@phdthesis{Ramm2014, author = {Ramm, Jessica}, title = {Occurrence and life-cycle strategies of bloom-forming Nostocales (cyanobacteria) in deep lakes in Northern Germany and in Lake Kinneret, Israel}, url = {http://nbn-resolving.de/urn:nbn:de:kobv:co1-opus4-31729}, school = {BTU Cottbus - Senftenberg}, year = {2014}, abstract = {Nostocalean cyanobacteria differentiate heterocysts to fix dissolved nitrogen (N2) and dormant cells (akinetes) to survive harsh environmental conditions. The distribution and proliferation of Nostocales and their hibernation strategies in deep stratified lakes of different trophic states and climate zones were investigated. Studies were carried out in the meso-eutrophic Lake Kinneret (Israel) and in the mesotrophic Lake Scharm{\"u}tzelsee and the oligo-mesotrophic Lake Stechlinsee (Germany). The spatio-temporal distribution of akinetes in sediments was analysed. The abundance in the sediment surface increased with water depth and differed due to basin morphometry. Light and temperature distribution revealed shallow areas of sedimentary akinete pool as a potential inoculum to contribute to the formation of a pelagic population. Hence, a small viable akinete pool was deposited in shallow sediments. A CARD-FISH protocol was implemented to identify and quantify the akinetes in sediments. Tested Nostocales strains and akinetes in sediment samples were successfully labelled with 16S rRNA targeted probes and microscopically detected by their fluorescence signal. Akinete enumeration in field samples confirmed the suitability of the CARD-FISH approach. Species- or genus-specific differences in the overwintering strategies of Nostocales were observed. Akinetes were the only overwintering form of Anabaena spp. On the other hand, Aphanizomenon flos-aquae overwintered as vegetative filaments in the pelagial of Lake Stechlinsee. In the other lakes studied, Aphanizomenon spp. performed an intermediate life cycle, with akinetes and a small pelagic population in winter. This suggested that Aphanizomenon spp. had another overwintering strategy contrary to the exclusively dormant strategy of Anabaena spp. Putative strains of cylindrospermopsin (CYN)-producing Aphanizomenon ovalisporum were isolated from Lake Kinneret. Their morphologic and phylogenetic diversity, as well as the presence of CYN-encoding gene cluster and CYN production, were analysed. Four of the six strains were assigned to Anabaena bergii. Although all the isolated strains possess at least fragments of CYN gene cluster, no CYN production was detected. Non-CYN-producing Aphanizomenon ovalisporum strains and the presence of non-toxic Anabaena bergii in Lake Kinneret have not been reported before. This suggested that toxic and non-toxic Nostocales strains can coexist in lakes.}, subject = {Cyanobacteria; Cylindrospermopsin (CYN); Lake sediment; Akinetes; Cyanobakterien; Lebenszyklusstrategien; Akineten; Seesediment; Cylindrospermopsin (CYN); Life-cycle strategies; Brandenburg; Israel; Seesediment; Cyanobakterien; Klimazone; Lebensdauer}, language = {en} } @phdthesis{Belyaeva2013, author = {Belyaeva, Maria}, title = {Effects of multiple abiotic stressors on the species and genetic biodiversity of littoral Cladocera in two types of acidic habitats in Germany : hard-water mining lakes and soft-water bog lakes}, isbn = {978-3-8440-2391-6}, url = {http://nbn-resolving.de/urn:nbn:de:kobv:co1-opus-29373}, school = {BTU Cottbus - Senftenberg}, year = {2013}, abstract = {Ecological research on acidic lakes has historically focused on soft-waters, whereas biota in natural and man-made acidic hard-water lakes remains poorly studied. My thesis deals with the effects of multiple abiotic stressors on species and genetic biodiversity of littoral Cladocera in two types of acidic waters in Germany: hard-water mining and soft-water bog lakes. I found that these two types of acidic lakes supported highly distinct cladoceran communities, both with respect to their species diversity and composition, what led to the rejection of my null hypothesis that pH was the only abiotic factor, determining species diversity patterns. Further analyses revealed that, apart from pH, TDS-related parameters and trophy significantly affected species composition of littoral Cladocera in the studied lakes. Particularly the role of TDS and its constituents for colonization of acidic lakes was virtually neglected by previous studies, based on soft-water lakes' data sets. My study on the genetic diversity of a generalist cladoceran Chydorus sphaericus provided evidence for genetic erosion, i.e. negative effects of abiotic stress in the acidic hard-water mining lakes, but not in the acidic soft-water bog lakes. I conclude that the observed genetic erosion in acidic mining lakes may have negative long-term consequences for population persistence even in broadly tolerant species. In general, biodiversity at both species and genetic levels was much more impaired in the acidic hard-water mining lakes, compared to the naturally acidic soft-water bog lakes. This was possibly due to both ecological (higher abiotic stress) and evolutionary (insufficient time for long-term adaptations to evolve) mechanisms. My results suggest that colonization of acidic hard- and soft-water lakes in each case should require specific physiological adaptations at both species and population levels. The practical relevance of my studies is that they provide the scientific basis for monitoring of acidic hard-water mining lakes based on littoral Cladocera. Especially genetic diversity proved a valuable indicator of water quality in acidic mining lakes, as it provided unique information on population-level responses, being complementary to species diversity assessment. Overall, my results demonstrate that inclusion of acidic hard-water lakes into the research framework as well as comparisons among communities in chemically diverse acidic lakes can result in important new insights, concerning the community organization and adaptations in acidic environments.}, subject = {Brandenburg; Chydoridae; Bergbaurestsee; Bioindikation; Extreme Lebensr{\"a}ume; Saure Tagebauseen; Bioindikation; Evolution{\"a}re Toxikologie; Chydoridae; Extreme environments; Acidic mining lakes; Bio-indication; Evolutionary toxicology; Chydoridae}, language = {en} } @phdthesis{Baptista2012, author = {Baptista, Melissa}, title = {Phytoplankton succession and diversity-productivity relation in German and Brazilian shallow lakes}, url = {http://nbn-resolving.de/urn:nbn:de:kobv:co1-opus-24386}, school = {BTU Cottbus - Senftenberg}, year = {2012}, abstract = {Phytoplankton succession linked to productivity-diversity relationship at steady-state/non steady state conditions, mixing events as predominant disturbance in sense of Connell (1978) and influence of conditional differentiation (temperature) on phytoplankton diversity were investigated. Water samples were taken two times a week in 4 German shallow lakes in Brandenbug region (Melangsee, Petersdorfer See, Wolziger See, and Langer See) from 2007 to 2010 and in 2009/2010 during cold and rainy season in a Brazilian coastal lagoon Peri. A comparison between literature data from 4 Brazilian lakes, in order to investigate the influence of temperature on diversity and dynamic of phytoplankton species was also done. The cyanobacterial species dominated all studied lakes and the mixing had a positive effect on the supremacy of this group in tropical lakes. The high biovolume of cyanobacteria contributed to the achievement of steady state conditions in sense of Sommer et al. (1993) during consecutive periods in Petersdorfer See and in Peri lagoon practically during all phases. The monodominance of Cylindrospermopsis raciborskii was observed in warm water, under no stratification regime. Oscillatoriales of group S1 (Reynolds 2002), represented by Limnothrix redekei and Pseudanabaena limnetica, typical in turbid mixed layers and with high nitrogen affinity, were typical in Petersdorfer See. In Melangsee, steady state was observed during colder periods under dominance of Bacillariophyceae and Chrysophyceae. Lower diversity coincided with steady state conditions and higher values of resource use efficiency (RUE), while higher diversity occurred mainly at transitional state during the spring in temperate lakes, supporting the non-equilibrium concept (Hutchinson 1961) at lower RUE values. Higher biovolume occurred mainly during the late summer in temperate lakes under dominance of cyanobacteria, and/or at steady state. Concerning the temporal variation of phytoplankton, the highest peak of species richness preceded the resource use efficiency, suggesting the productivity as consequence of diversity. The richness was much higher in temperate shallow lakes, which were more similar to each other in terms of seasonality, species number and biovolume. A positive correlation between richness and biovolume of temperate lakes was found and the opposite was observed in tropical lakes. The biovolume and richness in tropical lakes were more variable and in temperate lakes presented higher richness at intermediate level of biovolume (annual mean from 10 to 18 mm3/l). Low level of biodiversity allows an ecosystem to function under constant conditions, but a greater biodiversity occurred in fluctuating environments.}, subject = {Brandenburg; Brasilien; Flachsee; Phytoplankton; {\"O}kosystem; Phytoplanktondiversit{\"a}t; Prim{\"a}rproduktion; Phytoplanktonsukzession; Paradoxon des Phytoplankton; Steady-state; Phytoplankton diversity; Succession; Primary productivity; Paradox of phytoplankton}, language = {en} }