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During open-cast lignite mining in Lusatia (NE Germany), iron sulfide minerals associated with lignite, are exposed to air and weather. The weathering products iron (Fe), sulfate and acids subsequently enter the fluvial-lacustrine system Spree and its tributaries.
The aim of this work was to identify and explain the evolving biogeochemical signatures (spatio-temporal patterns) in River Spree. These signatures are significantly influenced by biogeochemical turnover processes triggered by iron input. To identify the signatures, a regional field study was conducted from the inland delta Spreewald to the mouth. This study was followed by two laboratory experiments under controlled redox conditions to investigate the effect of Fe on the long-term binding of phosphorus and the degradation of particulate organic material in the iron-enriched sediments.
Characteristic elements introduced by lignite mining (iron, sulfur, aluminum, cobalt, nickel) and by urban areas (zinc, lead, copper, chromium) could be determined by means of a principal component analysis. Based on these findings, the impact range of the open-cast mining was determined to be at least ~ 90 km downstream of the Spreewald. Within the urban-influenced systems Fürstenwalde and Berlin, the urban signature is more dominant than the mining signature. By means of sequential extractions and XRD analyses of the sediments, iron binding forms and characteristic iron minerals have been additionally identified (e.g., Fe(III) oxyhydroxides, pyrite, vivianite).
Sediment analyses and column experiments have shown that iron increases the phosphorus sorption and decreases the phosphorus release in the sediments of three studied lakes of the fluvial-lacustrine system. However, the application of different phosphorus retention models for Lake Neuendorfer See showed that Fe cannot reduce the eutrophic state of the lakes along the river, since the water retention times are too short and the external phosphorus loads are too high. Additionally, lake sediments with different Fe contents have been incubated with particulate organic material. Higher Fe contents resulted in reduced emissions of the greenhouse gases CO₂ and CH₄, which can be attributed to a reduced degradation of organic matter by Fe. Possible reasons include sorption processes of (dissolved) organic matter onto Fe oxyhydroxides and toxic effects of iron on microorganisms. Nevertheless, Fe (and sulfate) are available as electron acceptors during the decomposition of organic matter in River Spree.
The findings of this work deepen the understanding of the impact of iron from mining on sulfur, phosphorus and carbon turnover processes in fluvial-lacustrine systems. As a consequence of the Fe input from the Lusatian area, the signature will persist for decades in River Spree.
Intermittent rivers and ephemeral streams (IRES) experience drying events, and they are becoming increasingly common due to climate change and anthropogenic water withdrawal. Despite their prevalence, IRES have been less studied than non-drying rivers, and more research is needed to understand their dynamics. This dissertation examines drying events' effects on the sediment microbial community structure and biogeochemistry in temperate IRES. First, a research study was carried out using an outdoor mesocosm setup to track changes in bacterial and fungal communities, microbial functions and properties of sediment-dissolved organic carbon during three different drying events. Results showed that drying duration and intensity and sediment organic matter content regulated river Spree sediment microbial community composition and biogeochemical processes during drying. The associated sediment respiration, assessed as CO2 flux, rapidly declined during all drying treatments, and Bacilli class became the most dominant bacteria after 90 days of drying, except in non-enriched sediment under the most intense drying. Second, a microcosm experiment was conducted to understand how sediment drying history and properties influence biogeochemical dynamics during an IRES expansion phase. Sediment respiration and nutrient release/retention rates were measured through flow resumption, and results showed that drying duration and intensity and sediment organic matter content regulated the dynamics of nutrients and respiration upon flow resumption. Under the most intense and prolonged drying, non-enriched sediment showed a lag response in respiration during the first day after flow resumption, while all other treatments had either a linear increase or a fast pulse in respiration. Finally, the long-term microbial succession in IRES sediment and soil in the experimental catchment of Chicken Creek was investigated. In 2008 and 2018, the sediment of three ephemeral streams and their adjacent soil was analyzed for the structure of the bacterial and fungal communities and microbial functions across different seasons. Results showed that environmental factors, such as vegetation type and organic matter content, mediated sediment and soil microbial succession in Chicken Creek. Ephemeral streams under spare and sporadic flow events remained unique ecosystems with distinctive microbial communities and biogeochemical dynamics, different from its riparian soil. Overall, this dissertation concludes that temperate IRES are dynamic ecosystems where dry-wet cycles and environmental factors modulate their sediment microbial community structure and function trajectories in the short- and long term.
Indawgyi Lake is one of the largest lakes in East Asia. Due to its habitat diversity and its great importance for international bird migration, it has the status of an UNESCO biosphere reserve. In the last decades, anthropogenic pressures on the lake due to increasing population numbers, overfishing and intensification of agriculture and forestry as well as to the impacts by artisanal small-scale gold mining in the catchment area have increased sharply. As a result of gold mining, lake inflows have very high suspended matter loads, both from the washing of gold-bearing sediments and from soil erosion as a result of the destruction of the floodplain and of the forest close to the river. The input of sediments and suspended matter from the Hkaung Tung Hka Chaung River has led to massive deposits of river sediments in the southern part of Indawgyi Lake within a few years.
In the context of short-term investigations and a one-year monitoring close to the stream mouth, the extent of the suspended matter input from Hkaung Tung Hka Chaung River into Indawgyi Lake was estimated and heavy metal pollution concentrations of the suspended matter were measured as a basis for recommendations for the reduction of the pollution pressure on the lake.
Sedimentation analyses showed that the river water was still very turbid even after 50 hours due to high concentrations of very small solids. In contrast, material in the size of sand grains settled completely after about ten hours. The clay fraction of the suspended matter was heavily contaminated by different heavy metals, including cadmium, copper, nickel, chromium and lead.
The load of suspended matter was subject to strong fluctuations and showed no correlation with the discharge. The mean concentration of suspended matter was 9.6 g/L (as dry weight per volume of water). The daily dry matter load in Hkaung Tung Hka Chaung River varied between 2.3 and 2,900 t. The mean load was 359 t/d, with by far the largest amount being transported by the river during the rainy season during times of high discharge. That indicates that, in addition to direct inputs from mining activity, there was also suspended matter input from soil erosion and from the remobilization of river sediments. The estimates of the annual input into Indawgyi Lake came to an amount of about 133,000 t. This corresponds to a volume of the fresh matter between 0.26 and 0.4 million m³.
The results show the urgent need for a control of the artisanal small-scale gold mining activities and for the building of sedimentation basins at Hkaung Tung Hka Chaung River to protect Indawgyi Lake with its highly valuable ecosystem.
In-stream microbial carbon transformation under opposing stresses - drought and sediment transport
(2018)
The mineralization of organic matter (OM) is an important ecosystem service that has come under pressure because of increased frequency of droughts and higher sediment loads in running waters. In particular, lowland streams in temperate regions may experience reinforced sediment transport through migratory ripples and changes of naturally sorted sand and gravel in streambeds towards sand-dominated, homogenized streambed structure. The impact on microbial carbon (C)-transformation from these changes was the main focus of my doctoral thesis, in particular the impact of (i) periodic mechanical disturbance associated with ripple migration (ii) streambed structure homogenization, and (iii) drought in streambeds with sorted or homogenized sediment structure.
In a set of microcosms, the significance of periodic mechanical disturbances for microbial C-transformation was tested. Thereby, the quantity and quality of the OM in the sandy sediments were varied by the addition of leaves and fish feces to the OM-poor sands. The results revealed that periodic mechanical disturbances resulted in significant decrease in microbial respiration to a low and similar level regardless of OM quality contained in sand.
The importance of the streambed structure (sorted vs homogenized) for C-transformation was tested using set of experimental streams. The focus was on the interaction between benthic and hyporheic microbial processes in C-transformation to better understand the consequences of streambed homogenization on microbial function. The results showed that sediment structure determines connectivity between the benthic and hyporheic zones. The lower water exchange in homogenized streambeds and thereby reduced supply of freshly produced bioavailable OM from the benthic to the hyporheic zone, curtailed microbial respiration in the latter affecting the water quality.
The influence of a drought and rewetting was tested on C-transformation in streambeds with a sorted or homogenized sediment structure using experimental streams where one half of the streams were strongly shaded and the other half moderately shaded. The results showed that streambeds affected by droughts, either with sorted or homogenized sediment structure have a similar microbial activity at the first place controlled by shading, whereas microbial composition during drought and its recovery after rewetting was additionally affected by sediment structure.
Overall, this doctoral thesis showed that in sediment transport– and drought-impacted streambeds (i) ripple migration results in decreased C-transformation regardless of the available quality of OM, (ii) homogenization of sorted sediment structure leads to a decrease in microbial C-transformation in the hyporheic zone, and (iii) interaction between sediment structure and shading alters microbial community composition especially critical for resistance and resilience of C-transformation during drought and rewetting.
In order to lower the phytoplankton biomass in lakes it is theoretically most effective to reduce the nutrient that is actually limiting. However, it is widely assumed that the abundance and N₂-fixation rate of N₂-fixing cyanobacteria (Nostocales) would increase in response to reduced N loading, and thereby render efforts to improve water quality by N reduction ineffective. Nostocales N₂-fixation has a huge energy demand and consequently the light intensity may affect the response of Nostocales biovolume and N₂-fixation to varying N additions. This led to the following aims, for which three different sets of experiments were conducted.
(i) Determination of the seasonal dynamic of N- and P-limitation for four lakes of differing lake types in the German lowlands and testing the power of four N:P ratios to predict the limiting nutrient: Biweekly experiments were performed in 4 lakes differing in lake. For the shallow lakes there was a trend from P limitation in spring to N or light limitation in summer and autumn, while the deep lake remained predominantly P limited. The ability of in-lake N:P ratios to predict the relative strength of N vs. P limitation was tested using linear regression. All four N:P ratios had significant positive relationships with the response ratio to N and P additions, but the TN:TP and DIN:TP ratios performed best. Nitrogen limitation was predictable, frequent and persistent, suggesting that nitrogen reduction could play a role in water quality management.
(ii) Determination of the response of Nostocales biovolume and N₂-fixation to varying N additions: To achieve this, an experiment with water from an N limited lake (LAN) was conducted. While the Nostocales biovolume did not respond to varying N additions, the N₂-fixation increased in low N microcosms. To quantify the extent to which Nostocales compensated for the varying N addition rate, we calculated a compensation rate (CR). By the end of the experiment a CR of 36 % was reached. However, at biovolumes typical for summer in LAN the CR would be much lower. Therefore, in shallow polymictic lakes like LAN, reduced N loading may lower both in-lake N concentrations and biovolumes of non-fixing phytoplankton without significantly impacting Nostocales biovolume.
(iii) Determination of the effect of the light intensity on the response of Nostocales biovolume and N₂-fixation to varying N additions: To accomplish this aim another microcosm experiment with water from LAN was conducted. While at low and intermediate light intensities the reduction of N addition had no effect on Nostocales biovolume, at high light intensities it led to an increase. The N₂-fixation increased at all light intensities when N addition got reduced. This positive response to a reduction in N addition increased with light, showing that Nostocales may take advantage of being able to fix N₂ mainly at high light intensities.
Nostocales form thick-walled, resting cells (akinetes) for overwintering in lake sediments of Central Europe. The pelagic Nostocales population recruits after the germination of akinetes, which mainly takes place in the spring with increasing temperatures and light intensities. The study aimed to i) characterize the sediment surfaces inhabited by viable akinetes that potentially contribute to the formation of a pelagic population, and ii) estimate the inoculum size of the available sedimentary akinete pool. We investigated the horizontal distribution of akinetes in sediments and the seasonal course of light and temperature in two deep dimictic lakes (Lake Stechlinsee, max. depth 69 m and Lake Scharmützelsee, max. depth 29.5 m; NE Germany). The akinete pool was calculated and the potential inoculum was estimated using assumed light and temperature data for akinete germination. The akinete abundance in sediments depended on the basin morphometry and increased with water depth. Only a small proportion of the viable akinete pool in shallow water areas contributed as inoculum to pelagic population. The potential inoculum size in Lake Scharmützelsee was larger than in Lake Stechlinsee.
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.
The ability to fix molecular nitrogen is considered to be a competitive advantage of Nostocales to overcome periods of nitrogen shortage but it is unclear to what extend these cyanobacteria import nitrogen into freshwaters and if they are able to compensate the efforts of reducing anthropogenic nitrogen input.
We studied nitrogen fixation, cyanobacterial biovolume and species composition and abiotic parameters in two polymictic lakes (Germany) over three years. Although Nostocales were present from April to November N2-fixation was found only from June/July to September. In the summer months, it amounted up to 40 mgN m-²d-¹ or up to 500 mgN m-²d-¹ resulting in rather low annual N-inputs between 0.1 and 8 gN m-²a-¹. We found a high variation in N2-fixation rates between the two lakes and the years, which could neither be explained by total Nostocales biovolume nor heterocyte numbers. N2-fixation rates measured in the field will be analyzed on Nostocales species level, be compared to those of laboratory cultures and be discussed in the context of possible phosphorus or light limitation of Nostocales.
Many lake water bodies not attained the goal of the European Water Framework Directive (WFD) to achieve a good ecological state by 2015. This is, among other things, because the assessment and improvement of hydromorphological conditions of lakeshores has been neglected as an important component ensuring the ecological integrity of lake ecosystems. In recent years, macroinvertebrates were emphasized to be useful indicators for the assessment of lakeshore hydromorphology. Hence, in Europe macroinvertebrate-based assessment methods were developed to evaluate the hydromorphological conditions of lakeshores.
In this thesis, some of the uncertainties and missing aspects of existing macroinvertebrate-based assessment methods were addressed. The results were obtained by sampling macroinvertebrates and macrophytes at natural shores and at shores modified by marinas and beaches in three depth zones between April and November 2011 in a large lowland lake (Lake Scharmützelsee, Germany).
Firstly, I clarified that upper littoral macroinvertebrates should be used for assessing the hydromorphology of lakeshores. It was shown that the effect of lakeshore modification on macroinvertebrate diversity and community composition was most pronounced in the upper littoral and decreased to the profundal zone. Secondly, I demonstrated that a single seasonal sampling is sufficient to capture the compositional differences of macroinvertebrate communities associated with human lakeshore modification. Seasonal effects on upper littoral macroinvertebrate diversity and composition were less important than shore type in comparison with the middle littoral and profundal zone. Thirdly, upper littoral macrophyte communities were also affected by lakeshore modification and at the same time the most important variable structuring macroinvertebrate communities. Hence, the effects of different shore types on macrophytes were transferred to macroinvertebrates, but artificial substrates were also able to partly substitute macrophyte habitats as it was shown for the studied marinas. Since lakeshore modification affected macrophytes slightly differently than macroinvertebrates, macrophytes should be considered as an additional component in lakeshore assessment. Finally, secondary production as proxy to determine the effect of lakeshore modification on the functioning of macroinvertebrates was estimated. Estimation of secondary production requires the determination of biomass. Biomass was indirectly determined by using length-mass regressions established for macroinvertebrates from temperate lakes of the central European lowland. The result showed that total secondary production and secondary production of native taxa in the upper littoral was substantially lower at the studied beaches compared to natural sites. In contrast, upper littoral secondary production at marinas did not differ to natural sites, but secondary production of non-native taxa was significantly higher at marinas. No effects of lakeshore modification on secondary production were found with increasing depth. Different scenarios based on upscaling of site-specific production to whole lake ecosystem level gave evidence that the observed local impacts of lakeshore modification can translate into alterations of the functioning of macroinvertebrates at whole lake ecosystem level. In addition, it was emphasized that secondary production as a functional measure is more sensitive in detecting hydromorphological alterations than the structural measures diversity or biomass. Secondary production should therefore be included in existing lakeshore assessment methods. In order to obtain a comprehensive overview about the changes in the functioning of macroinvertebrates following lakeshore modification, it is recommended to consider not only total secondary production but also secondary production of functional groups. With these results, this thesis contributes to the mechanistic understanding of the effect of lakeshore modification on the functioning of macroinvertebrates and the consequences for the functioning of the whole lake ecosystem. The newly generated knowledge helps to optimize the development of successful lakeshore assessment tools and identification of management measures.
The main goal of this dissertation was to explore the interactions between the hydrogeomorphology of the streambed in sandy lowland low-order streams and the microbial community inhabiting it. In particular, (i) the influence of the vertical water exchange across the streambed and (ii) of the sediment transport on the function and structure of the streambed microbial community, (iii) and the potential of the microbial community to influence these physical factors were explored. The influences were studied with a model system approach (micro- and mesocosms).
Firstly, I examined the significance of vertical water exchange across the streambed for the microbial community. I determined the differences in the microbial community structure and function associated with sediments of differing grain sizes. The grain sizes differed in surface-to-volume ratio and hydraulic conductivity. The results revealed vertical water exchange as the major factor for the structure and function of the microbial community.
Secondly, I studied the ability of the microbial community to influence the vertical water exchange across two sandy streambeds: leveled and rippled. My results showed that the microbial community can reduce and even block the vertical water exchange by reducing pore space with gas bubbles formed due to high primary production.
Thirdly, I determined the effect of short-term sediment transport events on the function of the microbial community and on the influence of the microbial community on vertical water exchange. The results show that the mechanical stress associated with short-term sediment transport events does not influence the microbial community function. However, a single short-term sediment transport event increased vertical water exchange by (i) releasing the gas bubbles produced by the microbial community and (ii) creating irregularities in the flume bed.
Lastly, I ascertained the potential of benthic algal mats to transport sediment by means of buoyancy-mediated detachment from the bed. The results revealed the detachment of algal mats as a novel mechanism of sediment transport during low-flow periods. Overall, the interactions studied show that in sandy streambeds (i) the pattern of vertical water exchange is the primary physical template for the microbial community, and (ii) the activity of the microbial community and sediment transport are stochastic sources of spatiotemporal heterogeneity in vertical water exchange. These results contribute to the understanding and prediction of stream ecosystem functions in sandy streams, which is of special significance in light of the increase in fine sediment load in streams worldwide.