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Die Grewioideae sind eine Unterfamilie der Malvaceae sensu Bayer et al. (1999). Sie umfassen mit 25 Gattungen und ca. 700 Arten einen Großteil der früheren Tiliaceae. Diese waren vor allem aufgrund der durchweg dithecischen Antheren und der oft zahlreichen, freien Stamina zu einer Familie zusammengefasst worden, auch wenn die enge Verwandtschaft mit den Sterculiaceae, Bombacaceae und Malvaceae bekannt war und die Abgrenzung dieser Familien untereinander oft als künstlich angesehen wurde. ... Insgesamt 45 Arten aus allen 25 Gattungen der Malvaceae-Grewioideae (sensu Bayer & Kubitzki 2003) wurden hinsichtlich ihrer Morphologie im Blüten-, Frucht- und vegetativen Bereich untersucht. Der Schwerpunkt lag dabei auf einer vergleichenden Bearbeitung der Blütenstruktur, für die neben morphologischen auch ontogenetische und anatomische Untersuchungen durchgeführt wurden. Die Ergebnisse waren Grundlage für eine Datenmatrix mit 55 Merkmalen, die ebenso wie DNA-Sequenzdaten (ndhF) für phylogenetische Analysen verwendet wurden. Die Analysen beider Datensätze ergeben eine Zweiteilung der Grewioideae. Auf der Basis der Ergebnisse wird vorgeschlagen, die Grewioideae in die zwei Triben Apeibeae und Grewieae zu unterteilen. Diese Gliederung widerspricht früheren Klassifikationen, ist aber durch strukturelle Merkmale gut gestützt. Die Apeibeae zeichnen sich durch hornförmige Verlängerungen der Sepalen-Spitze und stachelige Emergenzen auf der Fruchtoberfläche aus, Reduktionsformen sind durch Übergänge nachweisbar (Ausnahme: Glyphaea). Leitbündelstränge innerhalb der Fruchtwand verlaufen einzeln. Bestäubungsbiologisch relevante Nektarien, soweit vorhanden, befinden sich vor den Petalen auf einem Androgynophor. Das Androeceum entwickelt sich zentrifugal in einer unterschiedlichen Zahl einheitlicher Kreise. Den Grewieae fehlen Fortsätze der Sepalen-Spitzen sowie stachelige Emergenzen der Früchte. Sie sind durch Nektarien auf den Petalen charakterisiert (Ausnahme: Mollia). Ihre Fruchtwand weist einen geschlossenen Leitbündelmantel auf. Steinkerne oder dorsal geflügelte Fruchtfächer kommen vor. Das Androeceum entwickelt sich oft ungleichmäßig mit einer Förderung des antesepalen Sektors, bisweilen ausgehend von Komplexprimordien. Innerhalb der Triben lassen sich teils neue, teils früher schon bekannte Gruppen erkennen; andere sind anhand der vorliegenden Daten nicht aufzulösen. Dies gilt insbesondere für die Verwandtschaft von Grewia, bei der die Gattungsgrenzen einer kritischen Revision bedürfen. Die Kartierung der morphologischen Merkmale auf den Konsensusbaum der DNA-Sequenzdaten ergab, dass insbesondere der Androgynophor innerhalb der Grewioideae mehrfach parallel entstanden ist und im Gegensatz zu früheren Klassifikationen nicht als Tribus-Merkmal herangezogen werden kann. Auf der Suche nach einem gemeinsamen Bauplan, der den stark unterschiedlichen Blütenstrukturen der Schwestergruppen Grewioideae und Byttnerioideae zugrunde liegen könnte, wurde insbesondere das Androeceum vergleichend untersucht. Bei beiden Unterfamilien findet man polystemone Androeceen, die bei den Byttnerioideae in staminodiale antesepale und fertile antepetale Sektoren differenziert sind. Dies wird in der Literatur oft als obdiplostemones Arrangement zweier Kreise interpretiert, von denen der fertile antepetale Teil dédoubliert. Bei den Grewioideae findet man keine derartige Differenzierung; sie sind in ihrer androecealen Struktur außerordentlich variabel. Die Befunde der Morphologie, Ontogenie und Anatomie widersprechen sich dabei jeweils dergestalt, dass eine theoretische Gliederung des polystemonen Androeceums in zwei Kreise kaum zu rechtfertigen ist. In diesem Zusammenhang wird die in der Literatur verbreitete Vorstellung einer sekundären Polyandrie kritisch beleuchtet. Für die untersuchte Gruppe wird ein Zusammenhang zwischen Bestäubungsbiologie und Blütenstruktur als nahe liegender angesehen, der zu unterschiedlichen Gruppenbildungen innerhalb polystemoner Androeceen führen kann. Während Petalen und Stamina bei den oft fliegenblütigen Byttnerioideae eine spezielle Funktionseinheit bilden, findet man bei den größtenteils bienenblütigen Grewioideae in Zusammenhang mit den Petalen oft Nektar. Die fertilen Stamina können den gesamten antesepalen und antepetalen Raum einnehmen. So stand an der Basis der Grewioideae möglicherweise der Wechsel der Bestäubergruppe und die Auflösung eines blütenbiologisch fixierten Musters, ein Vorgang, wie er innerhalb der Malvaceae mehrfach auf unterschiedliche Weise erfolgt sein könnte. Auch andere Gruppen weisen Blütenstrukturen mit vorwiegend freien Stamina und verborgenem Nektar in Zusammenhang mit Bienenbestäubung auf. Es mag diese blütenbiologisch bedingte Ähnlichkeit gewesen sein, die zur Vereinigung nicht näher verwandter Gruppen zur früheren Familie Tiliaceae geführt hat.
Biodiversity is unevenly distributed on Earth. Highly diverse biotas are particularly expected in mountain systems, because altitudinal zonation provides a number of habitat alternatives, which could lead to lower extinction rates during climatic changes. Nevertheless, the impact of environmental changes on plant diversification (especially for sub-alpine taxa) in the course of mountain orogenesis remains poorly understood. This is also true for the highest and largest plateau on Earth, the Qinghai-Tibetan Plateau (QTP) and its surrounding areas.In this doctoral thesis, I investigated the impact of environmental changes on plant diversification and the floristic exchange between the QTP region and biodiversity hotspots of Southeast Asia as well as other parts of the world by using the sub-alpine genera Agapetes and Vaccinium (Vaccinieae, Ericaceae) as well as Tripterospermum (Gentianinae, Gentianaceae) as model systems. Furthermore, I examined the role of niche evolution and conservatism in a changing environment over time, and detected possible beneficial morphological traits of plants in the surroundings of the QTP by investigating subtropical Gentianinae (Crawfurdia, Kuepferia, Metagentiana, Sinogentiana, and Tripterospermum; Gentianaceae).
Lizards of Paraguay: an integrative approach to solve taxonomic problems in central South America
(2018)
Paraguay is located in the center of South America with drier and warmer climatic conditions in the western part of the country, and more temperate and humid in the eastern region. Biogeographically, Paraguay is a key spot in South America, where several ecoregions converge. In my study, I sampled most of the ecoregions of Paraguay. The main objective of my work is to solve taxonomic problems, identified through genetic barcoding analyses, in the central region of South America. To achieve this objective, I used selected taxa of the Paraguayan Squamata as models taking into consideration the crucial geographic position of the country, plus the scarce available genetic data of Paraguayan reptiles.
The collecting activities were performed in the framework of a barcoding inventory project of the Paraguayan herpetofauna and carried out mostly in rural areas searching for animals in different types of habitats using active search as the sampling technique.
For genetics, the extraction of DNA was performed with DNeasy® Blood & Tissue Kit of Qiagen® for sets of few samples, and the fiber glass plate protocol for sets of 96 samples. I assessed the quality of sequences after amplification in agarose gel electrophoresis. The first marker sequenced was 16S mtDNA, used for barcoding analysis. A DNA barcode is a genetic identifier for a species. Once a taxonomic problem was detected, I generate more gene sequences to target the issue.
All the analyses to test phylogenetic hypotheses (based on single genes or concatenated datasets) were performed under Maximum Likelihood and Bayesian approaches. To root the phylogenetic trees, I chose the available taxon (or taxa) most closely related to the respective studied group as outgroups. For the general tree of Paraguayan Squamata, based on barcodes of 16S, I chose Sphenodon punctatus.
I generated a total of 142 sequences of 64 species of Squamata from Paraguay (Appendix I). The final alignment of 615 bp comprised 249 samples. The best substitution model for the Barcoding dataset based on the gene 16S was GTR+G, according to the BIC.
To complement molecular evidence generated with the ML grouping of 16S barcodes, I took a morphological approach based on voucher specimens collected during fieldwork (usually the same specimens that I used for genetic analysis), supplemented by the revision of museum collections.
Summarizing my results, samples of Colobosaura exhibit large genetic distances, and accordingly I revalidated Colobosaura kraepelini (Appendix II). Tropidurus of the spinulosus group show two clades and among them there is little genetic and morphological variation, I synonymized T. tarara and T. teyumirim with T. lagunablanca, and T. guarani with T. spinulosus (Appendix III). I detected the presence of candidate species of Homonota, and I restricted the name H. horrida for Argentina, and described two new species of Homonota (Appendices IV and V), and a new species of Phyllopezus also in the Family Phyllodactylidae (Appendix VI).
In this work I present the most comprehensive analysis of genetic samples of Squamata from Paraguay. The results obtained here will be useful to help to clarify further taxonomic issues regarding the squamate fauna from the central region of South America. Moreover, the data generated for this study will have a positive impact in a larger geographic context, beyond Paraguayan borders.
Regarding the conservation of the Paraguayan reptiles, and considering the taxonomic changes accomplished here, it is important to note that many species lack legal protection. In Paraguay, the major problem for conservation is habitat loss due to extensive crop farming. Thus, currently, the protected areas are the best strategy for conservation of biodiversity in the country. However, many such areas face legal problems (e.g., lack of official measurements, management plans, forest guards, infrastructure, etc.) so that the maintenance of their biodiversity over time is not guaranteed.
In conclusion, in this study I present contributions on the taxonomy of mostly lizards from Paraguay. Due to lack of samples, I was not able to deal with a deep taxonomic revision of the country's snakes. Based on my results, I can argue that analyses of Xenodontini and Pseudoboini are currently a pressing research issue. This barcoding project may continue since some colleagues in Paraguay are interested in collaboration. Given that the sequenced specimens are yet a small portion of the actual diversity of Paraguay, it will be of utmost importance to continue and expand these studies that will further improve our taxonomic knowledge. Furthermore, it is desirable to have Paraguayan scientists not only involved, but to see them taking the lead of high quality taxonomic research.
Die Interaktion zwischen der Kannenpflanze Nepenthes bicalcarata und der mit ihr assoziierten Camponotus schmitzi stand im Zentrum der Arbeit. Dabei wurden vier Themenbereiche zur genaueren Bearbeitung ausgewählt. Drei davon (Kapitel 3, 5 und 6) sind in vier Artikeln bereits in Fachzeitschriften publiziert worden (siehe Kapitel 14.1.2). Die Untersuchungen aus Kapitel 4 sind noch unveröffentlicht. Entsprechend den sich entwickenden Ergebnissen wurden zudem auch vergleichende Untersuchungen zu anderen mehr oder minder im gleichen Habitat vorkommenden Nepenthes Arten, N. gracilis, N. ampullaria, N. mirabilis var echinostoma, N. rafflesiana und N. albomarginata durchgeführt.
Lichens are present in most land ecosystems, frequently occupying habitats where few other organisms are able to survive. Their contribution to the ecosystems in terms of biomass and ground cover increases with latitude and altitude, being, together with bryophytes, the most conspicuous component of alpine and polar landscapes. Whereas some polar lichens have reduced distributions and are restricted to high latitudes, most of them have very wide distributional ranges, which oven extend over several climatic regions. Many of them are common to Polar Regions of both hemispheres, a distributional pattern that has been denominated as bipolar, antitropical or amphitropical. Bipolar distributions are not exclusive to lichens, but common to many groups of organisms. The bipolar element in lichens is exceptional as it includes a large number of species, while in most other land organisms it includes genera or families but very seldom species.
In this dissertation I use the bipolar lichen Cetraria aculeata to give a first insight into the phylogeography of this biogeographic element in lichens. I discuss how and when the disjunct distribution of C. aculeata came to be, and try to partial out the roles that historical and ecological processes played in shaping its distribution.
Sampling was designed to cover a wide geographic extension. The main e"ort was made to collect in boreal, temperate and tropical mountain ranges in North and South America, as well to include Mediterranean populations in which specimens with deviant morphologies are observed.
I found that Cetraria aculeata forms a genetically congruent taxon. Although whether it should include C. muricata remains unsolved, I excluded all specimens identified as the latter from our analyses. Thee populations of both algal and fungal symbionts have a strong geographic structure. The study of the lichen fungus suggested that the species originated in the Eurasian continent and later expanded to acquire its current distribution during the Pleistocene. The results showed that all American populations originated from an ancestral population, more similar to the extant Arctic populations than to the Mediterranean ones.
The comparison between the structure of fungal and algal populations showed a high degree of coherence between them. However, the similarity in photobiont use between Arctic and Antarctic populations suggests that photobiont use responds not only to a history of codispersal in vegetative propagula, but it is also a result of a selective process related to climate. Since this climatic pattern of similarity is also found in the community of Alphaproteobacteria associated with C. aculeata, we concluded that lichens might be able to accommodate or to respond to different environmental conditions by selectively associating with different symbiotic partners.
Lastly, we found the Mediterranean populations of C. aculeata to be genetically differentiated in algal and fungal symbionts from the rest of the populations. While we found no grounds to believe that the overgrown morphs encountered in the region are due to the association with different algal lineages, I believe that a switch in photobiont use might be responsible for the pattern of genetic isolation encountered. Furthermore, I suggest that the Mediterranean and bipolar C. aculeata could be two different species, since both are ecologically, genetically and at least in part morphologically divergent.
Savannas are the most important timber and non-timber forest products (NTFPs) providing ecosystems in West Africa. They have been shaped by traditional human land-use (i.e. agriculture, grazing, and harvesting) for thousands of years. In the last decades, land-use has drastically changed due to the rapid population growth and the growing production of cash-crop in West Africa and this process is still continuing. The percentage of land intensively used for agriculture has increased, while the length of fallow periods has decreased. Such changes have enormous ecological, economic, and social consequences. In the context of land-use changes, there is an urgent need to better understand and evaluate the impact of land-use on savannas. Such an understanding provides insights on appropriate management activities that ensure the maintenance of savannas and guarantee the availability of savanna products for subsistence and commercial use of rural West African people.
The major objective of the present thesis was to study the impact of land-use on savanna vegetation and diversity as well as on populations of two important NTFP-providing tree species in a semi-arid area in West Africa. The study area was located in the south-eastern part of Burkina Faso and comprised the protected W National Park and its adjacent communal area.
In the first study (chapter 2), I investigated in cooperation with a colleague from Burkina Faso (Blandine Nacoulma) the impact of land-use on the savanna vegetation. We analyzed which environmental factors determine the occurrence of the vegetation types and investigated the effect of land-use on vegetation structure and the occurrence of life forms and highly valued tree species. Furthermore, we tested whether land-use has an impact on plant diversity pattern and if this impact differed between the vegetation types and layers (woody and herb layer). Vegetation relevés were performed and the vegetation and plant diversity of the protected W National Park were compared with those of its surrounding communal area. Our results reveal five vegetation types occurring in both areas. Elevation and physical soil characteristics and thus soil water availability for plants played the most important role for the occurrence of the vegetation types. The influence of land-use on plant diversity differed between the five vegetation types and the two layers. The impact was highest on the vegetation types with the most favorable soil conditions for cultivation and lowest on rocky habitats with poor soils. While the diversity of the woody layer was increased under human land-use, the diversity of the herb layer was diminished. Overall, as land-use effects were not only negative, our findings suggest that land-use does not automatically lead to a loss of plant species and to a degradation of savanna habitats. We conclude that both protected and communal areas are of great importance for the conservation of savanna vegetation and diversity. Our study highlights furthermore the importance of different management strategies for each vegetation type.
In the following two studies (chapter 3 and 4), the impact of land-use - and in particular of harvesting - on populations of Adansonia digitata L., the baobab tree, and Anogeissus leiocarpa (DC.) Guill. & Perr. was examined. These two tree species were chosen as they provide several NTFPs for the local population and as they show different levels of human protection and opposed life histories. Thus, they may react differently to land-use. Stands of the protected W National Park were compared with those of its surrounding communal area (in fallows, croplands, and villages). I applied dendrometric methods to study the population structures and combined it with rates and patterns of NTFP-harvesting (debarking and chopping/pruning). Furthermore, the impact of land-use and harvesting on the fruit production of A. digitata and on the sprouting ability of A. leiocarpa were studied. The inverse J-shaped size class distribution curve indicates that the stands of A. digitata were in a healthy state in the park, while the low number of smaller size classes in fallows, croplands, and villages may give evidence of an ageing population. However, a high number of seedlings were recorded in villages. The stands of A. leiocarpa were also in healthy states in the park and likewise in fallows. In contrast, the absence of saplings gives evidence of a declining population in croplands. Both species were strongly harvested by local people and harvesting was tree size-specific. Pruning in interaction with tree-size had a significant impact on fruit production of A. digitata. While smaller trees were more vulnerable to pruning, bigger trees benefited from slight-pruning. A. leiocarpa had a great ability to respond to chopping by sprouting. The sprouting ability increased even with higher chopping intensity. Results suggest that despite the intense harvesting and the land-use impact, populations of both species are still well preserved. While A. digitata can withstand the harvesting and land-use pressure by its longevity, extremely low adult mortality rates, and particularly due to positive human influences, A. leiocarpa is able to withstand the use pressure by its fast growing, high recruitment, and high sprouting ability. I conclude that a none protected tree species (A. leiocarpa) might not necessarily be at higher risk to the harvesting and land-use impact than a protected tree species (A. digitata) as the adverse impact of harvesting and land-use can be compensated by its specific life history.
Important additional information to such ecological findings can be provided by local people. Learning from traditional knowledge and management systems of local people will help to produce culturally and ecologically reasonable conservation and management strategies. Thus, I investigated local uses and management strategies of A. digitata and A. leiocarpa in the last two studies (chapter 5 and 6). Quantitative ethnobotanical surveys among the Gulimanceba people were conducted in the communal area in order to document uses of the different plant parts, harvesting modes, perceptions about the population status, and conservation status of both species. Hereby, differences in knowledge between gender, generations, and people from different villages were tested. Interviews reveal that both species are harvested for multipurpose and emphasize the high importance of both species for local people. Especially the leaves and fruits of A. digitata add valuable minerals and vitamins to the otherwise micronutrient-“poor” staple crops of the Gulimanceba people. In comparison with other studies in West Africa, it has turned out that people in this area could benefit even more from A. leiocarpa, e.g. for dyeing of clothes, for treatment of malaria and skin problems. Local knowledge did not differ between genders and generations, while it slightly differed between people from different villages. The lack of age differences suggests that the traditional knowledge about these two species is passed on from one generation to another. Differences between people from different villages might be explained by influences from the neighboring countries Niger and Benin. Current local harvesting modes and management strategies of both species resulted in sustainable use. However, ongoing land-use intensifications require adapted harvesting and management techniques to guarantee the persistence of these economically important species. These results provide, in combination with the ecological findings (chapter 3 and 4), appropriate management recommendations for A. digitata and A. leiocarpa that are reliable under currently practiced management strategies.
Die Bromeliaceae umfassen mehr als 3.100 fast ausschließlich neotropische Arten. Bekannt für ihre außergewöhnliche ökologische Vielseitigkeit haben sich Bromelien erfolgreich in terrestrischen und epiphytischen Lebensräumen ausgebreitet.
Eine umfassende Untersuchung des Gefährdungsgrades aller Bromelienarten Panamas und Costa Ricas stand bisher noch aus und ist insbesondere aufgrund des großen Reichtums an Lebensräumen, der beide Länder auszeichnet, und den vielfältigen Veränderungen geboten.
Im Rahmen der vorliegenden Arbeit wurden während der insgesamt etwa achtmonatigen Feldarbeit 54 Exkursionen in Westpanama durchgeführt und Belege von 61% (126 Arten) der für Panama bekannten Arten gesammelt.
Auf der Basis der Feldarbeit und der in verschiedenen Herbarien durchgeführten Studien (Überprüfung und Digitalisierung von > 8.000 Aufsammlungen) wurden Diversität, Endemismus, Areale und räumliche Muster der Artenvielfalt der Bromeliaceae in Panama und Costa Rica erfasst, dokumentiert und analysiert.
Nur drei der derzeit bekannten acht Unterfamilien der Bromeliaceae finden sich in Panama und vier in Costa Rica. Zwanzig Arten werden hier erstmals für Panama gemeldet. Sechs bisher für Panama gemeldete Bromelienarten wurden als irrtümlich gemeldet identifiziert. Die Flora der Bromeliaceae umfasst nun 16 Gattungen und 206 Arten in Panama sowie 18 Gattungen und 199 Arten in Costa Rica.
33 Arten sind endemisch in Panama, 32 Arten in Costa Rica und 36 Arten sind auf das Gebiet beider Länder beschränkt. Die Gattung Werauhia hat ihr Diversitätszentrum in Panama (47 von insgesamt 87 Arten) und Costa Rica (59/87 Arten) und ist gleichzeitig die artenreichste Gattung in beiden Ländern.
In Panama treten 113 Arten (54,9 %) zwischen 1.000 und 2.000 Höhenmetern auf. Die Art mit der niedrigsten Höhengrenze ist Pitcairnia halophila, die am höchsten angetroffene Art ist Werauhia ororiensis.
Für jede der für Panama und Costa Rica (259 Arten) gemeldeten Bromelienarten wurde eine Verbreitungskarte erstellt; für die in beiden Ländern auftretenden 191 Arten wurde darüber hinaus die potenzielle Verbreitung modelliert.
In Panama ist der prämontane Regenwald mit 138 Arten (einschließlich 25 der insgesamt 33 endemischen Arten) die Holdridge-Vegetationszone mit der höchsten Anzahl an Bromelien. In Costa Rica hat der untere Bergregenwald einen besonders hohen Anteil endemischer Bromelien (13 von insgesamt 32 Arten).
In Panama und Costa Rica beherbergen mittlere Höhenlagen den größten Artenreichtum der Bromeliaceae mit Maximalwerten von etwa 125 Arten im Osten Costa Ricas und in Westpanama. Einige Regionen Panamas verfügen nicht über ausgewiesene Schutzgebiete, weisen jedoch einen hohen Artenreichtum an Bromelien auf (z.B. Teile Westpanamas, El Valle de Anton und benachbarte Gebiete sowie die Serranía de Cañazas).
In der hier vorgestellten Klassifizierung des Gefährdungsgrades gemäß den Richtlinien der IUCN werden für Panama 32 Arten als vom Aussterben bedroht (CR), 36 Arten als Stark Gefährdet (EN) und 36 Arten als Gefährdet (VU) eingestuft. In Costa Rica wird Aechmea aquilega als Ausgestorben (EX) eingeschätzt. Vier Arten werden als vom Aussterben bedroht (CR), 30 Arten als Stark Gefährdet (EN) und 39 Arten als Gefährdet (VU) klassifiziert.
In Panama wurden 184 Arten (89% der insgesamt 206 Arten) in Schutzgebieten nachgewiesen. 122 Arten (59%) wurden sowohl innerhalb als auch außerhalb und 19 Arten (9%) nur außerhalb von Schutzgebieten nachgewiesen. In Costa Rica kommen 182 Bromelienarten (91% der insgesamt 199 Arten) in Schutzgebieten vor, 168 Arten (84%) wurden sowohl innerhalb als auch außerhalb und 14 Arten (7%) nur außerhalb von Schutzgebieten nachgewiesen.
Die Schätzungen zeigen, dass die zu erwartende Gesamtzahl der Bromelienarten in Panama zwischen 224 und 250 Arten liegt, und die zu erwartende Gesamtzahl der Bromelienarten in Costa Rica liegt zwischen 207 und 221 Arten. Den Ergebnissen der Modellierung zufolge wird für eine Anzahl bisher nur für Costa Rica gemeldeter Arten das Auftreten in Panama mit erheblicher Wahrscheinlichkeit prognostiziert (z.B. Guzmania blassi, Werauhia ampla), wie auch umgekehrt das Vorkommen bisher nur für Panama bekannter Arten in Costa Rica (z.B. Aechmea strobilina, Pitcairnia kressii).
Der Erhalt der bestehenden Schutzgebiete sollte ein vorangiges Ziel sein. Darüber hinaus ist es wünschenswert, einige dieser Gebiete auszudehnen und neue Schutzgebiete auszuweisen, um biologisch hochdiverse Gebiete mit einem hohen Anteil endemischer Arten zu schützen.
This manuscript-based thesis is divided into four chapters. Chapter one is an introduction to lichens and the Antarctic. It introduces the goal of the thesis and the problems related with lichen systematics and the lack of knowledge about Antarctic lichens. The Antarctic is one of the last wildernesses, isolated from the other continents by the Antarctic Circumpolar Current, the Subantarctic Front, the Antarctic Polar Front, and the Drake Passage. Terrestrial life in Antarctica is restricted to widely separated and small ice-free areas that cover only 0.3% of the continent. Colonization of the Antarctic is a challenge for many taxa and is related to their ability for long-range dispersal and their adaptation to the harsh climate. Antarctic terrestrial ecosystems are significantly threatened by climate change, invasive species, and their interactions. Glacial retreat caused by higher than average temperatures exposes new habitats that can be easily colonized from local biota, but non-native species can also be favored by the new climatic conditions. In addition, propagule movement mediated by humans can introduce new species or change the population structure of many taxa. The terrestrial biota is comprised almost exclusively by “lower organisms” (invertebrates, bryophytes, algae, lichenized fungi, and microorganisms). Lichens are the dominant component, and the most important primary producers. Lichens are symbiotic associations consisting of a fungus (mycobiont) and one or more photosynthetic (photobiont) partners. They can disperse sexually or vegetatively. There are several problems related to the symbiotic nature of lichens that do not facilitate easy identification; although molecular data offers additional evidence, species delimitation in lichens is still not straightforward. The true number of species is underestimated due to the presence of cryptic species and species pairs. Recommended universal fungal barcode sequences (e. g. ITS) sometimes fail to delimit species pairs. Thus, it is necessary to identify fast-evolving markers that allow for the delimitation of closely related species before proceeding with the analysis of lichen populations. The goal of this thesis is to elucidate the so far unknown genetic structure among Antarctic lichen populations because of the immediate consequences for conservation strategies. The thesis focuses not only on patterns of differentiation and gene flow, but also investigates the question of human-mediated propagule transfer into Antarctica and among Antarctic sites. This project provides data on the genetic structure of Antarctic lichens that is urgently needed to develop conservation strategies in the face of global warming and increased human activities in the region. Due to the fact that it is not possible to apply all of the unspecific fingerprinting methods to lichens, microsatellites or simple sequence repeats (SSRs) are one of the best tools to investigate the genetic structure of lichen populations. SSRs offer the possibility to discriminate the lichen partners, but species-specific microsatellites have been developed for only a few species. Regarding the Antarctic, only one species has been studied with SSRs.
The second chapter describes new methods and tools to delimit closely related species of lichens and provides fast evolving markers to characterize their genetic structure. The chapter introduces the lichen species analysed in this thesis and the problems related to their correct identification by morphological methods and molecular data. Chapter two explains the sampling methods for lichen populations and the localities from small areas in which the species pairs occur together. Then the methods used to generate and validate fungal specific microsatellites that cross-amplify species pairs are described. This chapter focuses on the species pair Usnea antarctica and U. aurantiacoatra because they are the most common lichens in the Maritime Antarctic. An internal transcribed spacer (ITS) marker do not discriminate between these species, and some authors have suggested to synonymize them. Unpublished results from another Antarctic species pair, Placopsis antarctica and P. contortuplicata, are included to confirm the capability of SSRs to discriminate closely related lichen species. This thesis is the first study to generate SSRs that cross amplify species pairs, using BLAST to compare one genome against the other to obtain markers with the same length in flanking regions. The de novo developed SSRs are able to discriminate the two closely related species, and can detect variability at the population level. In the end of the chapter, ITS sequences, microsatellites, and SNPs are used to delimit the species of Usnea antarctica and U. aurantiacoatra. The chapter exposes the importance of a correct species delimitation and the ability of SSRs and SNPs to delimit the Antarctic Usnea species pair compared with the recommended universal fungal barcode sequence ITS. ...
The existence of all living organisms depends on their multidimensional adjustment to the conditions of the environment in which they live. Organisms must constantly deal with not only abiotic stress factors (such as water availability or extreme temperatures), but also with various biotic interactions (the competition between different organisms, both intraspecific and interspecies). When there is a consensus between an organism and the environment it means that this organism is well adjusted and increases its probability of survival.
Symbiotic organisms possess the ability to establish an intimate interaction with another species (symbiont) that provides benefits for survival. Organisms that are involved in obligate symbiosis may adapt to a new environment by switching to another symbiotic partner that is locally better adapted; or by reshuffling symbiont communities present in the holobiont. This ability potentially gives them the opportunity to flexibly react to changing environmental conditions.
In this thesis I studied the genetic diversity and geographic distribution of symbiont lineages in a lichen symbiosis to better understand environmental adaptation in symbiotic systems. Lichens are symbiotic associations of photobionts (one or several green-algal species or cyanobacteria), filamentous mycobionts (lichen-forming fungi) and co-inhabiting symbiotic microorganisms (lichen-associated bacteria, endolichenic fungi, and basidiomycete yeast). The coccoid green algae of the genus Trebouxia are the most common and the most studied lichen photobionts. However, the lack of formal Trebouxia taxonomy impedes our understanding of this photobiont diversity.
Different species of mycobionts may share the same photobionts and a single species of mycobiont may associate with multiple, genetically different photobionts. Interactions among symbionts are not random and are constrained by evolutionary and environmental processes. The ability to associate with specific symbiotic partner is considered as a lichen strategy to facilitate adaptation to the constantly changing environments.
The objectives of this thesis were to 1. Elucidate the intraspecific diversity of fungal and algal symbionts in the lichen Umbilicaria pustulata, given a range-wide (Europe-wide) sampling; 2. Evaluate species delimitation in trebouxioid photobionts based on molecular data, and 3. Quantify the climatic niches of photobiont lineages within U. pustulata, to establish whether the association with particular photobionts may modify the range and ecological niche of this lichen.
The main findings of this thesis are:
1. The genetic diversity within trebouxoid photobiont of U. pustulata is higher than within the mycobiont. The most variable photobiont loci are nrITS rDNA, psbJ-L, and COX2. RbcL is the least variable photobiont locus. The most variable mycobiont loci are MCM7 and TSR1. This study shows a lack of genetic variability in the mycobiont loci EF1, nrITS rDNA, RPB1, and RPB2.
2. U. pustulata shows a low level of selectivity and is associated with numerous (most likely six) putative algal species. All photobiont haplotypes found in U. pustulata are shared between other lichen-forming fungi species, showing different patterns of species-to-species and species-to-community interactions.
3. The geographic distribution of U. pustulata symbionts associations is strongly connected to changes in the climatic niches. The mycobiont-photobiont interactions change along latitudinal temperature gradients (cold-adapted hotspot) and in Mediterranean climate zones (warm-adapted hotspot). U. pustulata broadens its distribution range by switching between photobionts that posses specific environmental preferences.
Overall, this thesis contributes to the understanding of the symbiont diversity, fungal-algal association patterns and local adaptation linked to symbiont-mediated niche expansion in lichens. While identifying intraspecific diversity of both lichen symbionts is a key predisposition to understand symbiont interactions, population dynamics or co-evolution, my comparative study of the sequence-based molecular markers is relevant to reveal cryptic diversity in other lichen-forming fungi and their photobionts.
The determination of species boundaries in lichen symbionts is essential for the study of selectivity and specificity, co-distribution, and co-evolution. Whereas the phylogenetic relationships of Trebouxiophyceae are poorly understood, the application of a novel multifaceted approach based on phylogenetic relationships, coalescence methods and morphological traits presented in this thesis is a promising tool to address species boundaries within this heterogeneous genus.
This thesis provides evidence for symbiont-mediated niche expansion in lichens and highlights the preferential photobiont association from a niche-modeling perspective. My results shed light on symbiont polymorphism and partner switching as potential mechanisms of environmental adaptation in the lichen symbiosis. The spatial genetic pattern found in U. pustulata symbionts supports the concept of ecological fitting and is consistent with patterns found in other lichen studies. Results presented here relate also to findings in different symbiotic systems, like reef-building corals, where different latitudinal patterns and symbiont switching has been reported as an adaptive response to severe bleaching events. Furthermore, this study is timely in light of global warming, because the identification of interaction hotspots among symbionts helps to understand how lichens or other symbiotic organisms adjust to the ongoing climate change. This knowledge will, in turn, facilitate the proper conservation of the most vulnerable lichen populations. My doctoral thesis provides a conceptual framework for analyzing symbiont diversity, interaction patterns, and symbiont-mediated niche expansion that could be applied to other types of lichen species as well as other organisms involved in facultative or obligate symbiosis.
Arten von Aschersonia Mont. (Anamorphe von Hypocrella spp., Clavicipitaceae, Hypocreales, Sordariomycetidae, Askomycota) parasitieren Weiße Fliegen und Schildläuse. Petch (1921) stellte eine Monographie über Hypocrella und Aschersonia vor. Seit dieser Zeit wurden einige Arten neu beschrieben und vereinzelte Artkomplexe revidiert. Die vorgestellte Arbeit ist seit rund 80 Jahren das umfassendste Werk über die Gattung Aschersonia. Hierfür wurden Proben in Kuba, Malaysia, Mexico, Panama, Taiwan und Thailand gesammelt und z.T. kultiviert. Es werden 20 Arten detailliert vorgestellt und illustriert. Die Arten sind: A. acutispora, A. aurantiaca, A. australiensis, A. badia, A. basicystis, A. blumenaviensis, A. caespiticia [A. insperata, syn. nov.], A. columnifera, A. crenulata, A. duplex, A. hypocreoidea [A. goldiana, syn. nov.; A. confluens, syn. nov.], A. marginata, A. oxystoma, A. philippinensis, die Anamorphe von H. rhombispora, A. samoensis, A. taitensis [A. aleyrodis, syn. nov.; A. placenta, syn. nov.; A. tamurai, syn. nov.], die Anamorphe von H. tubulata, A. turbinata [A. coffeae, syn. nov.] und A. viridans. Hierzu wurden auch wichtige Merkmale wie Stromataform und Konidiengröße in situ und in vitro charakterisiert. Mit anderen gültigen Beschreibungen von Arten, die nicht untersucht werden konnten, gibt es 32 Arten. Zum ersten Mal wurden ausführliche Daten über die Wirtsinsekten sowie die Trägerpflanzen berücksichtigt. Erstmals wurde die Verbreitung der Aschersonia-Arten kritisch beleuchtet. Die Funde von A. acutispora, A. basicystis, A. hypocreoidea, A. oxystoma, A. turbinata und A. viridans sind Erstnachweise für Panama. Die Funde von A. australiensis, A. hypocreoidea, A. marginata und A. tubulata sind Erstnachweise für Taiwan. Zum ersten Mal wird für Arten der Gattung Aschersonia ein dichotomer Bestimmungsschlüssel vorgestellt. Es werden drei Hypothesen zur Phylogenie der Aschersonia spp. vorgestellt: 1. Die Stellung der Aschersonia spp. innerhalb der Clavicipitaceae basierend auf Sequenzdaten des LSU-Gens: Aschersonia bildet eine schwach unterstützte Paraphylie, dabei steht A. badia basaler als die übrigen Aschersonia-Arten. 2. Die Beziehung der Aschersonia spp. zueinander: A. badia und eng verwandte Arten parasitieren ausschließlich Weiße Fliegen und stehen basal. Arten einer zweiten Gruppe parasitieren Arten der Aleurodidae und Coccidae und Arten einer dritten Gruppe parasitieren ausschließlich Arten der Coccidae. 3. Eine phylogenetische Hypothese basierend auf Sequenzdaten der ITS: Es gibt noch zu wenig Sequenzen um eine eindeutige Aussage treffen zu können.