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Die Spinozerebelläre Ataxie Typ 2 (SCA2) ist eine autosomal dominant vererbte neurodegenerative Krankheit, welche durch die Expansion des Trinukleotids Cytosin-Adenin-Guanin von ~22/23 auf >32 im Ataxin-2 Gen (ATXN2) verursacht wird. Dieses Trinukleotid codiert für die Aminosäure Glutamin weshalb SCA2 auch zu den Polyglutaminerkrankungen zählt. Zu dieser Gruppe zählen außerdem fünf weitere SCA-Subtypen sowie drei weitere neurodegenerative Erkrankungen, darunter die Huntington-Krankheit.
SCA2 wurde 1971 zum ersten Mal von Wadia und Swami beschrieben und unterscheidet sich von den anderen SCAs aufgrund der typischen Störung der sakkadischen Augenbewegungen. Weitere klinische Symptome von SCA2 sind Ataxie, Tremor, Dysmetrie, Dysarthrie, Hyporeflexie und Dysdiadochokinese. Die Symptome gehen auf einen neuronalen Verlust insbesondere im Cerebellum, aber auch in anderen Hirnregionen wie zum Beispiel dem Hirnstamm zurück.
Atxn2 wird in weiten Teilen des Zentralnervensystems aber auch in vielen nicht-neuronalen Geweben exprimiert. Es handelt sich um ein überwiegend cytoplasmatisch lokalisiertes Protein, welches im Gegensatz zu vielen anderen SCA-Proteinen cytoplasmatische und nur selten nukleäre Aggregate bildet. Die exakte Funktion von Atxn2 ist bisher unklar, es wurde allerdings mehrfach gezeigt, dass es in die mRNA Translation involviert ist aufgrund seiner Interaktion mit dem PolyA-bindenden Protein PABPC1.
Eine Expansion des Trinukleotids in Ataxin-2 kann nicht nur zu SCA2 führen, sondern stellt bei Wiederholungen zwischen 27 und 32 CAGs auch ein erhöhtes Risiko für eine Erkrankung an Amyotropher Lateralsklerose (ALS) und anderen neurodegenerativen Krankheiten dar. Eine Interaktion zwischen ATXN2 und dem ALS-verursachenden TDP43 (Tardbp) wurde bereits zahlreich beforscht, da Aggregate von ATXN2 in Motoneuronen des Rückenmarks von ALS-Patienten und aggregiertes TDP43 in SCA2-Neuronen beobachtet wurden.
Generell sind die Mechanismen, die zur Pathologie von SCA2 und ALS führen, noch weitgehend unklar. Ziel dieser Arbeit war es daher auf der einen Seite einen Einblick in den Pathomechanismus von SCA2 zu erhalten, indem mögliche oder bereits bekannte Interaktoren in etablierten Atxn2-Mausmodellen untersucht wurden. Auf der anderen Seite wurden zwei neue Mausmodelle charakterisiert, um ihre Eignung für die Erforschung von ALS und SCA2 zu prüfen.
Für den ersten Teil der Arbeit dienten Daten aus mehreren Transkriptomstudien von Atxn2-Knock-Out (KO) und Atxn2-CAG42-Knock-In (KIN) Mäusen als Grundlage. Konnten die Daten mit einer unabhängigen Methode bestätigt werden, folgten weitere Untersuchungen auf mRNA und Proteinebene sowie unter zusätzlicher Verwendung von Zellkultur und Patientenmaterial. Dadurch konnten neue Interaktionspartner von ATXN2 identifiziert und bereits bekannte in diesen Mausmodellen bestätigt werden.
So wurde zum Beispiel eine Interaktion von ATXN2 mit der E3-Ubiquitin-Protein-Ligasekomponente FBXW8 gezeigt und deren Beteiligung am Abbau von expandiertem ATXN2. Außerdem wurde eine Interaktion von FBXW8 mit dem bereits bekannten ATXN2-degradierenden Protein PARK2 gezeigt. Eine Hochregulierung des Fbxw8 Transkripts wurde sowohl im Atxn2-CAG42-KIN-Mausmodell als auch in SCA2-Patientenfibroblasten gefunden, während Park2 in keinem der Modelle signifikant veränderte Transkriptspiegel aufwies. Diese Daten belegen die Relevanz von Fbxw8 für den Abbau von moderat-expandiertem Atxn2 und begründen weitere Studien zur genauen Funktion dieses Proteins im Pathomechanismus von Atxn2.
Des Weiteren wurden diverse Kalziumhomöostasefaktoren untersucht, welche eine konsistente Herunterregulierung der Transkripte in beiden Mausmodellen aufwiesen. Auf Proteinebene zeigten sich jedoch Unterschiede zwischen den Modellen. Diese Daten belegen, dass zwar ähnliche Transkriptveränderungen im KIN- und KO-Modell auftreten, diesen aber vermutlich verschiedene Mechanismen zugrunde liegen. Welche Mechanismen dies genau sind bleibt zu klären, es ist jedoch wahrscheinlich, dass im KIN-Modell die Aggregatbildung sowie in beiden Modellen die Beteiligung von ATXN2 an der Translationregulation eine Rolle spielen. Die Ergebnisse dieser Studie unterstreichen die Relevanz des Ca2+ Signalwegs für die Entwicklung von SCA2.
Der zweite Teil der Arbeit beinhaltet die Charakterisierung einer ATXN2/TDP43 Doppelmutante auf Verhaltensebene sowie die gründliche Evaluierung des Phänotyps einer vollkommen neuen SCA2 Mausmutante. Während in der Doppelmutante trotz doppelter Genmutation nur ein sehr schwacher Phänotyp auf Verhaltensebene festgestellt werden konnte und bis zu einem Alter von 12 Monaten keine Potenzierung der Mutationen zu beobachten war, zeigte die Atxn2-CAG100-KIN Maus signifikante und früh auftretende Pathologie. Neben einer verminderten Überlebensrate, einem Gewichtsverlust und diversen motorischen Störungen, konnten auch Aggregate des mutierten Proteins in diversen Hirnregionen identifiziert werden. Der Atxn2-CAG100-KIN Phänotyp spiegelt die humanen Symptome daher recht gut wider, weshalb diese Mausmutante ein wertvolles Modell für die weitere SCA2-Forschung darstellt.
Zusammengefasst zeigt diese Arbeit die Bedeutung des ATXN2-Interaktors FBXW8 im SCA2-Mausmodell als auch im Patientenmaterial. Sie betont die Relevanz des Atxn2-KO-Modells in Bezug auf Störungen der Kalziumhomöostase und dokumentiert die Alters- und Gewebespezifität dieser Veränderungen. Außerdem beinhaltet sie die vorläufige Beschreibung eines kombinierten Atxn2/TDP43-Mausmodells und schließlich die ausführliche Charakterisierung eines vollkommen neuen und äußerst wertvollen SCA2-Mausmodells.
Amphibians have existed on the planet for over 300 million years and are today one of the most diverse vertebrate classes in the world with over 7000 known species and still many more to be discovered. However, several studies assume that approximately one third of the world´s known living amphibians are directly threatened with extinction, making it the most endangered vertebrate class. In relation to the relatively small land mass that is occupied by the state of Panama, it supports one of the most diverse amphibian faunas. However, in many cases the ecological role of single species in a wider context and their habitat preferences are still poorly understood and subject to ongoing research. Modern taxonomic approaches in other tropical regions have shown that former assumptions of amphibian diversity were distinct underestimations of the actual species diversity; a situation that is probably also true for Panama. Concurrently, the collection of amphibian diversity data and the description of new species is a race against time. The amphibian fauna of the world and that of Panama in particular, has suffered from an unprecedented loss of diversity over the last 30 years. The reasons are manifold and include destruction, alteration, and fragmentation of their natural habitats as the main causes, but also the deadly amphibian disease chytridiomycosis caused by the fungal pathogen Batrachochytrium dendrobatidis (Bd). In Panama and Costa Rica, this Emerging Infectious Disease (EID) spread in a wave-like manner from west to east causing mass die-offs and reduced amphibian diversity even in well-preserved habitats. The disease has primarily affected stream-associated highland species. The last large-scale evaluation of the conservation status of Panama´s amphibians through the IUCN Red List of Threatened Species in 2004 concluded that approximately 30% of the known species are acutely threatened with extinction. Furthermore, around 17% of the amphibian species that have been known back then lacked adequate data to be assessed. In view of Panama´s already overwhelming amphibian diversity, as well as the variety of habitats and the large number of sites that have not been examined with regard to amphibians before, I started this study with the conviction that the inventory of Panama´s amphibian diversity is far from being completed. Furthermore, when I started this study, it was uncertain if there would be any surviving amphibian species in areas where chytridiomycosis had emerged. The loss of whole amphibian communities in upland western Panama following Bd arrival led to a shift of amphibian research to lowland sites in central and eastern Panama aiming primarily on pathogen arrival and the documentation of epizootic outbreak and subsequent population decline. The situation of amphibian communities in areas post-decline was therefore largely unknown. Accordingly, the main goals of my study were to add to the taxonomic inventory of amphibians in Panama and to assess the situation of amphibian populations in habitats where chytrid-driven declines have been observed. To address these tasks I conducted fieldwork in western Panama with a focus on mountainous elevations between 1000 and 3475 m asl. Additionally, I visited different lowland sites between sea level and 1000 m asl to collect comparative material. In the period between 2008 and 2013, I conducted five collection trips to Panama that add up to a total of approximately 13 months in the field. I have sampled nine regions in western Panama and collected 767 specimens together with student collaborators, 531 of which were collected under my personal field number. Additional data obtained from those specimens include 68 male anuran call recordings, 102 standardized color descriptions of specimens in life, and 259 tissue samples that to date yielded 185 16S mtDNA sequences. This comprises the most comprehensive data set for amphibians of Panama and the first large-scale DNA barcoding approach for western Panama to date. After a preliminary DNA barcoding and subsequent comparative examination of morphological und bioacoustic data of all specimens collected, the number of taxonomic problems that needed to be addressed was higher than I previously anticipated. For most genetic lineages deeper taxonomic analyses were required to reach conclusive results. A selection had to be made with which lineages to proceed in the analyses, in view of the substantial financial and time expenditure that would be needed for a complete taxonomic revision. Therefore, I chose to run deeper analyses on one genus from each of the three amphibian orders in Panama. The genera selection depended largely on the availability of sufficient material and the scientific relevance of the respective genus.
I selected the genus Diasporus from the order Anura. These small frogs are omnipresent in many habitats and thus relatively easy to find. In addition, the genus is underrepresented in taxonomic studies. This is the first taxonomic study on the genus Diasporus to include a molecular phylogeny and the first comparison of advertisement calls between several populations from western Panama. In total, I collected 67 Diasporus specimens throughout western Panama and compared them morphologically with 49 additional specimens from Central America in collections, including the primary types of D. diasporus and D. hylaeformis. Additional comparative data were taken from literature. The DNA barcoding analysis of a fragment of the 16S rRNA gene included 43 own sequences that were complemented with 15 relevant GenBank sequences. In addition, I compared the advertisement calls of 26 male individuals among each other and with call descriptions from the literature. The DNA barcoding approach revealed several unnamed genetic lineages, but in some cases also resulted in the lumping of morphologically and bioacoustically distinct specimens. Generally, the morphological examination of the collected material revealed almost no specific characters that could be used to distinguish between genetic lineages. However, it was possible to identify species using a combination of several morphological characteristics. Which ones are relevant in the individual case depends on the respective species. My extensive collection of call recordings made it possible to test for the first time the intraspecific call variation of D. hylaeformis in dependency of various parameters. This analysis showed that the dominant frequency depends significantly on the body size of the calling male; the smaller the calling male, the higher the frequency of the call. A similar relationship was observed between the call rate and temperature: the lower the temperature during calling, the lower the call rate. I suppose that these general patterns, which have already been observed in other anuran genera, are also true in other Diasporus species that could not be tested in this study. Taking into account the intraspecific variation of Diasporus advertisement calls, I consider comparative call analyses to be the best way to distinguish between species. This is especially true in syntopic species. Integration of the three lines of evidence (i.e., morphology, DNA barcoding, and bioacoustics) led to the identification of four new species, two of which (i.e., D. citrinobapheus and D. igneus) colleagues and I have already formally described.
I conducted an integrative taxonomic analysis of the western Panamanian representatives of the genus Bolitoglossa from the order Caudata, the larger of the two Panamanian salamander genera. Bolitoglossa is very species-rich with a centre of diversification in the high mountains of Costa Rica and western Panama. I collected 53 Bolitoglossa specimens and compared them to twelve specimens in collection, including the holotype and one paratype of B. gomezi. The dataset was complemented with information from the literature. Among the sampled specimens were two species considered to be endangered that have not been collected or observed for several decades; B. magnifica has not been seen for 34 years and B. anthracina has not been seen for 22 years. Further, I collected salamanders at several new locations. To date, my 16S mtDNA barcoding analysis represents the densest taxon sampling for Panamanian Bolitoglossa composed of 21 own sequences that were combined in the final alignment with 47 GenBank sequences. Even though the molecular phylogeny is based only on a single marker, the received trees largely coincide with previous studies and the nodes received high statistical support. In these trees, I retrieve all previously defined subgenera and species groups. On the basis of this molecular phylogeny, I placed B. anthracina, here sequenced for the first time, in the B. subpalmata species group. Due to the fact that B. anthracina is a large and dark colored species it had previously been placed by implication in the B. schizodactyla species group along with other large black salamanders of the B. nigrescens species complex. Moreover, I found deep divergent genetic lineages among geographically separated populations of B. minutula. However, until now there were no additional morphological characteristics detectable to distinguish between these lineages. Additionally, my colleagues and I described a new deep divergent lineage in the B. robinsoni species group as B. jugivagans, a species new to science. In contrast, I found only minor genetic differences between specimens of B. sombra and B. nigrescens. After combining morphometric data and tooth counts from literature of both species with additional data from specimens of B. sombra that I collected near the type locality, the distinguishing features blurred. In particular, including much larger specimens of B. sombra, not yet known at the time of its description, showed that the tooth count difference is dependent on the size and age of the specimen examined. Larger specimens have more maxillary and vomerine teeth. Based on this evidence I regard B. sombra as a junior synonym of B. nigrescens. Further, I revised the Panamanian distribution of the two relatively common lowland salamanders, B. colonnea and B. lignicolor. Besides filling the gaps in the fragmentary known distributions of these species, I assessed the molecular and morphological variation of both species among populations in Panama. While there was little variation in B. lignicolor, I found divergent genetic lineages among geographically distinct populations of B. colonnea that require further taxonomic examination.
Caecilians (order Gymnophiona) are among the least investigated terrestrial vertebrates. After I received a first specimen of the predominantly South American genus Oscaecilia (family Caeciliidae) in western Panama, I started to work more extensively on the taxonomy of Caeciliidae in Central America. The specimens from western Panama were not readily assignable to a single described species, but shared characters with O. elongata and O. osae. While O. osae was only known from the holotype, the type material of O. elongata was destroyed during World War II. On the basis of the original description, the unique feature in O. elongata within Oscaecilia is the absence of subdermal scales in the posterior part of the body. In a referred specimen of O. elongata mentioned in the original description from eastern Panama, this characteristic cannot be examined as it consists of head and neck only. Therefore, I used non-destructive high-resolution, synchrotron-based X-ray micro CT imaging (HRμCT) to examine cranial characters in the specimens in question and took normal radiographs to count vertebrae and to make subdermal scales visible. I found that the fragmented specimen from eastern Panama likely belongs to the well-sampled species O. ochrocephala and has not much in common with O. osae or the specimens from western Panama. Contrarily, O. osae and the specimens from western Panama share many morphological characters, but also show some differences. Genetic barcoding revealed that both species are close relatives, but the genetic distance could not be finally resolved, because 16S sequences obtained from blood samples of living O. osae were of poor quality. Thus, I compare the Oscaecilia from western Panama to O. osae in this study, but postpone a taxonomic decision until further material becomes available. Further, I designate O. elongata a nomen dubium, because the type material is lost, the type locality is not defined in more detail than “Panama”, and the original description does not allow for a definite assignment. Since previous molecular studies only considered O. ochrocephala, the monophyly of Oscaecilia was never tested before. So far, the genus Oscaecilia is based largely on a single cranial character, the eyes covered with bone. Here, I combined two 16S mtDNA sequences of O. osae from Costa Rica and two sequences from O. sp. from western Panama with two sequences of O. ochrocephala and ten sequences of four species of the genus Caecilia, the sister genus of Oscaecilia. The resulted phylogeny contains two well-supported clades, one clade containing two species of Caecilia, one from Panama and one from western Ecuador and all species of Oscaecilia tested. The other clade consists of two species of Caecilia from the Amazon basin. I therefore assume that the split in both clades is due to the rise of the Andes, what led to today’s cis-trans-Andean distribution of the two clades. For now, to restore monophyly, I suggest to place Oscaecilia within the synonymy of Caecilia until more taxa have been tested. When assessing the conservation status of the amphibian species in mountainous western Panama, I first compiled a list of known species that I potentially could have found during my fieldwork. Using the IUCN categories, I analyzed how many of the endangered species I actually found and how these are distributed over families and species groups. Surprisingly, my rediscoveries of lost species were not equally distributed among the four families that comprise most endangered amphibian species (i.e., Bufonidae, Craugastoridae, Hylidae, and Plethodontidae). While I discovered ten of eleven endangered hylids and six of nine endangered plethodontids, I found only one of four endangered bufonids and none of the nine endangered craugastorids. I assume that the secretive living plethodontids, for which no Bd related declines have been documented, were just overlooked in the past decades. In contrast, I propose that hylids, in which Bd related population decline is well documented, developed distinct evolutionary solutions permitting coexistence with the pathogen. The situation is obviously different in bufonids and craugastorids, where I found no signs of population recoveries at present. So far, the only surviving populations of species from these families exist in climatic or physiographic niches that have probably shielded them from Bd. My data confirm the current view that the risk for naïve amphibian populations to decline during Bd epizootics is predicted by ecological traits (e.g., aquatic index, vertical distribution) and not dependent on taxonomic affiliation. However, I propose that only certain amphibian families (e.g., hylids and centrolenids) have the ability to acquire immunity solutions to coexist with the pathogen during enzootic stages. This is a very new perspective on the worst infectious disease in amphibians worldwide, allowing for new research approaches to understand the host-pathogen dynamics. Moreover, I examined where the share of surviving endangered amphibian species is particularly high in mountainous western Panama. As was to be expected, most of the endangered species are found within the boundaries of protected areas. One exception is the unprotected Cerro Colorado region in the Comarca Ngöbe-Buglé that provides habitat for a wide variety of endangered and undiscovered amphibian species. Nonetheless, planned open pit mining would destroy the forests in a large part of the area. This demonstrates once again that human activities are the biggest threat to amphibians in Panama and elsewhere.