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Chemical pollution is one of the main contributors to the degradation of lotic ecosystems and their biodiversity. Among chemicals driving lotic biodiversity decline are anthropogenic organic micropollutants (AOM), which affect the survival and functioning of freshwater organisms. Continuous exposure of freshwater organisms to AOM leads to adverse effects that sometimes cannot be traced with standard toxicity methods such as standard toxicity testing or biodiversity indices. Among these effects of AOM are selective or mutagenic effects that cause impaired species genetic diversity. Thus, the correlation between different levels of AOM and genetic diversity of species is still poorly understood. However, it can be explored by applying population genetics screening.
In Chapter 1 of this thesis, background information on environmental pollution, genetic screening, and the detection of evolutionary-relevant AOM effects in freshwater organisms are described and the thesis goals are identified. The main goal of the thesis is to study whether AOM exposure occurring in European rivers causes a significant evolutionary footprint in freshwater species and leads to a selection of more tolerant geno-and phenotypes. Therefore, population genetics indices together with high-resolution chemical exposure screening of a widespread indicator invertebrate species, Gammarus pulex (Linnaeus, 1758), living in polluted and pristine European rivers were investigated.
In Chapter 2, the development of a genetic screening method for G. pulex (microsatellites) is described. Due to genetic differentiation and the presence of morphologically cryptic lineages, the available sets of target loci do not enable a reliable population genetic characterization of G. pulex from central Germany. Thus, a novel set of microsatellite loci for a high-precision assessment of population genetic diversity was here applied. Eleven loci were first identified and thereafter amplified in G. pulex from three rivers. The new loci reliably amplified and indicated polymorphisms in the studied amphipods. The amplification resulted in the successful identification of genetically distinct populations of G. pulex from the analyzed rivers. Moreover, the microsatellite loci were amplified in other genetic lineages of G. pulex and another Gammarus species, G. fossarum, promising a broader applicability of the loci in related amphipod species.
In Chapter 3, the effects of AOM on species genetic differentiation and sensitivity to toxic chemicals in a typical central European river with pristine and AOM-polluted sections was investigated. The river’s site-specific concentrations of AOM were assessed by chemical analysis of G. pulex tissue and water samples. To test, whether different levels of AOM in the river select for pollution-dependent genotypes, the genetic structure of G. pulex from the river was analyzed. Finally, the toxicokinetics of and sensitivity to the commonly used insecticide imidacloprid were determined for amphipods sampled at pristine and polluted sections to assess whether various levels of AOM in the river influence sensitivity of G. pulex to imidacloprid. The results indicated that different levels of AOM did not drive genetic divergence of G. pulex within the river but led to an increased sensitivity of exposed amphipods to imidacloprid. The amphipods living in polluted river sections were more sensitive to the insecticide due to chronic exposure to toxic levels of AOM.
In Chapter 4, the relationship between site-specific pollution levels of AOM and genetic diversity parameters of G. pulex was analyzed at the regional scale within six rivers in central Germany. The genetic structure of G. pulex in the studied area was tested for relatedness to the waterway distance between sites. Gammarus pulex genetic diversity parameters, including allelic richness and inbreeding rate, were tested against environmental pollution parameters using linear mixed-effect- and structural-equation models. According to the results, G. pulex genetic diversity parameters were significantly associated with the detected AOM levels. At sites with high concentrations of AOM and toxicity potential G. pulex showed reduced genetic diversity and increased rates of inbreeding. These results suggest that AOM play a major role in shaping the genetic diversity of G. pulex in rivers.
According to the findings presented here, the applied microsatellites can be used to successfully detect changes in genetic patterns in freshwater amphipods facing increased levels of AOM. The findings indicate that levels of AOM representative for European rivers do not lead to the separation of genotypes among G. pulex as the connectivity between sites majorly contributes to species’ genetic structure. However, the chronic exposure to increased levels of toxic AOM leads to a reduction of species genetic diversity and increases the sensitivity of G. pulex to the toxic chemical effects.
Spinocerebellar ataxia type 2 (SCA2) is an autosomal dominant neurodegenerative movement disorder caused by expansion of CAG repeats in the ATXN2 gene beyond 33 units, while healthy individuals carry 22-23 repeats. First symptoms of SCA2 include uncoordinated movement, ataxic gait and slowing of the saccadic eye movements in line with the early pronounced atrophy of cerebellum, spinal cord and brainstem. Cerebellar Purkinje cells and spinal cord motor neurons are the most affected cells from ATXN2 expansions. Later on, patients manifest distal amyotrophy, problems in breathing and swallowing, depression and cognitive decline caused by widespread degeneration throughout the brain. The striking loss of mass in the brain, due to severe myelin fat atrophy, is accompanied by a similar reduction in the peripheral fat stores. After the devastating progression of disease, the severity and duration of which depends on the CAG repeat size, genetic background and environmental factors, patients succumb to SCA2 mostly because of respiratory failure at the terminal stage. Larger repeat sizes lead to an earlier manifestation of the disease and a more rapid progression. Aside from SCA2, intermediate-length and short pathogenic CAG expansions in ATXN2 between 26-39 repeats significantly increase the risk of developing other neurodegenerative disorders, such as amyotrophic lateral sclerosis (ALS), fronto-temporal lobar dementia (FTLD) or Parkinson plus tauopathies like progressive supranuclear palsy (PSP) in various cohorts across the world.
Ataxin-2 (ATXN2) is a ubiquitously expressed cytosolic protein most famous for its involvement in neurodegenerative disease caused by the expanded poly-glutamine (polyQ) domain corresponding to a genomic (CAG)n tract. This N-terminal polyQ domain has no known function, other than increasing the aggregation propensity of mutant ATXN2 and facilitating interaction with other polyQ containing proteins, leading to their sequestration. The progressive accumulation of ATXN2 into cytosolic foci, and also that of its interaction partners over time, underlies the molecular pathomechanism. Next to polyQ domain, ATXN2 also contains a Like-Sm domain (Lsm), an Lsm-associated domain (LsmAD), multiple proline-rich domains (PRD) and a Poly(A)-Binding-Protein (PABP)-interacting motif (PAM2).
Through its Lsm/LsmAD domains, ATXN2 directly binds to a large number of transcripts, regulating their quality and translation rate. In a similar fashion, through its direct interaction with PABP via PAM2 motif, ATXN2 indirectly modifies the fate of even larger number of transcripts and global translation. Several PRDs scattered across the protein help ATXN2 associate with growth factor receptors and other endocytosis factors, modulating nutrient uptake and downstream signaling.
ATXN2 is a stress response factor. Therefore, its involvement in nutrient uptake plays a crucial part in cell’s capability to overcome non-permissive conditions. Upon nutrient deprivation, oxidative stress, proteotoxicity, heat stress or Ca2+ imbalance, ATXN2 relocalizes into cytosolic ribonucleoprotein particles known as stress granules (SGs), together with PABP, several eukaryotic translation initiation factors, many other RNA-binding proteins (RBP) with their target transcripts and the small ribosomal subunit. Collectively, they modulate the stability of the trapped transcripts, favoring the maturation and translation of IRES-dependent stress response proteins instead, according to the specific need. Many RBPs interact either directly or in an RNA-dependent manner in the SGs, and due to the large number of ALS-causing mutations identified in them (such as TDP-43, FUS, TIA-1, hnRNPA2/B1), SGs became a hot topic in neuropathology. Acute SGs serve to halt translation and growth, and to spend energy only for survival until stress disappears. However, chronic SG assembly eventually activates apoptotis leading to cell death. While the polyQ expansions in ATXN2 enhance SG stability, reduce their dissociation rate after stress, and lead to aberrant post-translational modifications of other SG components like TDP-43, complete loss of ATXN2 delays SG formation and results in easily dissolvable foci.
Most of the stressors that induce SG formation eventually converge on energetic deficit. Therefore, it is logical that the ultimate task of SGs is to stop further growth when it cannot be afforded. In yeast, the molecular mechanism underlying this growth arrest was explained as sequestration of the master growth regulator complex, Target-of-Rapamycin Complex 1 (TORC1), into SGs in an ATXN2-dependent manner. The repressor effect of ATXN2 on mammalian TORC1 (mTORC1) and global protein translation had already been documented in earlier studies; complete loss of ATXN2 function in knock-out mouse (Atxn2-KO) resulted in mTORC1 hyperactivity and transcriptional upregulation of multiple ribosomal subunits indicating an increased need for these machines. ...
Evidence is increasingly pointing towards a significant global decline in biodiversity. The drivers of this decline are numerous, including habitat change and overexploitation, rapid deforestation, pollution, exotic species and disease, and finally climate change as an emerging driver of biodiversity change (Nakamura, et al., 2013; Hancocks, 2001; Pereira, Navarro & Martins, 2012). Raising public awareness of the need to conserve biological diversity is essential to safeguard the richness of life forms all over the world (Lindemann-Matthies, 2002). In this regard, institutions such as science museums, zoos and aquariums have the potential to play an important role (Rennie & Stocklmayer, 2003). Especially, zoos can provide a productive learning environment (Miles & Tout, 1992), facilitating the promotion of public conservation awareness and the adoption of pro-environmental behaviours that would reduce negative human impacts on biodiversity (Barongi, et al., 2015).
Based on these concepts, my study contributes to the developing field of visitor studies. Taking as reference non-zoo visitors and zoo visitors, I have focused on reviewing some aspects of conservation education, such as people's awareness of conservation, people's interest in animals and people's feelings towards animals and attitudes towards zoos. The study identified differences between non-regular and regular zoo visitors in interests in animals, as well as visitor attitudes towards conservation issues and zoos. Therefore, the present study indicated that positive emotional reactions and, in particular, a perceived sense of connection to the animal were linked and depended on the frequency of zoo visits. It was as well remarkable, that conservation awareness was influenced by the interest in animals, the interest in visiting zoos, the attitudes towards these institutions, and the age and the country of origin. All these variables had a greater effect in the conservation consciousness of the participants. Additionally interestingly, the main reason for visiting zoos in every country was to learn something about animals. This highlights the educational role of zoos and broadly supports the idea that people want to visit zoos to learn something about animals, in turn facilitating pro-conservation learning and changes in attitude. They are uniquely positioned to interact with visitors, communities, and society and to contribute by providing an informative and entertaining environment. Visiting zoos could led to contribute to promoting animal connectedness and interest in species.
Fuer die schlechte Prognose von Glioblastompatienten mit einer ueberlebenszeit von 9-15 Monaten (Norden and Wen, 2006) ist vor allem die hohe Invasivitaet dieser Tumore verantwortlich. Nach operativer Entfernung des Haupttumors entstehen aus den verbleibenden invadierten Zellen sekundaere Tumore, die sich mitunter ueber weite Bereiche des Hirns verteilen. Des Weitern sind die hochinvasiven Tumorzellen oft resistent gegen Chemo- und Strahlentherapie (Drappatz et al., 2009; Lefranc et al., 2005). In Maustumormodellen und Pateinten konnte zudem gezeigt werden, dass die neuartige antiangiogenetische Therapie zwar das Tumorwachstum verringert, jedoch die Invasivitaet stark erhoeht. (Norden et al., 2008; Ebos et al., 2009; Paez-Ribes et al., 2009). Ueber die Mechanismen die diese hohen Invasivitaet induzieren, ist bislang nur sehr wenig bekannt. Die durch Reduktion von Blutgefaessen steigende Hypoxie des Tumors foerdert die Expression von Matrix-Metalloproteinasen (MMPs). Dies fuehrt zum Abbau der extrazelluaeren Matrix des umgebenden gesunden Gewebes und beguenstigt dadurch die Tumorzellinvasion (Indelicato et al., 2010; Miyazaki et al., 2008; Shyu et al., 2007). Die Umformung des Aktinzytoskeletts und damit die Mobilitaet von Zellen wird vorwiegend durch ein akkurates Zusammenspeil der Rho GTPasen Rac, Rho und Cdc42, kontrolliert (Ridley et al., 2003). Fuer die Organisation von Axonen im Nervensystem und fuer die Blut- und Lymphgefaessbildung wurde gezeigt, dass die Interaktion der Eph-Rezeptortyrosinkinasen und Ihrer Ephrin-Liganden Signalwege induziert, die in die Regulation dieses Zusammenspiels involviert sind (Egea and Klein, 2007; Makinen et al., 2005; Palmer et al., 2002; Sawamiphak et al., 2010). Des Weiteren zeigt die Analyse der Genloci von Eph-Rezeptoren und Ephrinen in verschieden Hirntumoren eine gehaeufte Deletionen des Ephrin-B2-Gens. Die Quantifizierung von Ephrin-B2 mRNA in diesen Tumoren hat ausserdem ergeben, dass mit zunehmender Malignitaet die Expression von Ephrin-B2 sinkt. Aus diesen Gruenden wurden die Untersuchungen in dieser Arbeit auf die Rolle von Ephrin-B2 anhaengigen Signalwegen in der Glioblastomzellinvasion konzentriert. In einem modifiziertem Boyden-Chamber-Assay konnte gezeigt werden, dass das Ephrin-B2 induzierte EphB4 forward signaling und EphB4 induzierte Ephrin-B2 reverse signaling die Invasivitaet der human Glioblastomzelllinien LN-229, G55 und SNB-19 reduziert. In einem Maustumormodel konnte weiterhin gezeigt werden, dass Ephrin-B2 Knock-Out (KO) Astrozytomzellen, im Vergleich zu Wild-Typ (WT) Zellen, Tumore mit einem groesseren Volumen und einer erhoehten Invasivitaet bilden. Da die Expressionslevel fuer die Ephrin-B2 bindenden Rezeptoren EphA4, EphB1 EphB3 und EphB6 auch im adulten Hirn hoch sind (Hafner et al., 2004), weisen diese in vitro und in vivo Ergebnisse auf eine Tumorsupressorfunktion von Ephrin-B2 hin, die durch repulsive Effekte des Ephrin-B2 reverse signaling vermittelte werden koennten. Dies geht mit Erkenntnissen ueber kolorektale Tumore einher (Batlle et al., 2005). Die in einem Sphaeroid-Invasionsassay mit einer EphB-Rezeptoren freien Umgebung beobachtete verminderte Invasion von Ephrin-B2 WT deutet auf eine zusaetzliche invasionsblockierende Rolle der Ephrin-B2-Eph-Rezeptor Interaktion zwischen benachbarten Tumorzellen hin, wie sie auch in Brusttumoren gefunden wurde (Noren et al., 2006). Es scheint als sei Tumorprogression und Invasion erst moeglich, nachdem die Expression von Ephrin-B2 vermindert wurde. Es konnte weiterhin gezeigt werden, dass in hypoxischen Glioblastomzellen die Ephrin-B2 Expression durch die direkte Bindung des den Transkriptionsfaktors ZEB2 an den Ephrin-B2 Promoter reprimiert wird. In einem Weiteren Maustumormodel konnte gezeigt werden, dass die Blockierung der ZEB2 Expression mittels shRNA und die damit einhergehenden Inhibition der hypoxie induzierten Ephrin-B2 Repression das Wachstum und die Invasivitaet von Glioblastomen verringert. Zusaetzlich wurde gezeigt, dass der Verlust von ZEB2 ausreicht, die durch antiangiogenetische Therapie induzierte stark erhoehte Invasivitaet zu vermeiden. Die in dieser Arbeit gewonnen Erkenntnisse fuehren zu folgendem Modelmechanismus. In kleinen normoxischen Tumoren koennen repulsive Effekte des Ephrin-B2 reverse signalings und EphB forward signalings zwischen Tumorzellen und Zellen des umgebenden Gewebes die Ausbreitung und Invasion des Tumors unterdruecken. Zusaetzlich koennte das Ephrin-B2 induzierte EphB forward signaling zwischen benachbarten Tumorzellen die Mobilitaet der Tumorzellen wie in Brusttumoren inhibieren. Beim Erreichen einer bestimmten Tumorgroesse tritt Hypoxie auf, wodurch HIF-1alpha stabilisiert wird. Dies fuehrt dann zur ZEB2 Expression und leitet die Repression von Ephrin-B2 ein, was wiederum zur erhoehten Tumorzellemobilitaet und im Zusammenspiel mit MMPs zu Invasion fuehren kann. Gleichzeitig werden durch den HIF-induzierten VEGF-Gradienten neue Blutgefaesse rekrutiert. Damit wird der hypoxie-induzierten Invasivitaet entgegengewirkt. Wird mittels antiangiogenetischer Behandlung versucht Tumorprogression entgegenzuwirken, resultiert daraus eine erneut gesteigerte Hypoxie, die dann durch die ZEB2 vermittelte Repression von Ephrin-B2 wieder eine erhoehte Invasivitaet induzieren kann. Das Blockieren der ZEB2 Expression kann dieser durch antiangiogenetischen Behandlung induzierten Invasivitaet entgegenwirken.
Plastics contain a complex mixture of chemicals including polymers, additives, starting substances and side-products of processing. These plastic chemicals are prone to leach into the packaged goods, in the case of food contact materials (FCMs), or into the natural environment, in the case of plastic debris. Thus, plastics represent an exposure source of chemicals for humans and wildlife alike. While it is widely known that individual plastic chemicals, such as bisphenol A and phthalates, are hazardous, little is known on the overall chemical composition and toxicity of plastics. When fragmented into smaller particles, referred to as microplastics (< 5 mm), the plastic itself can be ingested by many species. It is well established that microplastic ingestion can have negative consequences for a wide range of organisms including invertebrates, but the contribution of plastic chemicals to the toxicity of microplastics is unclear.
Given the above, the present thesis aimed at a comprehensive toxicological, ecotoxicological and chemical characterization of everyday plastics. For a comparative evaluation, 77 plastic products were selected covering 16 material types (e.g., polyethylene) made from petroleum or renewable feedstocks. These products included biodegradable products, FCMs and non-FCMs, as well as raw materials and final products, respectively. In the first two studies, the chemical mixtures contained in the 77 products were extracted with methanol and extracts were analyzed in a set of four in vitro bioassays and by non-target high-resolution gas or liquid chromatography mass spectrometry. Since an exposure only occurs if chemicals actually leach under realistic conditions, in a third study migration experiments with water were conducted for 24 out of the 77 products. The aqueous migrates were assessed in the same way as the methanolic extracts. In addition, the freshwater invertebrate Daphnia magna was exposed chronically to microplastics made of polyvinylchloride (PVC), polyurethane (PUR) and polylactic acid (PLA) to investigate the contribution of chemicals in microplastic toxicity, in a fourth study.
The experimental findings demonstrate that a wide variety of chemicals is present in plastics. A single plastic product can contain up to several thousand chemical features, most of which unique to that product and at the same time unknown. The results also indicate that the majority of these chemical mixtures are toxic in vitro. Accordingly, 65% of the plastic extracts induced baseline toxicity and 42% an oxidative stress response, while 25% had an antiandrogenic and 6% an estrogenic activity. This implies that chemicals causing unspecific toxicity are more prevalent in plastics than such with endocrine effects. These chemicals can also leach from plastics under realistic conditions. Between 17 and 8936 chemical features were detected in a single migrate sample and all 24 tested migrates induced in vitro toxicity. This means that humans and wildlife can actually be exposed to toxic plastic chemicals under realistic conditions. Generally, each product has its individual toxicological and chemical fingerprint. Thus, neither material type, feedstock, biodegradability nor the food contact suitability of a product can serve as a predictor for the toxicity, the chemical composition or complexity of a product. Likewise, this means that bio-based and biodegradable materials are not superior to their petroleum-based counterparts from a toxicological perspective despite being promoted as sustainable alternatives to conventional plastics.
Moreover, the present thesis demonstrates that plastic chemicals can be the main driver for microplastic toxicity. Irregular microplastics made of PVC, PUR and PLA adversely affected life-history traits of D. magna in a polymer type- and endpoint-dependent manner at concentrations between 100 and 500 mg L-1 and with a higher efficiency than natural kaolin particles. While the toxicity of PVC was triggered by the chemicals used in the material, the effects of PUR and PLA were induced by the physical properties of the particle.
In addition, in the fifth study, results and observations made during this thesis were integrated inter- and transdisciplinarily with the perspectives of a social scientist and a product manufacturer. This elucidated that knowledge on plastic ingredients is often concealed, is lacking or not applicable in practice. These intransparencies hinder the safety evaluation of plastic products as well as the choice and sale of the least toxic packaging material.
Overall, the present thesis highlights that the chemical safety of plastics and their bio-based and biodegradable alternatives is currently not ensured. Thus, chemicals require more consideration in the toxicity and risk assessment of plastics and microplastics. Product-specific and complex chemical compositions, including unknown compounds, pose a challenge here. Two essential steps towards non-toxic products are to increase transparency along the product life cycle and to reduce the chemical complexity of plastics by communication and regulation. The results of the present thesis indicate that products exist which do not contain toxic chemicals. These can serve to direct the design of safer plastics. Since toxicity and chemical complexity seem to increase with processing, the integration of toxicity testing during the production steps would further support the safe and sustainable production and use of plastic products.
The process of urbanization is one of the major causes of the global loss of biodiversity; however, cities nowadays also have the potential to serve as new habitats for wildlife. The European rabbit (Oryctolagus cuniculus, L. 1758) is a typical example of a wildlife species that reaches stable population densities in cities. Due to intense plant and soil damages, German city authorities aim to control high rabbit densities through the application of a yearly hunting regime (e. g., in Munich, Berlin or Frankfurt am Main). In contrast, population densities of O. cuniculus are on decline in German rural areas, i. e., numbers of yearly hunting bags decreased. The aim of my doctoral thesis was to answer the following research questions: Do population densities of the European rabbit correlate with the intensity of urbanization in and around Frankfurt am Main and if so, which factors play a role in varying densities? How are burrow construction behaviors and group sizes, daytime activity patterns and anti-predator behaviors as well as communication behaviors of this mammal affected by urbanization?
In my first study, I focused on population dynamics across 17 different study sites in and around Frankfurt. As one of yet few studies, I invented an approach that quantified the intensity of urbanization (degree of urbanity) of each study site base on four variables: (1) intensity of anthropogenic disturbance per min and ha, (2) number of residents within a radius of 500 m, (3) proportion of artificial ground cover and (4) numbers of anthropogenic objects per ha. Spearman rank correlations confirmed that with increasing degree of urbanity also rabbit and burrow densities increased. The access to dense shrubs, bushes etc. as suitable sites for burrow construction is the most determining factor for rabbit abundances, and therefore I presumed different densities along the rural-to-urban gradient to be driven by shifts in the availability of thick vegetation.
In the second study, I calculated two indices that in both cases classified burrows to be either accumulated, evenly or randomly distributed within study sites. Additionally, in cooperation with local hunters the number of burrow entrances and animals that occupy the same burrow had been determined during the hunting season. With increasing degree of urbanity burrow distribution patterns shifted from accumulated in rural areas towards more evenly distributed within the city center of Frankfurt. This is a clear sign for an increasing access to sites suitable for burrow construction along the rural to-urban gradient. Additional Spearman rank correlations revealed that the external dimensions of burrows decreased (shorter distances between entrances) and that burrows became less complex (fewer entrances) along the rural-to-urban gradient. In accordance, the number of rabbits that commonly shared the same burrow system was highest within rural areas, whereas I found mainly pairs and single individuals within highly urbanized study sites.
In the last study I compared activity patterns, burrow use and percentages of anti-predator behaviors from one hour before sunrise until one hour after sunset of rural, suburban and urban rabbit groups. A linear mixed model (LMM) and Spearman rank correlations confirmed that rabbits located at urban and suburban sites spent more time outside their protective burrows compared to their rural conspecifics. At suburban sites, individuals invested the least amount of time in anti-predator behavior. Results of this third study gave evidence that suburban rabbit populations on one hand benefit from less predation pressure by natural predators in comparison to rural sites, whereas on the other hand are exposed to less intense disturbance by humans compared to urban study sites.
The last study focused on the effects that urbanization had on the latrine-based communication behavior of rabbits. As many other mammals, O. cuniculus exchange information via the deposition of excreta in latrines, and depending on the intended receiver(s), latrines are either formed in central areas for within-group communication or at territorial boundaries, e. g., for between-group communication. The relative importance of within- vs. between-group communication depends on, amongst other factors, population densities and group sizes which I proved both to shift along the considered rural-to-urban gradient. I determined latrine sizes, latrine densities and latrine utilization frequencies relative to their distance to the nearest burrow at 15 different study sites. Latrine densities and utilization frequencies increased with increasing distance from the burrow in suburban and urban populations whereas at rural sites, largest latrines and those containing the most fecal pellets were close to the burrow, suggesting that within-group communication prevailed.
To sum up, for the first time, I was able to relate shifts in the ecology and behavior of the European rabbit as adaptations to a gradual anthropogenic habitat alteration that are typical for “urban exploiters”. Especially the suburban habitat provides high landscape heterogeneity (“edge habitat“) which is essential for high and stable rabbit populations. Moreover, here, comparably low human disturbance and predation pressure are given in contrast to the agriculturally transformed, open landscapes which are nowadays typical for most rural areas in central Europe. I argue that this mainly leads to the observed behavioral changes along the rural-to-urban gradient. Future plans for rural land management actions should aim to increase refuge availability by generating networks of ecotones. This would also benefit species that depend on similar ecosystem structures as the European rabbit and are on decline in Germany.
Xenorhabdus and Photorhabdus bacteria are gaining more and more attention as a subject of research because of their unique yet similar life cycle with nematodes and insects. This work focused on the secondary metabolites that are produced by Xenorhabdus and Photorhabdus. With the help of modern HPLC-MS methodologies and increasingly available bacterial genome sequences, the structures of unknown secondary metabolites could be elucidated and thus their biosynthesis pathways could be proposed, too.
The first paper reported 17 depsipeptides termed xentrivalpeptides produced by the bacterium Xenorhabdus sp. 85816. Xentrivalpeptide A could be isolated from the bacterial culture as the main component. The structure of xentrivalpeptide A was elucidated by NMR and the Marfey´s method. The remaining xentrivalpeptides were exclusively identified by feeding experiments and MS fragmentation patterns.
The second paper described the discovery and isolation of xenoamicin A from Xenorhabdus mauleonii DSM17908. Additionally, other xenoamicin derivatives from Xenorhabdus doucetiae DSM17909 were analyzed by means of feeding experiments and MS fragmentation patterns. The xenoamicin biosynthesis gene cluster was identified in Xenorhabdus doucetiae DSM17909.
The manuscript for publication focused on the biosynthesis of anthraquinones in Photorhabdus luminescens. The Type II polyketide synthase for the biosynthesis of anthraquinone derivatives was discovered in P. luminescens in a previous publication by the Bode group,1 in which a partial reaction mechanism for the biosynthesis has been proposed. The manuscript reported in this thesis however elucidated the biosynthetic mechanisms in a greater detail as compared to the previous publication. Particularly, the biosynthetic mechanism was deciphered through heterologous expression of anthraquinone biosynthesis (ant) genes in E. coli. Additionally, deactivation of the genes antG encoding a putative CoA ligase and antI encoding a putative hydrolase, was performed in P. luminescens. Selected ant genes were over-expressed in E. coli as well as the corresponding proteins purified for in vitro assays. Model compounds were chemically synthesized as possible substrates of AntI and were used for in vitro assays. Here, it was revealed that the CoA ligase AntG played an essential role in the activation of the ACP AntF. Furthermore, a chain shortening mechanism by the hydrolase AntI was identified and was further confirmed by in vitro assays using model compounds. Additionally, this chain shortening mechanism was supported by homology based structural modeling of AntI.
The application of natural products (NPs) as drugs and lead compounds has greatly improved human health over the past few decades. Despite their success, we still need to find new NPs that can be used as drugs to combat increasing drug resistance via new modes of action and to develop safer treatments with less side effects.
Entomopathogenic bacteria of Xenorhabdus and Photorhabdus that live in mutualistic symbiosis with nematodes are considered as promising producers of NPs, since more than 6.5% of their genomes are assigned to biosynthetic gene clusters (BGCs) responsible for production of secondary metabolites. The investigation on NPs from Xenorhabdus and Photorhabdus can not only provide new compounds for drug discovery but also help to understand the biochemical basis involved in mutualistic and pathogenic symbiosis of bacteria, nematode host and insect prey.
Nonribosomal peptides (NRPs) are a large class of NPs that are mainly found in bacteria and fungi. They are biosynthesized by nonribosomal peptide synthetases (NRPSs) and display diverse functions, representing more than 20 clinically used drugs. Although a large number of NRPs have been identified in Xenorhabdus and Photorhabdus, the advanced genome sequencing and bioinformatic analysis indicate that these bacteria still have many unknown NRPS-encoding gene clusters for NRP production that are worth to explore. Therefore, this thesis focuses on the discovery, biosynthesis, structure identification, and biological functions of new NRPs from Xenorhabdus and Photorhabdus.
The first publication describes the isolation and structure elucidation of seven new rhabdopeptide/xenortide-like peptides (RXPs) from X. innexi, incorporating putrescine or ammonia as the C-terminal amines. Bioactivity testing of these RXPs revealed potent antiprotozoal activity against the causative agents of sleeping sickness (Trypanosoma brucei rhodesiense) and malaria (Plasmodium falciparum), making them the most active RXP derivatives known to date. Biosynthetically, the initial NRPS module InxA might act iteratively with a flexible methyltransferase activity to catalyze the incorporation of the first five or six N-methylvaline/valine to these peptides.
The second publication focuses on the structure elucidation of seven unusual methionine-containing RXPs that were found as minor products in E. coli carrying the BGC kj12ABC from Xenorhabdus KJ12.1. To confirm the proposed structures from detailed HPLC-MS analysis, a solid-phase peptide synthesis (SPPS) method was developed for the synthesis of these partially methylated RXPs. These RXPs also exhibited good effects against T. brucei rhodesiense and P. falciparum, suggesting RXPs might play a role in protecting insect cadaver from soil-living protozoa to support the symbiosis with nematodes.
The third publication presents the identification of a new peptide library, named photohexapeptide library, which occurred after the biosynthetic gene phpS was activated in P. asymbiotica PB68.1 via promoter exchange. The chemical diversity of the photohexapeptides results from unusual promiscuous specificity of five out of six adenylation (A) domains being an excellent example of how to create compound libraries in nature. Furthermore, photohexapeptides enrich the family of the rare linear D-/L-peptide NPs.
The fourth publication concentrates on the structure elucidation of a new cyclohexapeptide, termed photoditritide, which was produced by P. temperata Meg1 after the biosynthetic gene pdtS was activated via promoter exchange. Photoditritide so far is the only example of a peptide from entomopathogenic bacteria that contains the uncommon amino acid homoarginine. The potent antimicrobial activity of photoditritide against Micrococcus luteus implies that photoditritide can protect the insect cadaver from food competitor bacteria in the complex life cycle of nematode and bacteria.
The last publication reports a new family of cyclic lipopeptides (CLPs), named phototemtides, which were obtained after the BGC pttABC from P. temperata Meg1 was heterologously expressed in E. coli. The gene pttA encodes an MbtH protein that was required for the biosynthesis of phototemtides in E. coli. To determine the absolute configurations of the hydroxy fatty acids, a total synthesis of the major compound phototemtide A was performed. Although the antimalarial activity of phototemtide A is only weak, it might be a starting point towards a selective P. falciparum compound, as it shows no activity against any other tested organisms.
In the present study the cryo-immunogold technique was used and optimized for investigating the ultrastructure and immunolabeling of synaptic proteins. It is evidently a suitable method for the localization of membrane proteins since the antigens are not treated with any chemical denaturation before immunolabeling except for the fixation and since the antigens are directly exposed to the surface of the cryo-ultrasections. The v-SNARE VAMP II and the vesicle-associated proteins SV2 and Rab3A were detected extensively at small vesicles in the mossy fiber terminals. The t-SNARE SNAP-25, and N-type and P/Q type Ca2+ channels were allocated to the plasma membrane both at the active zone and outside the active zone. SNAP-25 and N-type Ca2+ channels appeared also at synaptic vesicles. A significantly increased immunolabeling of VAMP II, SV2, Rab3A, SNAP-25 and N-type Ca2+ channels was found at the active zones of fast synapses, indicating a concentration of these proteins at sites of exocytosis. The widespread distribution of the t-SNARE SNAP-25 at the axonal plasma membrane reveals that membrane-targeting specificity cannot be determined solely by v/t-SNARE interactions. Additional control components are required to assure the docking and exocytosis of the synaptic vesicles at active zones. The novel protein Bassoon was only found at active zones of central synapses and showed the highest specific labeling among all proteins investigated. Its labeling pattern implies an association of Bassoon with the presynaptic dense projections, the structural guide for vesicle exocytosis. The involvement of Bassoon in the organization of the neurotransmitter release site suggests that Bassoon may play an important role in determining the specificity of vesicle docking and fusion. In the neurosecretory endings of neurohypophysis the synaptic proteins VAMP II, SNAP- 25, SV2, Rab3A, and the N-type Ca2+ channels showed a preferential labeling over microvesicles. Moreover, the immunolabeling intensity of these proteins over microvesicles corresponded closely to that over synaptic vesicles. This suggests that these synaptic proteins share an identical association with synaptic vesicle and microvesicles. A significant labeling of SNAP-25, the N-type Ca2+ channels and VAMP II was also detected at the plasma membrane near the clustered microvesicles, indicating the competence of microvesicles for docking and exocytosis along the plasma membrane in the absence of active zones. No significant labeling of VAMP II, SNAP-25, SV2 and N-type Ca2+ channel was observed at the membrane of neurosecretory granules. This is in agreement with the notion that synaptic vesicles and microvesicles possess regulatory mechanisms for exocytosis different from those of granules. In contrast, a/ß-SNAP and NSF were found on the granules, and Rab3A and the P/Q-type Ca2+ channels on granules in a subset of terminals. Rab3A is associated specifically with the oxytocin-containing granule population. Interestingly, some plasma membrane proteins, such as SNAP-25 and even N-type Ca2+ channels and P/Q-type Ca2+ channels, were observed not only at the plasma membrane but also at the vesicular organelles. This suggests that these vesicular organelles may be involved in transporting newly synthesized proteins from the soma to the plasma membrane of the terminal. Furthermore, the vesicular pool of the Ca2+ channels may serve in the stimulationinduced translocation into the plasma membrane when required. Using the conventional preembedding method with Epon and the post-embedding method with LR Gold, VAMP II was localized at vesicular organelles of varying size and on horseradish peroxidase filled endocytic organelles in cultured astrocytes, with and without stimulation in the presence of the horseradish peroxidase. This indicates that VAMP II is involved in the cycle of vesicular exocytosis and endocytosis in astrocytes. U373 cells are capable of expressing all three members of the synaptic SNARE complex (v-SNARE VAMP II, t-SNARE syntaxin I and SNAP25). This indicates the competence of U373 to carry out regulated exocytosis by means of the classical SNARE mechanism. In addition, the ubiquitous v-SNARE cellubrevin and the endosome-associated small GTPbinding protein Rab5 could be expressed in U373 cells. All recombinant synaptic proteins investigated in U373 cells revealed a punctuate cellular distribution under the fluorescence microscope, suggesting that they are mainly associated with intracellular compartments. The cryo-electron microscopy provided direct evidence for the association of all expressed proteins with electron-lucent vesicular organelles. It further supports the potential of U373 MG cells to release low molecular weight messengers by a regulated exocytosis mechanism. In addition, myc-VAMP II was found on dispersed granules. Probably, VAMP II also participates in the exocytosis event of granules in U373 cells. Gold labeling for the two presumptive t-SNAREs syntaxin I and SNAP-25 in U373 cells was confined to the vesicular organelles. At the ultrastructural level no significant labeling was identified at the plasma membrane. The high level of colocalization of the two SNARE proteins VAMP II and syntaxin I in the cell body and in cell processes suggests that the two proteins are mostly sorted into identical vesicular organelles. A partial colocalization of VAMP II and cellubrevin as well as of VAMP II and Rab5 was observed under the fluorescence microscope. At the ultrastructural level, a colocalization of VAMP II and cellubrevin as well as of VAMP II and Rab5 was found on some clustered vesicles. The partial colocalization of VAMP II and cellubrevin implies that they similarly function as v-SNAREs. The partial colocalization of Rab5 with VAMP II in U373 cells suggests that the endosomal protein Rab5 is associated with VAMP II-containing organelles during some stages of their life cycle.