Working Programme
The sediment cores of the Lake Stadtsee will be sampled for the planned investigations in approx. 5 annual sections. If possible, special events recorded in historical written sources will be resolved to the exact year.
The working concept of the project follows a so-called multi-proxy approach, i.e. sedimentological, biochemical and biological parameters of the lake sediments are used as indirect indicators (proxies) for past changes and analysed together in the sense of a comprehensive environmental reconstruction.
Precise dating is necessary to enable a high-resolution reconstruction of environmental conditions. Lake sediments are usually dated using the radiocarbon method on large plant remains. This serves as the basis for creating an age model of the sediments. In addition, the period from the Middle Ages to the Early Modern Period is recorded in detail in order to obtain an exact varve chronology. The varve counting carried out here makes it possible to date the sediment section exactly. Since laminated sedimentary sections are embedded in unlaminated older and younger sequences, the varve chronology is referred to as floating. By linking it to historical events and its high chronological accuracy, the floating varve chronology can be transformed into an absolute (varve) chronology.
In addition to natural processes, anthropogenic environmental changes are archived in the lake. Since Lake Stadtsee is very closely linked to the city of Bad Waldsee and the surrounding area, information about local and regional effects of climate changes in the direct living environment of humans as well as about the development of the city and the surrounding countryside is stored in the sediments. In Bad Waldsee, the sediments of Lake Stadtsee illustrate the special situation of increased anthropogenic influence on the water body from the Middle Ages at the latest.
The development of the city is expected to be indirectly reflected in the lake sediments through wastewater discharges (pollutants), soot inputs and hydrological interventions.
Inputs of persistent pollutants such as heavy metals and organic pollutants to the lake are determined using various geochemical methods. Polycyclic aromatic hydrocarbons (PAHs) from combustion processes and urban fires are deposited as thin layers of soot or ash in the sediment. Specific PAH
patterns can be used to determine the sources of origin. The analyses are carried out by means of gas chromatography (GC-MS).
Heavy metals can enter the lake through medieval metal processing, textile production as well as dyeing and tanning. By means of inorganic geochemical investigations (ICP-MS, XRF) and sequential extraction, the metal species and bioavailability can be determined. The aim is to verify whether extensive environmental pollution with pollutants was already caused by anthropogenic activity in the Middle Ages and which activities were associated with it.
Weather conditions and climatic trends are also archived by the lake sediments. Extreme events change the sediment facies and are determined using thin sections from representative sections. Weather events such as floods lead to the formation of coarse-grained clastic layers in the sediment, which are determined by microscopic examination of the thin sections. Flood frequencies over several centuries can be derived from the frequency of these layers.
The mineral composition of the sediment is derived from μXRF scans of the sediment cores. Increased contents of elements such as silicon, titanium and aluminium provide evidence of increased clastic external material input into the lake. In general, this is due to increased soil erosion in the catchment area caused by forest clearing, urban construction activity or intensification of agriculture or land use change. With the help of further information from the historical written archives, possible effects and causes of increased soil erosion can be deduced.