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- Institut für Integrierte Naturwissenschaften, Abt. Biologie (29) (entfernen)
Amphibian populations are declining worldwide for multiple reasons such as habitat destruction and climate change. An example for an endangered European amphibian is the yellow-bellied toad Bombina variegata. Populations have been declining for decades, particularly at the northern and western range margin. One of the extant northern range centres is the Westerwald region in Rhineland-Palatinate, Germany. To implement informed conservation activities on this threatened species, knowledge of its life-history strategy is crucial. This study therefore focused on different developmental stages to test predictions of life-history theory. It addressed (1) developmental, (2) demographic and (3) genetic issues of Bombina variegata as a model organism: (1) Carry-over effects from larval environment to terrestrial stages and associated vulnerability to predators were investigated using mesocosm approaches, fitness tests and predation trials. (2) The dynamics and demography of B. variegata populations were studied applying a capture-mark-recapture analysis and skeletochronology. The study was complemented through (3) an analysis of genetic diversity and structuring of B. variegata populations using 10 microsatellite loci. In order to reveal general patterns and characteristics among B. variegata populations, the study focused on three geographical scales: local (i.e. a former military training area), regional (i.e. the Westerwald region) and continental scale (i.e. the geographical range of B. variegata). The study revealed carry-over effects of larval environment on metamorph phenotype and behaviour causing variation in fitness in the early terrestrial stage of B. variegata. Metamorph size and condition are crucial factors for survival, as small-sized individuals were particularly prone to predator attacks. Yellow-bellied toads show a remarkable fast-slow continuum of the life-history trait longevity. A populations’ position within this continuum may be determined by local environmental stochasticity, i.e. an extrinsic source of variation, and the efficiency of chemical antipredator protection, i.e. an intrinsic source of variation. Extreme longevity seems to be an exception in B. variegata. Senescence was absent in this study. Weather variability affected reproductive success and thus population dynamics. The dispersal potential was low and short-term fragmentation of populations caused significant genetic differentiation at the local scale. Long-term isolation resulted in increased genetic distance at the regional scale. At the continental scale, populations inhabiting the marginal regions were deeply structured with reduced allelic richness. As consequence of environmental changes, short-lived and isolated B. variegata populations at the range margin may face an increased risk of extinction. Conservation measures should thus improve the connectivity among local populations and reinforce annual reproductive success. Further research on the intraspecific variation in B. variegata skin toxins is required to reveal potential effects on palatability and thus longevity.
Nandi forests (South and North Nandi forests) are situated in the Rift Valley Province of Kenya very close to Kakamega forest. From previous documents it has been seen that Kakamega and Nandi forests were connected to each other forming one big "U" shaped forest block till the beginnings of 1900s. Due to human pressures, currently there are three different forests form the previous one block forest. Although they were one forest, information on Nandi forests is very scanty when it is compared to that of Kakamega forest. The species composition and diversity as well as plant communities and population structure of Nandi forests have not been studied. Information is not available about the similarity status of South and North Nandi forests. Furthermore the natural regeneration potential (seedling bank) of these forests is not well studied and documented. Hence this study aims to fill these gaps.
In this study totally 76 quadrates (49 from South Nandi and 27 from North Nandi) were used to collect data. In the South Nandi forests 27 of the quadrates were laid in the better side of the forest (at Kobujoi) and the remaining 22 were in the heavily disturbed part of this forest (Bonjoge). The quadrates were arranged on transects that have one to one and half km which were parallel to the slope. The distance between the quadrates was 100 meter and transects are 500 m apart. The size of the main quadrate was 400 m2 (20 X 20 m) which also had five small plots (3 X 3 m) distributed on the four corners and in the center. Each woody plants (climbers, shrubs and trees) having more than one meter and greater than two centimeter diameter at breast height (dbh) were measured and recorded. Seedlings and herbaceous plants were sampled in the smaller plots. Individual plants were identified at species level and when it was not possible to identify in the field voucher specimen were prepared and latter identified at the East African Herbarium, National Museum of Kenya, and Nairobi. Clustering and ordination were performed using PC-ORD and CANOCO ecological softwares, respectively. For both clustering and ordination abundance data of the species was used. Shannon diversity index and evenness were computed using PC-ORD while similarity indices, Fisher alpha, rarefaction, species richness estimation (nonparametric species richness estimators) were conducted using EstimateS. Indicator species analysis was undertaken using PC-ORD. Basal area and height class distribution at forests level or site level (Bonjoge and Kobujoi) and diameter (dbh) class distribution for selected trees species were performed to evaluate population structure.
Furthermore importance value (IV) of woody plant species was calculated. SPSS version 16 was used to undertake both parametric (when data assume normal distribution) and nonparametric (when data are not assuming normal distribution) comparison of means, correlation and regression analysis.
In this study totally 321 vascular plant species comprising 92 families and 243 genera were identified in Nandi forests (both South and North Nandi forests). In South Nandi forest 253 plant species form 82 families and 201 genera were recorded while in North Nandi 181 species comprising 67 families and 155 genera were recorded. Jackknife second order estimators gave the highest species richness estimate for both South and North Nandi forests i.e. 284 and 209, respectively. In the case of highly disturbed and less disturbed parts of South Nandi forest 138 and 172 vascular plant species were recorded, respectively. Asteraceae, Rubiaceae and Euphorbiaceae are the top three species rich families of Nandi forests. In terms of different diversity measures (i.e. alpha and beta diversity, Fisher alpha, Shannon diversity and evenness indices) South Nandi is more diverse than North Nandi forest. Sörensen and Jaccard (classic) as well as their respective abundance based similarities showed that there is a low species similarity between South and Nandi forests. The cluster analysis resulted in three different plant communities and this result is supported by the ordination result.
South and North Nandi forest has inverted "J" height class distribution showing that larger proportion of woody plant individuals are found in the lower height classes. Similar pattern is observed when the diameters of all woody plants were considered together. However, different diameter class distributions (seven types) were identified when selected tree species were analyzed separately. It has been observed that the basal area of South Nandi forest is significantly lower than that of North Nandi forest (Mann-Whitney U =358, p < 0.001). Similarly Bonjoge has significantly lower basal area (t-value=3.77, p<0.01) than that of Kobujoi. Number of woody plat seedlings in South Nandi forest is significantly higher than that of North Nandi (Mann-Whitney U = 362.5, p<0.001). In the same way Bonjoge has significantly smaller number of ssedlings than Kobujoi (t-value 4.24, p<0.001). Most of species in both forests are able to resprout from stumps after physical damage; hence this helps the regeneration of the forests in addition to seedling banks. This study enables to fill some of the information gaps about Nandi forests especially of floristic composition, population structure, natural regeneration and human impacts on this ecosystem.
Die Verwendung physiologischer Indikatoren, welche die Reaktion von Organismen auf Veränderungen ihrer Umwelt widerspiegeln, bietet ein großes Potenzial für ökologische Studien. Durch die Analyse des physiologischen Zustandes von Organismen ermöglichen diese Indikatoren eine schnellere Erfassung von Veränderungen in aquatischen Ökosystemen als es durch die Betrachtung ökologischer Indikatoren, wie z. B. der Struktur der Benthosgemeinschaft oder des Reproduktionserfolges einzelner Arten, möglich ist. Dieser Zeitvorteil kann sowohl die Effektivität der Habitatbewertung als auch experimenteller Studien in der aquatischen Ökologie erhöhen. In diesem Zusammenhang konzentriert sich die vorliegende Arbeit auf physiologische Messgrößen, wie die Konzentration von Energiespeicherstoffen, den zellulären Energiestatus (Adenylate Energy Charge) oder die Stoffwechselaktivität in vivo, die den energetischen Zustand oder den aktuellen Energieverbrauch von Organismen charakterisieren, sowie auf das RNA:DNA-Verhältnis als Wachstumsindikator. Obwohl diese Indikatoren in der marinen Ökologie, und in jüngerer Zeit auch in der Ökotoxikologie, regelmäßig verwendet werden, haben sie in der limnischen Ökologie bisher wenig Anwendung gefunden. Um die Anwendung physiologischer Indikatoren in diesem Bereich zu verstärken verfolgt die Dissertation zwei Ziele. Zum einen verdeutlicht sie das Potenzial der einzelnen physiologischen Indikatoren, zum anderen stellt sie Grundlagenwissen zu ausgewählten ökophysiologischen Aspekten einheimischer und gebietsfremder Arten der Ordnung Amphipoda bereit, die als Schlüsselarten aquatischer Lebensräume als besonders geeignet für die Bestimmung physiologischer Indikatoren angesehen werden. In diesem Sinne werden in Kapitel 2 sowohl die grundlegenden Annahmen, als auch die theoretischen und methodischen Grundlagen für die Bestimmung physiologischer Indikatoren aufgezeigt und ihre Anwendbarkeit in Fallstudien verdeutlicht. Die durchgeführten Experimentalstudien (Kapitel 3−5) liefern Informationen zu (i) den art- und geschlechtsspezifischen Unterschieden in der saisonalen Variation des energetischen Zustandes natürlicher Gammarus Populationen (G. fossarum, G. pulex), (ii) den Unterschieden in der Stoffwechsel- und Bewegungsaktivität verschiedener Amphipoda-Arten (G. fossarum, G. roeselii und D. villosus), sowie (iii) den direkten Auswirkungen von Ammoniak auf die Physiologie und die Bewegungsaktivität von D. villosus. In Kapitel 6 werden abschließend die grundlegenden Schlussfolgerungen aus den durchgeführten Feld- und Laborstudien, sowie ihre Relevanz und Auswirkungen für die Anwendung physiologischer Indikatoren in der limnischen Ökologie diskutiert.
The stands surveyed are among the last closed canopy forests in Rwanda. Their exploration began in the early twentieth century and is still ongoing. Previous studies were mainly concerned with plant sociological issues and presented references to environmental factors in anecdotal form, at best using indirect ordination methods. The present study undertakes a classification of the vegetation with numerical methods and establishes quantitative relationships of the species’ distributional structure to environmental parameters using spatially explicit procedures. For this purpose, 94 samples were taken in 100 m² hexagonal plots. Of these, 70 samples are from Nyungwe, 14 are from Gishwati, and 10 are from Cyamudongo. Given the homogeneity of the terrain and vegetation, all vegetation types encountered, all types of stands, and all vegetation strata were included. The beta diversity is expressed by an average Bray-Curtis dissimilarity of 0.92, and in JOST’S (2007) numbers equivalents, 37.90 equally likely samples would be needed to represent the diversity encountered. Within the survey, 1198 species in 127 families were collected. Among the specimens are 6 local endemics and 40 Albertine Rift endemics. Resulting from UPGMA and FCM-NC, 20 to 40 plant communities were established depending on the level of resolution. It can be inferred by means of a Mantel correlogram that the mean zone of influence of a single vegetation stand, as sampled by a 100 m² plot in Nyungwe Forest, ranges between 0.016 and 3.42 km. Of the communities compiled using FCM-NC and UPGMA, 50% consist of individual samples. Beyond undersampling, natural small-scale discontinuities are reflected by this result. Partial db-RDA resulted in an explained variation of 9.60% and 14.41% for environmental and soil factors, respectively. Utilising variation partitioning analyses based on CCA and tb-RDA, between 21.70% and 37.80% of the variation in vegetation data could be explained. The spatially structured fraction of these parameters accounts for between 30.50% and 49.80% of the explained variation (100%). The purely environmental parameters account for a share of 10.30% to 16.30%, whereby the lower limit originates from the unimodal approach and has lost its statistical significance. The soil variables, also after partial analysis, account for a share of 19.00% to 35.70%. While the residual impact of the climatic parameters is hardly significant, the effect of the soil properties is prevalent. In general, the spatially structured fraction of the parameters is predominant here. While on the broad-scale climatic factors, the altitude a.s.l. and the geology are determining factors, some soil parameters and matrix components also show their impacts here. In the mid-range of the scale, it is the forest matrix, the soil types, and the geology that determine species distribution. While in the fine range of the scale, some unrecorded parameters seem to have an effect, there are also neutral processes that determine species composition.
Über 10.000 verschiedene organische Substanzen wie Arzneistoffe, Inhaltsstoffe von Körperpflegemitteln und Biozide werden regelmäßig im Alltag eingesetzt. Die meisten Substanzen gelangen nach ihrer Verwendung in das häusliche Abwasser. Bisherige wissenschaftliche Untersuchungen haben ergeben, dass eine konventionelle biologische Abwasserreinigung in kommunalen Kläranlagen keine ausreichende Barriere für die Emission dieser anthropogenen Stoffe in die Oberflächengewässer darstellt.
Dies birgt unvorhersehbare Risiken für die aquatischen Lebensgemeinschaften und die Trinkwasserversorgung. Hinsichtlich ihres Vorkommens und Verhaltens in kommunalen Kläranlagen besteht daher insbesondere für erst kürzlich eingeführte und/oder in der Umwelt nachgewiesene Spurenstoffe (sogenannte "neuartige" Spurenstoffe, engl.: "emerging micropollutants") ein großer Forschungsbedarf. Um ein möglichst umfassendes Bild vom Verhalten neuartiger organischer Spurenstoffe in der kommunalen Abwasserbehandlung zu erhalten, wurden im Rahmen dieser Dissertation die folgenden Substanzklassen, welche ein weites Spektrum an physiko-chemischen Eigenschaften aufweisen, untersucht: Arzneistoffe (Betablocker und psychoaktive Substanzen), UV-Filtersubstanzen, Vulkanisationsbeschleuniger (Benzothiazole), Biozide (Antischuppenmittel, Konservierungsmittel, Desinfektionsmittel) und Pestizide (Phenylharnstoff- und Triazinherbizide).
Human population pressure increased with the population growth around the NNP and Cyamudongo with disturbance impacts on the forests isolating populations into fragments and today, Cyamudongo natural forest is located a way at a distance of at least 8.5 km horizontal distance to Nyungwe main block with a surface area estimated at 300 ha. Under Cyamudongo project implementation, there was a need to understand how the flora diversity responded to human imposed challenges and to forest restoration initiatives. Three physiognomic landscapes forest were identified and considered for three phases of vegetation survey in Cyamudongo and related to the closest area of Nyungwe main block. In this study, 15 transects were laid in each physiognomic forest landscape and 10 and 5 plots were set respectively in Cyamudongo and Gasumo study area. In total, 315 phytosociological relevés were performed and the Braun-Blanquet methods used for three times vegetation surveys. Species life-forms and chorophyte were evaluated and tree species dbh and height have been measured. Data were subjected to different statistical analyses using different softwares such as PAST, R 3.5.2, and SPSS. The mapping was done using Arc GIS and the Multi-Spectral Remote Sensing used to find NDVI for the vegetation classification.
NDVI trends showed that there has been fluctuations in vegetation classifications of the studied area. In this study, 494 vascular plant species from 106 families were harbored in the study area and distributed differently among forest landscapes and study phases. Although, 43.54% were common to Cyamudongo and Gasumo landscapes while 48.54 % of species diversity were hold only by Cyamudongo and 7.92% confined to Gasumo and 12 in total were found new records for Rwanda while several others suspected require detailed research for identification showing how the flora diversity of Cyamudongo is of special interest and extremely important for discoveries.
The finding of the study on diversity indices, the PCA, CA and the Cluster analysis, all statistical analyses (MANOVA, ANOVA) and life form spectra unanimously showed that the anthropogenic disturbance shaped the vegetation cover, the floristic composition, the species diversity, the forest landscapes community structure, the life form spectrum and the phytoclimate of Cyamudongo and Gasumo forest landscapes. Although, the vegetation analysis couldn’t clearly identify communities and sub-communities at the initial and final vegetation surveys and cluster groups were heterogeneous as well as overlapping and species associations not clearly defined due to the high level of similarities in species composition among forest landscapes and vegetation surveys. The species diversity was found high in secondary forest and Gasumo landscape forest and low in the primary forest and the buffer zone of Cyamudongo and the disturbance with gaps openings was found to be associated to the species diversity with a seasonal variation. The patterns of dbh for the buffer zone and of the size classes of all landscapes with an inverted ‘J’ indicated a healthy regeneration in the forest landscapes and tree species explained a good regeneration and recruitment capacity. Different shapes in the pattern of dbh with respectively an inverted ‘J’, ‘J ‘and ‘U’ for the buffer zone, primary and together the secondary and Gasumo forest landscapes indicated differences in the landscapes health and degree of regeneration and recruitment capacity.
Findings from differents measuements showed at which extend human activities have shaped the flora diversity and structure of forest landcapes studied. For instance, disturbances due human activities were daily oberved and trees were logged by neighboring communities such as Batwa populations at Cyamudongo and local populations at Gasumo. Some species were evenly observed targeted for their barks such as Ocotea usambarensis, Parinari excelsa for medicines and many others for their wood quality, fire wood collection and for agricultural purposes.
In the period of Cyamudongo project implementation, important achievements included the increase of forest biomass and therefore the photosynthetic capacity and the evapotranspiration potential that influence the rainfall regime; the regulation of weather conditions and then species diversity; supporting local communities and limiting human activities; raising awareness on conservation and protection of biodiversity and improving of living conditions of neighboring populations by providing paid employment and so to restore to the Cyamudongo forest ecosystem functions. Moreover, Cyamudongo forest remains vulnerable as surrounded by local communities with a high population pressure relying on forest resources for its survival. Cyamudongo harbors a high level of endemism and is a small hotspot for biodiversity conservation. It is therefore recommended to strengthen conservation and protection measures and continue the support of local communities.
In the present study the flora and vegetation of Kakamega Forest, an East African rainforest in Western Kenya, was investigated. Kakamega Forest is highly degraded and fragmented and is an ideal model to study the anthropogenic influence on the forest inventory. The main focus was to analyse the influence of human impact on the vascular plant species composition. During five field phases in the years 2001 to 2004 a total of 19 study sites scattered over the whole forest including all fragments were investigated regarding forest structure, species composition and plant communities. The different forest sites were analysed by three different methods, phytosociological relevés, line-transect and with the variable-area transect method. The forest survey revealed about 400 taxa of vascular plant species, among them 112 trees, 62 shrubs, 58 climbers and 114 herbs. Several species are restricted to this forest in Kenya, but only one endemic species, the herb Commelina albiflora, could be discovered. About 15 species were recorded as new for Kenya and probably at least one species is new to science. Kakamega Forest is a unique mixture of Guineo-Congolian and Afromontane floral elements. About one half of the vascular plant species has its origin in the lowland forests of the Congo basin and one third originates from Afromontane habitats. The present study represents the first description of plant communities of Kakamega Forest. An analysis of different forest sites and plantations resulted in 17 different vegetation units. For the mature forest sites eleven plant communities were described. The young succession stage consists of two plant communities. Since the disturbance history and the age of the different plant communities could be estimated, their chronology was also described. An exception are the study sites within the plantations and afforested sites. The four defined vegetation units were not described as plant communities, because they are highly affected by man and do not belong to the natural succession of Kakamega Forest. Nevertheless, the regeneration potential of such forests was investigated. Due to the different succession stages the changing species composition along a disturbance gradient could be analysed. Most of Kakamega Forest consists of middle-aged secondary forest often surrounded by very young secondary forest. A true primary rainforest could not be found due the massive influence by over-exploitation. In all parts of the forest the anthropogenic influence could be observed. The forest develops towards a climax stage, but a 2 Abstract comparison with former surveys shows that the regeneration is much slower than expected. Human impact has to be avoided to allow the forest to develop into a primary-like rainforest. But several climax tree species might be missing anyway, because after the broad logging activities in the past there are not enough seed trees remaining. Species richness was highest in disturbed forest sites. A mixture of pioneer, climax and bushland species could be recorded there. Therefore, a high species richness is not a suitable indicator for forest quality. The proportion of climax species typical for Kakamega Forest would be a better measure. Compared to the main forest block the forest fragments do not lack in diversity as expected due to fragmentation processes. Instead, the only near primary forest could be recorded in Kisere, a northern fragment. The high amount of climax species and the more or less undisturbed forest structure is a result of the strict protection by the Kenya Wildlife Service and due to low logging activities. Differences in species composition between the studied forest sites are either a result of the different logging history or management regime rather than due to different edaphic or climatic conditions.
The ongoing loss of species is a global threat to biodiversity, affecting ecosystems worldwide. This also concerns arthropods such as insects and spiders, which are especially endangered in agricultural ecosystems. Here, one of the main causing factors is management intensification. In areas with a high proportion of traditionally managed grassland, extensive hay meadows that are cut only once per year can still hold high levels of biodiversity, but are threatened by conversion into highly productive silage grassland. The Westerwald mountain range, western Germany, is such a region. In this thesis, I compare the local diversity of bees, beetles, hoverflies, leafhoppers, and spiders of five grassland management regimes along a gradient of land-use intensity. These comprise naturally occurring grassland fallows, three types of traditionally managed hay meadows, and intensively used silage grassland. By using three different sampling methods, I recorded ground-dwelling, flower-visiting, and vegetation-dwelling species. The results show that in most cases species richness and diversity are highest on fallows, whereas variation among different managed grassland types is very low. Also, for most sampled taxa, fallows harbour the most distinct species assemblages, while that of other management regimes are largely overlapping. Management has the largest effect on species composition, whereas environmental parameters are of minor importance. Long-term grassland fallows seem to be highly valuable for arthropod conservation, even in a landscape with a low overall land-use intensity, providing structural heterogeneity. In conclusion, such fallows should be subsidized agri-environmental schemes, to preserve insect and spider diversity.
Foliicolous lichens are one of the most abundant epiphytes in tropical rainforests and one of the few groups of organisms that characterize these forests. Tropical rainforests are increasingly affected by anthropogenic disturbance resulting in forest destruction and degradation. However, not much is known on the effects of anthropogenic disturbance on the diversity of foliicolous lichens. Understanding such effects is crucial for the development of appropriate measures for the conservation of such organisms. In this study, foliicolous lichens diversity was investigated in three tropical rainforests in East Africa. Godere Forest in Southwest Ethiopia is a transitional rainforest with a mixture of Afromontane and Guineo-Congolian species. The forest is secondary and has been affected by shifting cultivation, semi-forest coffee management and commercial coffee plantation. Budongo Forest in West Uganda is a Guineo-Congolian rainforest consisting of primary and secondary forests. Kakamega Forest in western Kenya is a transitional rainforest with a mixture of Guineo-Congolian and Afromontane species. The forest is a mosaic of near-primary forest, secondary forests of different seral stages, grasslands, plantations, and natural glades.
Dadurch, dass Silber-Nanopartikel (Ag NPs) vielfältig in Konsumartikeln eingesetzt werden, führt deren Auswaschung zu einer kontinuierlichen Freisetzung von Ag NPs in natürliche Gewässer. Dadurch werden bakterielle Biofilme, welche die vorherrschende Lebensform von Mikroorganismen in der aquatischen Umwelt darstellen, sehr wahrscheinlich mit diesen in Form eines Umweltschadstoffes onfrontiert. Ungeachtet der bedeutsamen ökologischen Relevanz von bakteriellen Biofilmen in aquatischen Systemen und obwohl erwartet wird, dass Ag NPs in diesen Biofilmen in der Umwelt akkumulieren, liegt der Wissensstand hinsichtlich der umweltbedingten und ökologischen Auswirkung von Ag NPs hinter dem industriellen Wachstum der Nanotechnologie zurück. Demzufolge ist das Ziel dieser Dissertation, die Wirkungsbeziehung der Ag NP-Exposition gegenüber bakteriellen Biofilmen mit Ag NP-Immissionskonzentrationen und unter umwelt-relevanten Bedingungen zu erbringen. Infolgedessen wurden eine umfassende Reihe an Methoden angewendet, um zu untersuchen ob und inwiefern Ag NPs in zwei verschiedenen Größen (30 und 70 nm) und in umweltrelevanten Konzentrationen (600 - 2400 µg l-1) bakterielle Biofilme, d.h. monospecies- und Süßwasser-Biofilme, beeinträchtigen. Innerhalb des ersten Teils dieser Arbeit wurde ein neu entwickelter Assay validiert, um die mechanische Stabilität von monospecies Biofilmen des Bakteriums Aquabacterium citratiphilum zu untersuchen. In der ersten Studie, welche den Einfluss von Ag NPs auf die mechanische Stabilität von bakteriellen Biofilmen untersucht hat, wurden subletale Auswirkungen auf die mechanische Stabilität dieser Biofilme mit negativen Implikationen für die Biostabilisation festgestellt. Weiterhin wurde eine Mesokosmus-Studie konzipiert und durchgeführt, innerhalb der die Auswirkungen von Ag NPs auf Süßwasser-Biofilme eingehend unter realistischen Umweltbedingungen untersucht werden konnte, da es derzeit technisch noch sehr anspruchsvoll ist, die Ökotoxizität von Ag NPs in der Umwelt von Binnengewässern zu untersuchen. Innerhalb dieser Studie wurden verschiedene Methoden zur Untersuchung der Biofilmeigenschaften eingesetzt und damit Erkenntnisse über die Resilienz von bakteriellen Süßwasser-Biofilmen gewonnen. Demgegenüber konnte mittels t-RFLP fingerprinting und phylogenetischen Untersuchungen basierend auf der Sequenzanalyse des 16S-rRNA-Gens nachgewiesen werden, dass die Exposition der Biofilme mit Ag NPs zu einer Verschiebung innerhalb der Zusammensetzung der bakteriellen Biofilmgemeinschaft führt, in der Ag NP-sensitive Arten von Ag NP-toleranten Arten, die besser an Ag NP Stress adaptiert sind, verdrängt wurden. Diese Verschiebung innerhalb der bakteriellen Biofilmgemeinschaft könnte die Biofilm-Leistungen beeinträchtigen, die intakte Biofilme auszeichnen, wie etwa den Abbau erhöhten Nährstoffeintrags, die Umwandlung und/oder den Abbau von Schadstoffen sowie Biostabilisation. Durch das Zusammenführen der wichtigsten Erkenntnisse dieser Dissertation konnten 4 generelle Wirkmechanismen durch die Ag NP-Behandlung identifiziert werden, die auf natürliche Süßwassersysteme übertragbar sein könnten: (i) Comamonadaceae wurden als Ag NP-tolerant identifiziert, (ii) Biofilme zeigen ein partiell resilientes Verhalten, (iii) die beiden eingesetzten verschiedenen Ag NP-Größen führten zu vergleichbaren Ergebnissen unabhängig von deren Größe oder Synthesemethode, (iv) Bakterielle Biofilme verfügen über eine hohe Aufnahmekapazität für Ag NPs, die auf eine kumulative Anreicherung hinweist.