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Flooding of dry sediments is known to trigger pulses of microbial respiration at land-water-interfaces. The regulation of discharge variability is therefore proposed to affect the respiration balance of these sites. In this study, I assessed the impact of discharge regulation on microbial respiration associated to surface sediments at a land-water-interface of the river Spree. I developed a theoretical model, based on empirical respiration data, to estimate the two-month total respiration at the study site for three discharge scenarios. The real scenario represented the actual discharge at the study site, which was regulated by the Spremberg reservoir dam. In the unregulated scenario, the regulating effect by the dam was excluded. In the extremely regulated scenario, a hypothetical constant discharge was modeled. For each scenario, the daily discharge, the corresponding flooded areas, the extent of dry or rewetted areas, and the durations of flooding or rewetting by rain at the study site were determined. Microbial respiration rates associated to surface sediments were measured with a respirometer under flooded, dry, and rewetted conditions. The model applied these rates to the respective flooded, dry or rewetted areas of the study site, to calculate the daily areal respiration. In all sediments from the land-water-interface, a distinctive respiration pulse was measured on the first day of flooding, and higher respiration rates under flooded than under dry conditions. The discharge of the unregulated scenario was characterized by a higher variability and larger flow volume than the regulated real scenario. Due to the higher total discharge, larger areas were flooded in the unregulated scenario, the total respiration from sediments under long-term flooded conditions was therefore higher. Moreover, the daily extent of flooded areas fluctuated more strongly, hence more short-term respiration pulses upon flooding were triggered than in the real regulated scenario. The calculated total two-month respiration of the unregulated scenario exceeded that of the regulated real scenario by almost 14 %. These results suggest that discharge regulation can have a considerable negative impact on sediment-associated microbial respiration at land-water-interfaces.
Processes of microbial carbon transformation and accumulation during initial stream succession were investigated. Studies were carried out in the experimental watershed Chicken Creek, constructed to investigate ecosystem succession, and additionally in experimental flumes simulating sand-bed streams. In a one year investigation, microbial respiration in soils and sediments along the hydrologic flow path of three stream corridors in the Chicken Creek watershed was measured. Contrary to expectation, respiration rates of rewetted soil and sediment from dry stream channels were similar to rates measured with sediments collected in the perennial channel sections. This suggested that permanent water availability was not a main factor determining metabolic potential in this early successional watershed. In an outdoor flume experiment it was determined whether shallow (1cm) and deep (4cm) sediment disturbances in small sand-bed streams have similar effects on whole-stream metabolism, and whether autotrophic and heterotrophic processes and organisms respond in similar ways. Results suggested that disturbing sediments during early successional stages had no effect on whole-stream metabolism, whereas in advanced stages, deep but not shallow sediment disturbance could lead to a transitory shift towards heterotrophy. Changes in riparian and in-stream vegetation during stream succession come along with different amounts and types of organic matter input in stream ecosystems. It was tested to determine if increasing quality and quantity of litter input changes whole-stream metabolism and activity and structure of microbial communities associated with sediments and leaves. Whole-stream metabolism was found to be similar in all treatments because sediments and leaves were constrained by oxygen and nutrient availability. There seemed to be compensation between the effect of algae fueling microbial activity in open-land treatments and microbial use of allochthonous carbon sources in the litter treatments. Fungal and bacterial activity associated with leaves was unaffected by the background litter standing stock, but the structure of communities was affected. However, leaf quality had a clear effect on microbial activity and community structure with higher activity on tree compared to grass leaves.