verschiedenen Stockwerken des Oberflächenwassers aus verschiedenen Ablagerungsräumen und während unterschiedlicher Klimabedingungen beschrieben werden. Dies umfasst Bedingungen von kälter als heute (z.B. Letztes Glaziales Maximum) bis zu wärmer als heute (z.B. Marines Isotopen Stadium, MIS 5.5). Die Untersuchungen geben Hinweise zur (1) Sensitivität des antarktischen Ökosystems auf den Eintrag von Mikronährstoffen (Eisendüngung), (2) Oberflächenwasserstratifizierung und (3) 'Silicic-Acid leakage'-Hypothese, und tragen damit zur Überprüfung verschiedener Hypothesen zur Klimawirksamkeit von SO-Prozessen bei. Die neuen Proxies bilden überdies Oberflächen-Salzgehaltsanomalien ab, die Hinweise zur Stabilität des WAIS unter verschiedenen Klimabedingungen geben. Darüber hinaus kann die Hypothese getestet werden, nach der der WAIS während MIS 5.5 vollständig abgebaut war. Die Projektergebnisse sollen mit Simulationen mit einem kombinierten biogeochemischen (Si-Isotope beinhaltenden) Atmosphäre-Ozean-Zirkulations-Modell aus einem laufenden SPP1158-DFG Projekt an der CAU Kiel (PI B. Schneider) verglichen werden. Damit sollen die jeweiligen Beiträge der Ozeanzirkulation und der biologischen Produktion zum CO2-Austausch zwischen Ozean und Atmosphäre getrennt und statistisch analysiert werden. Informationen zu Staubeintrag, biogenen Flussraten, physikalischen Ozeanparametern und zur Erstellung von Altersmodellen stehen durch Zusammenarbeit mit anderen (inter)nationalen Projekten zur Verfügung.
Water is an intrinsic component of ecosystems acting as a key agent of lateral transport for particulate and dissolved nutrients, forcing energy transfers, triggering erosion, and driving biodiversity patterns. Given the drastic impact of land use and climate change on any of these components and the vulnerability of Ecuadorian ecosystems with regard to this global change, indicators are required that not merely describe the structural condition of ecosystems, but rather capture the functional relations and processes. This project aims at investigating a set of such functional indicators from the fields of hydrology and biogeochemistry. In particular we will investigate (1) flow regime and timing, (2) nutrient cycling and flux rates, and (3) sediment fluxes as likely indicators. For assessing flow regime and timing we will concentrate on studying stable water isotopes to estimate mean transit time distributions that are likely to be impacted by changes in rainfall patterns and land use. Hysteresis loops of nitrate concentrations and calculated flux rates will be used as functional indicators for nutrient fluxes, most likely to be altered by changes in temperature as well as by land use and management. Finally, sediment fluxes will be measured to indicate surface runoff contribution to total discharge, mainly influenced by intensity of rainfall as well as land use. Monitoring of (1) will be based on intensive sampling campaigns of stable water isotopes in stream water and precipitation, while for (2) and (3) we plan to install automatic, high temporal-resolution field analytical instruments. Based on the data obtained by this intensive, bust cost effective monitoring, we will develop the functional indicators. This also provides a solid database for process-based model development. Models that are able to simulate these indicators are needed to enable projections into the future and to investigate the resilience of Ecuadorian landscape to global change. For the intended model set up we will couple the Catchment Modeling Framework, the biogeochemical LandscapeDNDC model and semi-empirical models for aquatic diversity. Global change scenarios will then be analyzed to capture the likely reaction of functional indicators. Finally, we will contribute to the written guidelines for developing a comprehensive monitoring program for biodiversity and ecosystem functions. Right from the beginning we will cooperate with four SENESCYT companion projects and three local non-university partners to ensure that the developed monitoring program will be appreciated by locals and stakeholders. Monitoring and modelling will focus on all three research areas in the Páramo (Cajas National Park), the dry forest (Reserva Laipuna) and the tropical montane cloud forest (Reserva Biologica San Francisco).
Biogeochemical interfaces shape microbial community function in soil. On the other hand microbial communities influence the properties of biogeochemical interfaces. Despite the importance of this interplay, basic understanding of the role of biogeochemical interfaces for microbial performance is still missing. We postulate that biogeochemical interfaces in soil are important for the formation of functional consortia of microorganisms, which are able to shape their own microenvironment and therefore influence the properties of interfaces in soil. Furthermore biogeochemical interfaces act as genetic memory of soils, as they can store DNA from dead microbes and protect it from degradation. We propose that for the formation of functional biogeochemical interfaces microbial dispersal (e.g. along fungal networks) in response to quality and quantity of bioavailable carbon and/or water availability plays a major role, as the development of functional guilds of microbes requires energy and depends on the redox state of the habitat.To address these questions, hexadecane degradation will be studied in differently developed artificial and natural soils. To answer the question on the role of carbon quantity and quality, experiments will be performed with and without litter material at different water contents of the soil. Experiments will be performed with intact soil columns as well as soil samples where the developed interface structure has been artificially destroyed. Molecular analysis of hexadecane degrading microbial communties will be done in vitro as well as in situ. The corresponding toolbox has been successfully developed in the first phase of the priority program including methods for genome, transcriptome and proteome analysis.
We consider clay minerals, iron oxides and charcoal as major components controlling the formation of interfaces relevant for sorption of organic chemicals, as they control the assemblage of organic matter and mineral particles. We studied the formation of interfaces in batch incubation experiments with inoculated artificial soils consisting of model compounds (clay minerals, iron oxide, char) and natural soil samples. Results show a relevant contribution of both iron oxides and clay minerals to the formation of organic matter as sorptive interfaces for hydrophobic compounds. Thus, we intend to focus our work in the second phase on the characterization of the interface as formed by organic matter associated with clay minerals and iron oxides. The interfaces will be characterized by the BET-N2 and ethylene glycol monoethyl ether (EGME) methods and 129Xe and 13C NMR spectroscopy for determination of specific surface area, sorptive domains in the organic matter and microporosity. A major step forward is expected by the analysis of the composition of the interface at different resolution by reflected-light microscopy (mm scale), SEM (scanning electron microscopy, micrometer scale) and secondary ion mass spectrometry at the nanometer scale (nanoSIMS). The outcomes obtained in combination with findings from cooperation partners will help to unravel the contribution of different types of soil components on the formation and characteristics of the biogeochemical interfaces and their effect on organic chemical sorption.
In freshwater sediments, iron oxidation is dominated by phototrophic and chemotrophic (aerobic and nitrate-reducing) Fe(ll)-oxidizing microorganisms. Although these biogeochemical processes have been investigated in detail in laboratory studies, not much is known about their spatial distribution, interactions (e.g. competition) amongst each other, as well as their response towards environmental perturbations (i.e. temperature, geochemical variations (nutrient, organic matter input)). This research proposal aims to investigate the activity, abundance and resource competition between different chemotrophic (aerobic and (autotrophic/mixotrophic) anaerobic nitrate-reducing) and phototrophic ironoxidizing microorganisms. In order to better understand the spatial distribution of nitrate-reducing iron oxidizing bacteria, microbial nitrate-producing and competing, nitrate-depletion processes will also be studied throughout the sedimentary redox gradient. In addition, the activity and abundance of the ironoxidizing processes will be quantified with (geo)microbiological, molecular and novel spectral imaging techniques. Using high resolution geochemical measurements (microsensors) we will characterize the environmental conditions these bacteria experience in order to determine the role of spatial and functional niche competition in microbial iron oxidation and the interconnection to the N-cycle. Iron mineral formation will be investigated as a function of the microbial spatial and temporal activity, depending on environmental perturbations. The proposed research study will strongly improve the understanding of iron cycling, the interconnection to the N-cycle, as well as interactions and competition between phototrophic and chemotrophic metabolisms in aquatic environments.
The formation of biogeochemical interfaces in soils is controlled, among other factors, by the type of particle surfaces present and the assemblage of organic matter and mineral particles. Therefore, the formation and maturation of interfaces is studied with artificial soils which are produced in long-term biogeochemical laboratory incubation experiments (3, 6, 12, 18 months. Clay minerals, iron oxides and charcoal are used as major model components controlling the formation of interfaces because they exhibit high surface area and microporosity. Soil interface characteristics have been analyzed by several groups involved in the priority program for formation of organo-mineral interfaces, sorptive and thermal interface properties, microbial community structure and function. Already after 6 months of incubation, the artificial soils exhibited different properties in relation to their composition. A unique dataset evolves on the development and the dynamics of interfaces in soil in the different projects contributing to this experiment. An integrated analysis based on a conceptual model and multivariate statistics will help to understand overall processes leading to the biogeochemical properties of interfaces in soil, that are the basis for their functions in ecosystems. Therefore, we propose to establish an integrative project for the evaluation of data obtained and for publication of synergistic work, which will bring the results to a higher level of understanding.
Soil organic matter (SOM) controls large part of the processes occurring at biogeochemical interfaces in soil and may contribute to sequestration of organic chemicals. Our central hypothesis is that sequestration of organic chemicals is driven by physicochemical SOM matrix aging. The underlying processes are the formation and disruption of intermolecular bridges of water molecules (WAMB) and of multivalent cations (CAB) between individual SOM segments or between SOM and minerals in close interaction with hydration and dehydration mechanisms. Understanding the role of these mediated interactions will shed new light on the processes controlling functioning and dynamics of biogeochemical interfaces (BGI). We will assess mobility of SOM structural elements and sorbed organic chemicals via advanced solid state NMR techniques and desorption kinetics and combine these with 1H-NMR-Relaxometry and advanced methods of thermal analysis including DSC, TGADSC- MS and AFM-nanothermal analysis. Via controlled heating/cooling cycles, moistening/drying cycles and targeted modification of SOM, reconstruction of our model hypotheses by computational chemistry (collaboration Gerzabek) and participation at two larger joint experiments within the SPP, we will establish the relation between SOM sequestration potential, SOM structural characteristics, hydration-dehydration mechanisms, biological activity and biogechemical functioning. This will link processes operative on the molecular scale to phenomena on higher scales.
During the first project period we developed a general approach to quantify soil pore structure based on X-ray micro-tomography Vogel et al. (2010) which is applicable at various scales to cover soil pores larger that 0.05 mm in a representative way. Based on this method we generated equivalent network models to numerically simulate flow and transport of dissolved chemicals. The existing network model was extended to handle reactive transport and infiltration processes which are especially critical for matter flux in soil. The results were compared to experimental findings. The original research question 'what does a particle see on its way through soil' could be answered quantitatively for various boundary conditions including steady state flux and infiltration. However, we identified various critical aspects of the proposed modeling concept which will be in the focus of the second period. This includes 1) the spatial arrangement of interfaces having different quality which is crucial for chemical interactions and pore scale water dynamics, 2) the realistic multiphase dynamics at the pore scale which need to reflect the dynamic pressure and movement of trapped non-wetting phase and 3) the parametrization of structural complexity which need to be developed beyond the measurement of continuous Minkowski functions to allow the development of quantitative relations between structure and function. These aspects will be explored in a joint experiments in cooperation with partners within the SPP.
Atmospheric CO2 concentrations present a repetitive pattern of gradual decline and rapid increase during the last climate cycles, closely related to temperature and sea level change. During the Last Glacial Maximum (LGM; 23-19 kyr BP), when sea level was ca. 120 m below present, the ocean must have stored additionally about 750 Gt carbon. There is consensus that the Southern Ocean represents a key area governing past and present CO2 change. The latter is not only of high scientific but also of socio-economic and political concern since the Southern Ocean provides the potential for an efficient sink of anthropogenic carbon. However, the sensitivity of this carbon sink to climate-change induced reorganizations in wind patterns, ocean circulation, stratification, sea ice extent and biological production remains under debate. Models were not yet able to reproduce the necessary mechanisms involved, potentially due to a lack of the dynamic representation/resolution of atmospheric and oceanic circulation as well as missing carbon cycling. Data on past Southern Ocean hydrography and productivity are mainly from the Atlantic sector, thus do not adequately document conditions in the Pacific sector. This sector is not only the largest part of the Southern Ocean, but it also represents the main drainage area of the marine-based West Antarctic Ice Sheet (WAIS). In the proposed study we aim to generate paleo-data sets with a newly established proxy method from sediment core transects across the Pacific Southern Ocean. This will enhance the baselines for the understanding and modeling of the Southern Ocean's role in carbon cyling, i.e. ocean/atmosphere CO2 exchange and carbon sequestration. It will also allow insight into the response of the WAIS to past warmer than present conditions. Paired isotope measurements (oxygen, silicon) will be made on purified diatoms and radiolarians to describe glacial/interglacial contrasts in physical and nutrient properties at surface and subsurface water depth. This will be used to test (i) the impact of yet unconsidered dust-borne micronutrient deposition on the glacial South Pacific on shifts of primary productivity, Si-uptake rates and carbon export, (ii) the 'silicic-acid leakage' hypothesis (SALH) and (iii) the formation and extent of surface water stratification. Diatom and radiolarian oxygen isotopes will provide information on the timing of surface ocean salinity anomalies resulting from WAIS melt water. Climate model simulations using a complex coupled atmosphere ocean general circulation model (AOGCM) in combination with a sophisticated ocean biogeochemical model including Si-isotopes will be used for comparison with the paleo records. The analysis will cover spatial as well as temporal variability patterns of Southern Ocean hydrography, nutrient cycling and air-sea CO2-exchange. With the help of the climate model we aim to better separate and statistically analyse the individual impacts of ocean circulation and bio
Labor- und Feldstudien zeigen, dass die Oberflächengrenzschicht des Ozeans (â€Ìsurface microlayerâ€Ì, kurz SML) die biogeochemischen Kreisläufe von klimaaktiven und atmosphärisch wichtigen Spurengasen wie Kohlenstoffdioxid (CO2), Kohlenstoffmonoxid (CO), Methan (CH4), Lachgas (N2O) und Dimethylsulfid (DMS) stark beeinflusst: (i) Jüngste Studien aus den PASSME- und SOPRAN-Projekten haben hervorgehoben, dass Anreicherungen von oberflächenaktiven Substanzen (d.h. Tensiden) einen starken (dämpfenden) Effekt sowohl auf die CO2- als auch auf die N2O-Flüsse über die SML/Atmosphären-Grenzfläche hinweg haben und (ii) Spurengase können durch (mikro)biologische oder (photo)chemische Prozesse in der SML produziert und verbraucht werden. Daher kann der oberste Teil des Ozeans, einschließlich der SML, verglichen mit dem Wasser, das in der Mischungsschicht unterhalb der SML zu finden ist, eine bedeutende Quelle oder Senke für diese Gase sein, was von sehr großer Relevanz für die Forschungseinheit BASS ist. Die Konzentrationen von CO2, N2O und anderen gelösten Gasen in der SML (oder den oberen Zentimetern des Ozeans) unterscheiden sich nachweislich von ihren Konzentrationen unterhalb der SML. Typischerweise werden die Nettoquellen und -senken wichtiger atmosphärischer Spurengase mit Konzentrationen berechnet, die in der Mischungsschicht gemessen wurden und mit Gasaustauschgeschwindigkeiten, die die SML nicht berücksichtigen. Diese Diskrepanzen führen zu falsch berechneten Austauschflüssen, die in der Folge zu großen Unsicherheiten in den Berechnungen der Klima-Antrieben und der Luftqualität in Erdsystemmodellen führen können. Durch die Verknüpfung unserer Spurengasmessungen mit Messungen von (i) der Dynamik und den molekularen Eigenschaften der organischen Materie und speziell des organischen Kohlenstoffs (SP1.1; SP1.5), (ii) der biologischen Diversität und der Stoffwechselaktivität (SP1.2), (iii) den optischen Eigenschaften der organischen Materie (SP1.3), (iv) der photochemischen Umwandlung der organischen Materie (SP1.4) und (v) den physikalischen Transportprozessen (SP2.3) werden wir ein umfassendes Verständnis darüber erlangen, wie die SML die Variabilität der Spurengasflüsse beeinflusst.
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