590 Tiere (Zoologie)
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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.
The Southern Ocean (SO) is one of the most pristine regions of our Planet, characterised by high levels of biodiversity (5% of the global diversity) (David and Saucède 2015) and hosting a unique fauna (up to 90% of SO species are endemic) (De Broyer and Danis 2011; Chown et al. 2015). Yet, the knowledge on SO biodiversity is still far from being completed. In addition, the knowledge on the impact that changing environments have on SO species-richness is very little and for some groups, it is still totally unknown. For instance, most of studies generally focus on one single species such as Antarctic krill (Kawaguchi et al. 2011), Clio pyramidata Linnaeus, 1767 (Orr et al. 2005), Globigerina bulloides d'Orbigny, 1826 (Moy et al. 2009), or only on a high taxonomic level (e.g. phylum, class): Echinodermata, Crustacea, Mollusca, Porifera, Bryozoa, Brachiopoda, Hydrozoa, Ascidiacea, Holoturoidea
(Barnes 1999; Rowden et al. 2015; Post et al. 2017; Gutt et al. 2019; Vause et al. 2019; Pineda-Metz et al. 2020). Ultimately, the influence of sea-ice coverage on benthic species diversity was totally unknown prior to this study. In light of this, the objectives of the thesis are:
1. To expand the knowledge on shelf and deep-sea peracarid assemblage structure and abundance on a small regional (Weddell Sea) and on a large regional (Atlantic sector of the SO and South Atlantic Ocean) geographic scale.
2. To assess the environmental variables driving peracarid assemblage structure and abundance from the above mentioned areas.
3. To investigate SO benthic isopod species diversity from the Atlantic sector of the SO and assess the influence of environmental variables on their species-richness and composition.
4. To describe new possible peracarid species by means of integrative taxonomy, using morphological descriptions and whole genome sequencing analyses to support the species identification.
Objective outcomes: The present thesis provides new information on the abundance and assemblage structure based on 64766 peracarid crustaceans from different 28 locations within the Atlantic sector of the SO continental shelf and deep sea (Chapters I-II). These locations are characterised by different environmental conditions, for instance different sea-ice concentrations. Results from Chapters I-II confirmed the dominance of peracarid assemblages in the benthos, with amphipods being the most abundant group, followed by isopods. Sea ice was identified as the main driver shaping benthic peracarid assemblage structure (Chapter I). On a larger geographic scale and wider bathymetric range (e.g. including sampling locations from previous studies performed in the South Atlantic Ocean
and at a depth range from 160 to ~6000 m), depth was the main physical variable driving peracarid assemblage structure (Chapter III). In addition, 16157 isopod specimens from the Atlantic sector of the SO were identified to species level at a smaller scale (Chapter IV). In this case, sea ice was identified as the main physical driver affecting isopod diversity and composition among sampling locations (Chapter IV). Reduced concentration of sea ice
causes a decrease in isopod biodiversity, thus climate change was identified as a huge threat for this taxon and for SO benthos in general. During the identification process, two new isopod species were discovered (Chapter V). The two new species (Notopais sp.1 n. sp. and Notopais sp.2 n. sp.) were accurately described and identified by means of integrative taxonomy. This provided the first whole genome sequencing of benthic isopods from the SO and the first complete mitochondrial genome of the genus Notopais (Chapter V). Thanks to the collaboration with the University of Genoa (Dipartimento di Scienze della Terra dell'Ambiente e della Vita, DISTAV, Italy) and the National Antarctic Museum (MNA) in Genoa, two new SO species of the suborder Valvifera G. O. Sars, 1883 were described by means of classical taxonomy. In this case, a molecular approach could not be used because both new species were represented by a single specimen, therefore it was important to preserve the integrity of the holotypes (Chapters VI-VII).
Genetic and genomic tools have provided researchers with the opportunity to address fundamental questions regarding the reintroduction of species into their historical range with greater precision than ever before. Reintroduction has been employed as a conservation method to return locally extinct species to their native range for decades. However, it remains unknown how genetic factors may impact population establishment and persistence at the population and metapopulation level in the short- and long-term. Genetic methods are capable of producing datasets from many individuals, even when only low quality DNA can be collected. These methods offer an avenue to investigate unanswered questions in reintroduction biology, which is vital to provide evidence based management strategies for future projects. The Eurasian lynx (Lynx lynx) and European wildcat (Felis silvestris) are elusive carnivores native to Eurasia and have been the subject of multiple reintroduction attempts into their native range. During the 19th and 20th century, the Eurasian lynx was extirpated from West and Central Europe due to increasing habitat fragmentation and persecution. Similarly, the European wildcat was the subject of human persecution, residing in a few refugia in West and Central Europe. After legal protection in the 1950s, subsequent reintroduction projects of both species began in the 1970s and 1980s and continue to the present. Despite this large focus on species conservation, little attention has been given to the consequences these reintroductions have on the genetic composition of the reintroduced populations and if the populations have a chance of persisting in the long term. These species have not yet benefited from the large range of genetic and genomic techniques currently available to non-model organisms, leaving many fundamental aspects of their reintroduction poorly understood. In my dissertation, I investigate demography, population structure, genetic diversity and inbreeding at the population and metapopulation level in both species. In the introduction, which lays the foundation for the subsequent chapters of this PHD, I provide background on reintroduction, its role in conservation and the genetic consequences on populations, especially populations of apex and mesocarnivores. In Publication I, I investigated the reemergence of the European wildcat in a low mountain region in Germany using fine-scale spatial analysis. I found that the reintroduced population has persisted and merged with an expanding natural population. The reintroduced population showed no genetic differentiation from the natural population suggesting there is a good chance this population has retained sufficient genetic diversity despite reintroduction. In Publication II, I tracked population development and genetic diversity over 15 years in a reintroduced lynx population to determine the genetic ramifications on a temporal scale. I found slow genetic erosion after a period of outbreeding, which fits in line with other reintroduced taxa sharing similar demographic histories. I also found the number of genetic founders to be a fraction of the total released individuals, indicating that reintroduced populations of elusive carnivores may have fewer founder individuals than previously thought. In Publication III, I sampled all surviving lynx reintroductions in West and Central Europe as well as 11 natural populations to compare levels of genetic diversity and inbreeding across the species distribution. I found that all reintroduced populations have lower genetic variability and higher inbreeding than natural populations, which urgently requires further translocations to mitigate possible negative consequences. These translocations could stem from other reintroduced populations or from surrounding natural populations. The results contribute to a growing body of evidence indicating that inbreeding is likely to be more prevalent in wild populations than previously understood. Finally, in the discussion I explore how genetic methods can be applied to post-reintroduction monitoring of felid species to illuminate questions relating to genetic composition after release. The methods employed in these studies and in future work will be highly dependent on the research questions posed. Additionally, I investigate the drivers of the observed genetic patterns including founder size, source population, environmental factors, and population growth. I found that genetic diversity loss patterns across these two felid species are not clearly defined, however, management actions can be taken to mitigate the negative effects of reintroductions. These management actions include further translocation, introducing a sufficient number of released individuals and situating reintroductions adjacent to natural populations. All of these actions can minimize genetic drift and inbreeding, two factors which negatively impact small populations. This thesis further supports mounting evidence that genetic considerations should be assessed before releasing individuals, which allows for incorporation of scientific evidence into the planning process thereby increasing the overall success of reintroduction projects. Ultimately, the resources developed during this dissertation provide a solid baseline and foundation for future work regarding the consequences of reintroductions. This is especially important as an increasing number of species are at risk of extinction and reintroductions of both the European wildcat and Eurasian lynx, as well as many others, are planned in the coming years.
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.
The genus Giraffa likely evolved around seven million years ago in Indo-Asia and spread over the Arabian-African land bridge into Eastern Africa. The oldest fossil of the African lineage was found in Kenya and dated to 7-5.4 Mya. Beside modern giraffe, four additional African species have likely existed (G. gracilis, G. pygmaea, G. stillei, and G. jumae). Based on their morphological similarities, G. gracilis is often considered to be the closest relative of the modern giraffe. Nevertheless, the phylogeny within the genus Giraffa is largely unresolved.
Modern giraffe (Giraffa sp.) have been neglected by the scientific community for a long time and still very little is known about their biology. Traditionally, present-day giraffe have been considered a single species (G. camelopardalis) which is divided into six to eleven subspecies, with nine subspecies being the most accepted classification. This classification was based on morphological differences and geographic ranges. However, recent genetic analyses found hidden diversity within Giraffa and proposed four genetically distinct giraffe species (G. camelopardalis, G. reticulata, G. tippelskirchi, G. giraffa) with presumably little gene flow among them.
Gene flow on a population level is the exchange of genetic information among populations facilitated by the migration of individuals between populations. Additionally, it is an important criterion to delineate species, because many species concepts, especially the Biological Species Concept, rely on the concept of reproductive isolation. Yet, new genetic methods are identifying an increasing number of species that show signs of introgressive hybridization or gene flow among them. Therefore, strict reproductive isolation cannot always be applied to delineate species, especially in young, probably still diverging, species such as giraffe.
Therefore, giraffe are ideal study organisms to investigate the level of gene flow in recently diverged species with adjacent or potentially overlapping ranges. Furthermore, their recent classification as “Vulnerable” by the IUCN and their unreliable distribution maps require the genetic evaluation of their population structure, distribution and conservation status.
In Publication 1 (Winter et al. (2018a), Ecological Genetics and Genomics, 7–8, 1–5), I studied the distribution and matrilineal population structure of Angolan giraffe (G. giraffa angolensis) using sequences from the cytochrome b gene (1,140 bp) and the mitochondrial control region for individuals from across their known range and beyond, and additionally including individuals from all known giraffe species and subspecies. The reconstruction of a phylogenetic tree and a mitochondrial haplotype network allowed to identify the most easterly known natural population of Angolan giraffe, a population that was previously assigned to their sister-subspecies South African giraffe (G. giraffa giraffa), indicating the limit of classification by morphology and geography. Furthermore, the analyses show that Namibia’s iconic desert-dwelling giraffe population is genetically distinct, even from the nearest population at Etosha National Park, suggesting very limited, if any, natural exchange of matrilines. Yet, no geographic barriers are known for this region that would prevent genetic exchange. Therefore, the two populations are likely on different evolutionary trajectories. Limited individuals with an Etosha haplotype further suggest that translocation of Etosha giraffe into the desert population had only a minor impact on the local population. Two separate haplogroups within Etosha National Park suggest an “out of Etosha” radiation of Angolan giraffe to the East followed by a later back-migration.
In Publication 2 (Winter et al. (2018b), Ecology and Evolution, 8(20), 10156–10165), I investigated the genetic population structure of giraffe across their range (n = 137) with focus on the amount of gene flow among the proposed giraffe species with a 3-fold increased set of nuclear introns (n = 21). Limited gene flow of less than one effective migrant per generation, even between the closely related northern (G. camelopardalis) and reticulated giraffe (G. reticulata) further supports the existence of four giraffe species by a different methodology, gene flow. This is significant because most species concepts build on reproductive isolation. Furthermore, this result is corroborated by four distinct major clades in a phylogenetic tree analysis, and distinct clusters in Principal Component Analysis and STRUCTURE analysis. All these analyses suggest a low level of genetic exchange among the four giraffe species and, therefore, a high degree of reproductive isolation in accordance with the Biological Species Concept (BSC). In Addition, only a single individual in 137 was identified as being potential of natural hybrid origin, which promotes the four-species concept further. ...
During the last decades mammalian intracranial structures like the ethmoidal region have rarely been a focus of morphological studies, as they required invasive techniques. Contrary, the ontogeny of the fetal nasal capsule could easily be investigated based on histological material. Since the early 21st century modern imaging techniques like high-resolution computed tomography (μCT) reveal non-destructive insights into the mammalian skull. Furthermore, visualization software enables the virtual reconstruction of the tissues and additionally their morphometric analyses. However, the use of morphometric approaches on the nasal cavity is still scarce. Moreover, the turbinal skeleton is generally regarded as a unit, or the rostral respiratory part is compared to the caudal olfactory part; but the distinct olfactory turbinals have been considered only in a few studies.
The present study focuses on the highly diverse facial shape of the dog (Canis lupus familiaris) that evolved during domestication. Due to human-controlled breeding and care the natural selective pressure in prehistoric dogs has been replaced continually by artificial selection. As a consequence, harmful mutations on gene loci which e.g., control facial length growth got fixed within an extremely short time. According to veterinarian studies the turbinals of short snouted breeds continue their growth after the elongation of the facial bones has stopped prematurely. However, such investigations are based on low-resolution CT or MRT data and the morphological descriptions are vague. Referring to the elongation of the face in dolichocephalic breeds no former study has dealt with the detailed morphology of their turbinal skeleton so far.
The current study is based on comparative anatomical, morphometric, morphofunctional, and ontogenetic patterns of the dog’s turbinal skeleton. The 32 macerated skulls and four histological serial sections represent eleven breeds which cover different snout lengths (brachycephalic, mesaticephalic, dolichocephalic; according to two length indices), functional groups (scent hound, sighthound, companion/toy), and breeding histories (ancient pure-breeding associated with an unchanged appearance, modern time fashion breeding). The nasal cavity of the selected skulls was μCT-scanned and virtual 3D models of the turbinal skeleton were reconstructed. The breeds have been compared with each other in their number of olfactory turbinals, in the morphology of all turbinals and the lamina semicircularis as well as in their morphometrics and ontogeny. Based on morphological and ontogenetic patterns a new terminology of the interturbinals was established. The morphometric data covers the measurement of the relative turbinal surface area (IAT) and the calculation of the surface density (SDEN) and the turbinal complexity (TC). For the latter parameter a new morphometric approach was developed. For the ontogenetic comparison histological serial sections of perinatal dog stages have been consulted. As the dog’s ancestor macerated skulls of three adult Eurasian wolves (Canis lupus lupus) function for outgroup comparison and represent the grundplan with which the breeds are compared.
The results support former studies concerning a species-specific number of the fronto- and ethmoturbinals: in the Eurasian wolf and all postnatal dogs under study three ethmoturbinals and three frontoturbinals are observed. Additionally, two types of interturbinals are distinguished, namely four prominent interturbinals which are present in nearly all individuals and show a homologous pattern, and a variable number of additional interturbinals which differ in their shape among the dogs. Generally, longer snouted breeds have more additional interturbinals, so the total number of olfactory turbinals is increased to a maximum of 16 in the borzoi, whereas several short snouted breeds have only nine olfactory turbinals due to the loss of additional interturbinals and one prominent interturbinal. Regarding ontogeny the growth of the respiratory and the olfactory turbinals and the lamina semicircularis is highly associated with the growth of the facial bones after birth. As the viscerocranium of brachycephalic breeds is subjected to a postnatal growth inhibition the ethmoidal region stops growing prematurely, too. The turbinals of both functional parts develop less accessory lamellae that results in the reduction of the three morphometric parameters IAT, SDEN, and TC. The increase of all these three parameters with increasing snout length proves a correlation between both variables in the maxilloturbinal, all olfactory turbinals, and the lamina semicircularis in the dog. With the help of the perinatal dog stages plesiomorphic patterns which are present in all adult specimens (e.g., separation of ethmoturbinal I into two laminae, the presence of the uncinate process) were distinguished from less established morphological traits which get preferably reduced in association with brachycephaly (e.g., the anterior process of the posterior lamina of ethmoturbinal I, the caudal processes of frontoturbinal 1 and 2 within the frontal sinus due to the latter’s reduction). Obviously, the driving mechanism behind these and further variations are mutations on gene loci which control ontogenetic processes: the in other studies already described postnatal growth inhibition in the dermal bones of the midface of brachycephalic breeds seems to have a similar effect on the ethmoidal region. The results of the present study serve as basis for the evaluation how far the bony turbinals’ morphology, morphometrics, and ontogeny might be associated with physiological, genetic, neurological, and phylogenetic patterns. Additionally, the growth patterns of the hard tissues need to be compared to those of the soft tissues (i.e. the nasal epithelium).
In order to investigate the diversity of the western honeybee, Apis mellifera L., in West and Central Africa, a total of 204 colonies were sampled from 44 localities in four countries – Nigeria, Niger, Cameroon and Chad. 86 of these colonies, from 23 localities, were subjected to full morphometric analysis. In a principal component analysis (PCA) of the morphometric data, the colonies formed a single cluster. It also revealed that overall size of the body was the most important source of variation between the colonies. A hierarchical structure analysis, followed by a stepwise discriminant analysis, classified the colonies into three distinct morphoclusters; however, these clusters were not geographically demarcated. In another PCA carried out with the samples under investigation and reference samples of A. m. adansonii, A. m. jemenitica and A. m. scutellata, the colonies under investigation again formed one cluster which lying over and extended beyond the clusters of the reference subspecies. This is suggestive of a wider variation in size in the bees under investigation. In a stepwise DA, 94.2% of cross-validated grouped cases were correctly classified and the distances between group centroids were highly significant (p < 0.0005) according to F-statistic. 61 and 22 of the 83 colonies under investigation were assigned to A. m. jemenitica and A. m. adansonii, respectively. Mitochondrial DNA analysis was carried out on 148 colonies from 39 localities. Four mitochondrial haplotypes, previously reported from Africa and belonging to the African mitochondrial lineage, A, were detected: A1 (n = 62), A4 (n = 70), A4' (n = 15) and A14 (n = 1). The overall haplotype diversity was low (h = 0.478 ± S. E. 0.057). A chi-square test for association was conducted between haplotypes and type of vegetation, latitude, longitude, altitude, temperature and rainfall, severally. There was a statistically significant association between haplotype and each of the six variables and the association was strong with latitude, moderate with vegetation and rainfall and weak with the remaining variables. The neighbour-joining, maximum likelihood and maximum parsimony trees, obtained from sequence variation of the cytochrome b gene of mitochondrial DNA, showed that the samples, from the current study, unambiguously clustered with the reference sequences of A. m. scutellata from Kenya, but without showing further subdivision within this sub-Saharan cluster. 133 workers (one per colony) collected from 38 localities were subjected to microsatellite analysis. A total of 292 different alleles were recorded for the 15 microsatellite loci used. All microsatellite loci were polymorphic and the number of different alleles per locus ranged between 10, in locus At163, and 31, in locus A029. Heterozygosity (or gene diversity) was high in all loci. The unbiased expected heterozygosity, which is a better expression of gene diversity, was 0.861 ± S.E. 0.017. The overall FST value, which is a good estimate of genetic differentiation of populations, was very low: 0.007 ± S.E. 0.001 (0.001 - 0.014). AMOVA and Bayesian assignment showed no differentiation of the investigated populations. Based on morphometric analysis, the results of this study present the honeybees of western Africa as a single entity with an internal variation which lacks a geographical demarcation. Consequently the results do not support the splitting of the honeybees of the region into the two subspecies, A. m. adansonii and A. m. jemenitica, as reported in the literature. More morphometric, molecular, physiological and behavioural studies are required to confirm the taxonomic status of the honeybees of the region. Meanwhile, the use of A. m. adansonii, as the sole sub-specific name for the honeybees of West and Central Africa, is recommended.
Diese Dissertation befasst sich mit den Auswirkungen von nicht letalen Dosen von Neonikotinoiden auf Bienen. Neonikotinoide stellen eine Klasse von Insektiziden dar, die auf den nikotinischen Acetylcholin Rezeptor wirken. In dieser Dissertation wurden die Neonikotinoide Imidacloprid, Clothianidin und Thiacloprid benutzt. Die beiden erst genannten unterliegen zum Zeitpunkt des Verfassens dieser Arbeit einem temporären Verkaufs- und Ausbringungs-Stopp. Damit sind die Ergebnisse dieser Arbeit wichtig für die Bewertung der Gefahren von Neonikotinoiden. Neonikotinoide werden im großen Maße in der Landwirtschaft als Spritzmittel und Saatgutbeize eingesetzt. Dabei können sie in Rückständen von Bienen beim Sammeln von Nektar und Pollen aufgenommen und zum Stock gebracht werden. Um einen weiten Blick auf die Auswirkungen der Stoffe zu werfen wurden deshalb Experimente an einzelnen Sammlerinnen durchgeführt, ebenso wie an Bienenvölkern, bei denen die Substanzen verfüttert wurden. Als neuronal aktive Substanzen können sie die normale Funktion des Nervensystems von Bienen beeinflussen, was Veränderungen im Verhalten hervorrufen kann. Dies zeigt sich in Veränderungen in der Bewegung, Orientierung oder auch Interaktion mit anderen Bienen. Die Wirkung am Rezeptor variiert, trotz gleichen molekularen Ziels, stark zwischen den verwendeten Neonikotinoiden. Clothianidin wurde als Agonist beschrieben, der sogar stärkere Ströme als Acetylcholin bei gleicher Konzentration hervorrufen kann. Imidacloprid dagegen wurde bereits als partieller Agonist beschrieben, der geringere Ströme über den Rezeptor auslöst. In dieser Arbeit wurde ein erster Versuch durchgeführt um Thiacloprid ebenfalls als Agonist am nikotinischen Acetylcholin Rezeptor der Biene zu beschreiben. Hierbei wurde an einer Zelle in Kultur ein geringerer Strom ausgelöst.
Bienenvölker wurden unter kontrollierten Bedingungen gehalten, bei denen je eins der Neonikotinoide Clothianidin, Imidacloprid oder Thiacloprid in das Futter gemischt wurden. Hierfür wurden Dosen gewählt, bei denen davon ausgegangen werden konnte, dass keine akute Beeinflussung der Sammlerinnen bestand. Es konnte festgestellt werden, dass chronisches Füttern mit einer Zuckerlösung mit 8,876 mg/kg Thiacloprid zu einer verringerten Sammelleistung führte. Ebenso wurde die Entwicklung der Eier stark eingeschränkt, wobei die Königin weiterhin Eier legte. Es konnten nur vereinzelte verdeckelte Brutzellen, die ein spätes Entwicklungsstadium der Bienen darstellen, gefunden werden. Damit konnte gezeigt werden, dass geringe Dosen die Larval-Entwicklung von Bienen beeinflussen, eventuell durch Einflüsse auf die Kommunikation zwischen Ammenbienen und der Brut.
Um Auswirkungen auf einzelne Tiere zu zeigen, wurden unterschiedliche Parameter im Heimflug von Bienen nach Fütterung mit je einem der Neonikotinoide analysiert. Bienen mussten sich nach der Fütterung orientieren und von einer neuen Position den Heimweg zum Stock finden. Der Heimflug wurde per Radar verfolgt und so ein Flugprofil erstellt, das aus zwei Flugphasen bestand. Diese wurden durch die Navigation nach Vektorintegration und durch Landmarken unterteilt. Aus dem Flugprofil konnte abgelesen werden, wie lange die Bienen für die Phasen des Flugs benötigten, in welchem Hauptflugwinkel sie die erste Flugphase absolvierten, in welche Richtung sie am Ende der ersten Flugphase flogen und wie gerichtet der Flug war. Auch wurde erfasst, ob die Bienen überhaupt in der Lage waren zum Stock zurückzukehren. Hier zeigte sich, dass die Fütterung mit Zuckerwasser mit 0,6 µM und 0,9 µM Imidacloprid, ebenso wie mit 0,1 mM Thiacloprid zu einer verringerten Heimkehrwahrscheinlichkeit führte. In der ersten Flugphase konnte auch gezeigt werden, dass 0,2 µM Clothianidin im Zuckerwasser zu einem schnelleren Flug führte und dass der Flugwinkel im Vergleich zur Kontrolle in Richtung der wahren Position des Stocks verschoben war. Beide Imidacloprid-Gruppen zeigten eine ähnliche, signifikante Verschiebung des Flugwinkels, ebenso konnte im Flug selbst eine häufige Änderung der Richtung festgestellt werden. In der zweiten Flugphase zeigte sich, dass Bienen, welche mit Thiacloprid behandelt wurden häufiger eine inkorrekte Heimflugrichtung wählten, was in längeren Heimflügen resultierte. Die mit Clothianidin behandelten Bienen legten eine längere Flugstrecke zurück. Bienen, welche Imidacloprid beider Konzentrationen konsumierten, zeigten einen häufigen Wechsel ihrer Flugrichtung. Damit konnten bei allen drei gewählten Neonikotinoiden Einflüsse auf spezifische Komponenten der Navigation von Bienen gefunden und Einschränkungen im Heimkehr- und Orientierungsverhalten einzelner Sammlerinnen gezeigt werden. Somit konnten die eingehenden Fragen zumindest teilweise beantwortet werden und die Datenlage zur Frage der Schädlichkeit der, auch politisch umstrittenen, Substanzen erweitert werden.
The mammalian family of bears (Ursidae) comprises eight extant species, occurring on four different continents. Among them are the iconic and well-known brown and polar bears, both widely distributed across the Northern hemisphere. Their intraspecific genetic structuring has been extensively investigated, albeit with a focus on genetic markers from maternally inherited parts of their genomes (mitochondrial DNA). The evolutionary relationship and divergence time between brown and polar bears have recently triggered an extensive debate, while less focus has been put on to other parts of the ursid phylogeny, particularly to a clade of three Asian bear species. To date, whole genomes of more than 100 bear individuals from four different species have been sequenced. Yet, one fundamental part of the genome has been largely omitted from specific analyses, in bears as well as in most other mammals: the Y chromosome.
The mammalian Y chromosome provides a unique perspective on the evolutionary history of organisms due to its distinct features, and specifically reflects the patriline because of its male-specific inheritance. The characteristics of this chromosome make it well suited to complement and contrast evolutionary inferences based on other genetic markers, and to uncover processes like sex-biased gene flow and hybridization. The unique insights that can be gained from analyses of Y-linked genetic variation made me utilize this part of the genome to investigate the evolution of male lineages in bears. Studying the patriline is particularly promising in this taxonomic group because of male-biased dispersal and a complex and fast radiation of bears. The analysis of Y-chromosomal genetic markers is thus the common theme of this dissertation: I present the identification of large amounts of Y-chromosomal sequence, the development of male-specific markers from such sequences, and the application of these markers to trace the evolution of male lineages of different bear species.
Specifically, I developed a molecular sex determination system based on the detection of two Y-linked fragments that allows to reliably discriminate between females and males from seven different bear species (Bidon et al. 2013). The approach is highly sensitive, bear-specific, and can be applied in standard molecular laboratories. This makes it valuable in conservation genetics and forensic applications, e.g. to analyze non-invasively collected samples.
Furthermore, I used Y-linked markers in a comprehensive and range-wide sample of brown and polar bears, and show that male-biased gene flow plays an important role in distributing genetic material throughout the ranges of both species (Bidon et al. 2014). In brown bears, I detected a lack of paternal population structuring which is in strong contrast to the detailed structuring of the matriline.
Analyzing Y-chromosomal sequences from all eight bear species, I present a phylogeny of the patriline that largely resembles the topology from other nuclear markers but is different from the topology of the mitochondrial gene tree (Kutschera et al. 2014). This discordance among loci generates interesting hypotheses about inter-species gene flow, particularly among American and Asiatic black bears.
With the identification of almost two million basepairs of Y-chromosomal sequence and the analysis of an unprecedented large male-specific dataset in polar bears, a high-resolution view on the distribution of their intraspecific variation was obtained (Bidon et al. 2015). In particular, two clades that are divergent but do not show pronounced phylogeographic structure were detected, confirming the great dispersal capacity of males of this high arctic species.
This dissertation thus represents a comprehensive investigation of Y-linked genetic variation on the intra- and interspecific level in a non-model organism. With my research, I contribute to an increased understanding of the complex evolutionary history of bears. In particular, I show that male-biased gene flow strongly influences the distribution of nuclear genetic variation, and that the contrast between phylogenies of differentially inherited markers can help to understand interspecific hybridization between closely related species. Moreover, my findings demonstrate the potential of Y-chromosomal markers to uncover unknown evolutionary patterns and processes. This applies not only to bears but to many species, even such that are generally well known and well described.
Snake bite envenoming often results in disability or death of breadwinners of poor families in the rural tropics and the subtropics of Nepal. Identification of the medically relevant snake species, circumstances of venomous snake bites, prehospital care of their bites and human responses to snakes and snake bite is, therefore, crucial to enable victims or first aider to select the appropriate first aid measures, physicians to anticipate complications and to use appropriate treatment protocols as well as the local community to implement prevention strategies. Inadequate educational gaps exist in Nepal and hinder identification of snakes involved in bites. To fill this gap, I aim to provide an evidence-based list of medically relevant snake species. Snake specimens brought by patients bitten or their attendants from the tropical and subtropical regions in southeastern, southcentral, and southwestern Nepal to snake bite treatment centres over a period from 2010 through 2014, were taxonomically identified and medical records of envenoming were evaluated.
In Nepal, the epidemiology of snake bite is poorly known. Here I describe the ecological circumstances of proven krait (Bungarus spp.) and Russell´s Viper (Daboia russelii) bites to elucidate and examine, whether environmental circumstances or human behaviour contributed to envenoming. In a cross-sectional study, data about prehospital care, environmental circumstances of 46 krait and 10 Russell´s Viper bites were evaluated. Patients were interviewed using structured interview forms. Snake bite prone communities were surveyed to test people´s knowledge on snakes and their attitude towards venomous snakes in general.
Of 349 snakes involved in bites, 199 (57%) specimens were found to be medically relevant venomous snakes that included 11 species belonging to six genera and two families. Among them, Naja naja (n = 76, 22%), Bungarus caeruleus (n = 65, 19%) and Trimeresusurs albolabris (n = 10, 3%) were the most widely distributed snakes. Daboia russelii (n = 10, 3%) was found to be restricted to the southwestern part of Nepal. For B. walli, a previously poorly known species, 13 voucher specimens represent the first country records of this species as well as the first documented cases of involvement in snake bite envenoming by this species in Nepal.
Numerous snake bites (33%) occurred at night, during the rainy season, and are mainly due to Bungarus species, particularly B. caeruleus. Bites of cobras and Russell’s Vipers are a risk at daytime. Evaluation of data regarding the place where the bite happened, indicates that the snake bite risks appear to be as high in residential areas, in and around houses, as in rural areas. In cases of kraits (n = 46), 61% of the bites occurred while the victim was sleeping indoors, those of Russell´s Vipers mainly during agricultural activities in the fields. Analysis of socio-demographic data revealed that both krait and viper bites predominantly affected farmers or their family members. However, snake bites involved also people of higher socio-economic status, which suggests that it is not a health problem of poor people only living in the rural areas of Nepal.
A small number of snake bite victims (n = 7) sought help from traditional healers, but most patients went to hospitals for medical treatment using motorbikes (65%) or were transferred by ambulance cars (22%). As a first aid measure, most patients (78%) had used a tourniquet, which is of doubtful value and has often severe sequelae, instead of applying the WHO recommended pressure immobilisation bandage or local compression pad. The overall case fatality rate was calculated to be 10%, but up to 17% in cases of Bungarus spp. bites.
Rural community people were found to be extremely afraid of snakes, a major reason for indiscriminate killing of even harmless snakes, e.g., Lycodon aulicus, which were wrongly considered to be venomous. This is mainly due to the poor knowledge on snakes in general and on their role in providing ecological services, which may eventually lead to a decline in snake populations and even the extinction of rare species.
The results of the present study strongly emphasize that snake bite is an important public health issue in Nepal. There is an urgent need to improve the knowledge of people on snakes and to try changing their attitudes towards these reptiles, in addition to documenting the biodiversity and distribution of medically relevant snakes, the epidemiology and circumstances of their bites. Avoiding high-risk behaviour (e.g., killing of snakes), using screened doors and windows are some of the suggested measures preventing snake bite. Early and accurate identification of the snakes involved should help physicians to apply timely treatment, eventually referring the patient to the appropriate hospital. This also has important implications in developing public health and conservation strategies, to the benefit of the people of Nepal.