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Institute
The fungal interaction with plants is a 400 million years old phenomenon, which presumably assisted in the plants’ establishment on land. In a natural ecosystem, all plant-ranging from large trees to sea-grasses-are colonized by fungal endophytes, which can be detected inter- and intracellularly within the tissues of apparently healthy plants, without causing obvious negative effects on their host. These ubiquitous and diverse microorganisms are likely playing important roles in plant fitness and development. However, the knowledge on the ecological functions of fungal root endophytes is scarce. Among possible functions of endophytes, they are implicated in mutualisms with plants, which may increase plant resistance to biotic stressors like herbivores and pathogens, and/or to abiotic factors like soil salinity and drought. Also, endophytes are fascinating microorganisms in regard to their high potential to produce a great spectrum of secondary metabolites with expected ecological functions. However, evidences suggest that the interactions between host plants and endophytes are not static and endophytes express different symbiotic lifestyles ranging from mutualism to parasitism, which makes difficult to predict the ecological roles of these cryptic microorganisms. To reveal the ecological function of fungal root endophytes, this doctoral thesis aims at assessing fungal root endophytes interactions with different plants and their effects on plant fitness, based on their phylogeny, traits, and competition potential in settings encompassing different abiotic contexts. To understand the cryptic implication of nonmycorrhizal endophytes in ecosystem processes, we isolated a diverse spectrum of fungal endophytes from roots of several plant species growing in different natural contexts and tested their effects on different model plants under axenic laboratory conditions. Additionally,we aimed at investigating the effect of abiotic and biotic variables on the outcome of interactions between fungal root endophytes and plants.
In summary, the morphological and physiological traits of 128 fungal endophyte strains within ten fungal orders were studied and artificial experimental systems were used to reproduce their interactions with three plant species under laboratory conditions. Under defined axenic conditions, most endophytes behaved as weak parasites, but their performance varied across plant species and fungal taxa. The variation in the interactions was partly explained by convergent fungal traits that separate groups of endophytes with potentially different niche preferences. According to my findings, I predict that the functional complementarity of strains is essential in structuring natural root endophytic communities. Additionally, the responses of plant-endophyte interactions to different abiotic factors, namely nutrient availability, light intensity, and substrate’s pH, indicate that the outcome of plant-fungus relationships may be robust to changes in the abiotic environment. The assessment of the responses of plant endophyte interactions to biotic context, as combinations of selected dominant root fungal endophytes with different degrees of trait similarity and shared evolutionary history, indicates that frequently coexisting root-colonizing fungi may avoid competition in inter-specific interactions by occupying specific niches, and that their interactions likely define the structure of root-associated fungal communities and influence the microbiome impacts on plant fitness.
In conclusion, my findings suggest that dominant fungal lineages display different ecological preferences and complementary sets of functional traits, with different niche preferences within root tissues to avoid competition. Also, their diverse effects on plant fitness is likely host-isolate dependent and robust to changes in the abiotic environment when these encompass the tolerance range of either symbiont.
Soil fungal communities are an essential element in the terrestrial ecosystem, however their response to ongoing anthropogenic climate change is currently poorly understood. Fungi are one of the most abundant groups of microbes in soil, they are mainly responsible for the decomposition of organic matter (Baldrian et al., 2012; Buée et al., 2009). By binding carbon in soil, fungi thus maintain an important role in the global carbon cycle (Bardgett et al., 2008). Future climates are likely to influence the communities of belowground microbial organisms (Castro et al., 2010; Deacon et al., 2006). However, how these communities are affected in their diversity, composition, and function after environmental perturbation is insufficiently known.
Molecular techniques using high-throughput sequencing are presently revolutionizing the analysis of complex communities, such as soil fungi. High-throughput metabarcoding enables the recovery of DNA sequence data directly from environmental samples, and DNA sequences from entire communities present in these samples can be simultaneously recovered through massively parallel sequencing reactions (Bik et al., 2012; Taberlet et al., 2012b). This results in more accurate estimation of diversity and community composition and thus provides unprecedented insight into cryptic communities (Lindahl and Kuske, 2014). Yet, challenges associated with these novel techniques include the bioinformatic processing, and the ecological analyses of the large amount of sequence data generated. Most biologists without explicit training in bioinformatics spend a fair amount of time learning how to filter raw sequence data, and customize bioinformatics pipelines specific to their project. To improve the quality of data treatment, and decrease the time needed for the analyses, it is desirable to have bioinformatics pipelines that are easy to use, well explained to researchers not trained in bioinformatics, and adaptable to individual research needs...
Gallery forests (GFs) are floristically and functionally distinct forests along rivers and watercourses. The GFs of the West African savannas form thin stripes with a particular, species-rich flora differing significantly from the surrounding vegetation. Due to their relative isolation in the savannas and their dependence on rivers, GFs are particularly endangered by the expected global climate changes in the 21st century. Despite their high diversity, little is known about the ecology and biogeography of GFs in West Africa. Especially, their response to climate changes and their vegetation dynamics remain largely unknown. This thesis combines floristic, phylo-geographic and ecological data to investigate the biodiversity, historical and recent biogeography and conservation status of GF species in Burkina Faso (BFA) as a model for West Africa.
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.
Hyperparasitic fungi on black mildews (Meliolales, Ascomycota) : hidden diversity in the tropics
(2023)
Meliolales (Sordariomycetes, Ascomycota) is a group of obligate plant parasitic microfungi mainly distributed in the tropics and subtropics. Meliolalean fungi are commonly known as “black mildews”, as they form black, superficial hyphae on the surface of vegetative and reproductive organs of vascular plants. They are considered biotrophic parasites, and the infections caused by black mildews can lead to a decrease in the photosynthetic activity of plants, as well as to an increase in the temperature and respiration rate of their leaves.
Meliolales are frequently parasitized by hyperparasitic fungi, i.e., parasitic fungi that have parasitic hosts. These hyperparasites are all Ascomycota and belong mainly to the Dothideomycetes and Sordariomycetes. Although hyperparasites represent a megadiverse group, species were only described by morphology until 1980, and the systematic position of more than 60 % of known species is still unclear. In addition, there are no DNA reference sequences available in public databases for any of the species of hyperparasites of Meliolales, and no ecological studies have been done up to now.
Before this study, no exact number of hyperparasitic fungi growing on colonies of black mildews existed. Here, we present a checklist including 189 species of fungi known to be hyperparasitic on Meliolales, but the number of existing species is likely to be even higher. The elaboration of this species checklist laid the foundations for this investigation, as it helped to understand the present state of knowledge of hyperparasitic fungi on Meliolales worldwide.
For the present study, fresh specimens of leaves infected with colonies of Meliolales and hyperparasites were opportunistically collected at 32 collection sites in Western Panama and Benin, West Africa, in 2020 and 2022, respectively. In total, 100 samples of plant specimens infected with black mildews were collected, of which 58 samples were parasitized by hyperparasitic fungi. 31 species and morphospecies of hyperparasitic fungi were identified. In addition, 35 historical specimens, including 12 type specimens, were examined for the present work.
DNA of hyperparasitic fungi was isolated directly from conidia, synnemata, apothecia, perithecia or pseudothecia of fresh and dried specimens. The main challenges faced by scientists in doing molecular studies of hyperparasitic fungi are related to the fact that the hyperparasitic fungi are intermingled with tissues of the meliolalean hosts and other organisms present in a given sample. This makes the isolation of DNA exclusively from the hyperparasite difficult. Moreover, hyperparasitic fungi on Meliolales are biotrophs and cannot be grown axenically. The hosts themselves are also biotrophic, further complicating DNA isolation from either partner. These factors have contributed to a lack of reference sequences in public databases. After more than 100 attempts, DNA of 20 specimens of hyperparasitic fungi, representing seven species, has been isolated in the context of the present investigation. Three partial nuclear gene regions were amplified and sequenced: nrLSU, nrSSU and nrITS. The datasets were assembled for phylogenetic analyses applying Maximum Likelihood (ML) and Bayesian inference (BI) methods. DNA sequences of hyperparasitic fungi on Meliolales were generated for the first time in the context of the present investigation.
Hyperparasitic fungi on Meliolales do not represent a single systematic group, but a polyphyletic ecological guild of fungi. Because of this huge diversity, only the systematics of species of perithecioid hyperparasites, as well as of the species of the genera Atractilina and Spiropes known to be hyperparasitic on black mildews was discussed in this thesis, as they represented the most common groups of fungi found in Benin and Panama. The results indicated, for example, the systematic position of Dimerosporiella cephalosporii and Paranectriella minuta in the Sordariomycetes and Dothideomycetes, respectively. In addition, the first record of a hyperparasitic fungus of black mildews in the Lecanoromycetes, namely Calloriopsis herpotricha, is reported here. The systematics of Atractilina parasitica and of some species of Spiropes is also discussed here.
In the context of the present investigation, four species new to science were described. They are presented with detailed descriptions, photos and scientific illustrations. Taxonomic studies of this thesis also generated seven new synonyms, nine new records for Benin, seven for Panama, one for Africa and two for mainland America, as well as the confirmation of one anamorph-teleomorph connection by molecular sequence data.
The ecology of hyperparasitic fungi on Meliolales is complex and far from being completely understood. The hypothesis of host specificity between hyperparasitic fungi, their meliolalean hosts and their plant hosts was tested for the first time, through a tritrophic network analysis. Results indicate that hyperparasites of Meliolales are generalists concerning genera of Meliolales, but apparently specialists at the level of order. In addition, hyperparasitic fungi tend to be found alongside their meliolalean hosts, suggesting a pantropical distribution.
Fungi are an important component of every ecosystem but hardly considered in biodiversity monitoring projects. This thesis aims at characterizing fungal diversity, with an emphasis on epigeous fungi, encompassing different biogeographic zones and points in time. A main sampling area was established in the Taunus mountain range in Germany, which was sampled monthly over three years.
For testing species richness on spatial scale, the Taunus transect was compared with four other areas, which were assessed with lower sampling effort. One of these areas was Bulau in Germany, in which four excursions were made. Furthermore, two sampling events were performed in Somiedo in Spain and one sampling event in Kleinwalsertal in Austria. Already existing data of a two-year monitoring project in Panama next to the river Majagua were additionally used for comparison.
All these areas were investigated with a standardized sampling protocol focusing on macroscopically evident fungi and vascular plants using a time-restricted transect design. The transects consisted of strips, which were 500 m long and about 20 m broad, and were sampled for 2 hours at each single sampling event....
Antagonistic and mutualistic species interactions provide important ecosystem functions affecting plant population dynamics and distribution. Many of these functions are important for the regeneration of plants, either by limiting or facilitating successful transition between life stages. Interactions can occur across the whole geographical range of a species and thereby encompass different environmental gradients, such as changes in temperature or water availability. Understanding the joint effects of species interactions and environmental factors on the regeneration of plants is key for understanding plant population dynamics under global change and could provide important recommendations for managing and conservation efforts.
My thesis aimed at advancing the knowledge of how species interactions depend on environmental conditions and jointly affect plant recruitment along the elevational distribution of plants. This thesis includes three chapters in which I studied the effects of animal seed deposition, seed predation, mycorrhizal and pathogenic fungi occurrences as well as abiotic and biotic environmental factors on the recruitment of Swiss stone pine (Pinus cembra). I conducted fieldwork in the Swiss Alps across the entire elevational distribution of the pine (1850 – 2250 m a.s.l). Over a period of three years, I recorded animal seed deposition by spotted nutcrackers (Nucifraga caryocatactes) and conducted seed translocation experiments. Further, I assessed fungal communities using DNA metabarcoding. I measured abiotic environmental factors such as temperature, water and light availability, pH, as well as biotic environmental factors such as distance to conspecific adults and ground vegetation cover. In my thesis, I used a broad range of community ecology approaches, from seed dispersal ecology to experimental plant ecology and microbial ecology.
First, I investigated the effects of environmental factors on four recruitment processes (i.e. seed deposition, seed predation, seed germination, seedling survival) of Swiss stone pine. Further, I aimed at identifying the most important recruitment processes potentially limiting pine regeneration across its elevational range. To investigate pine recruitment, I firstly tested how seed deposition, seed predation, seed germination and seedling survival were affected by the microhabitat characteristics ultimately determining where a seed arrives in the environment (i.e. canopy cover & ground vegetation cover). Secondly, I applied a sensitivity analysis to investigate which of the four recruitment processes poses limitation to the pines’ regeneration across its range. My results reveal that the importance of particular recruitment processes varies along the pines’ elevational range. I found that at the lower range margin and the distribution centre seed germination and seedling survival were the main limiting factors, whereas animal-mediated seed dispersal became especially important at the upper range margin. My study contributes to the field with a new approach for disentangling the relative importance of recruitment processes across environmental gradients and thereby could help to project how plant recruitment might respond to future changes in environmental conditions.
The second aim of my study was to investigate how abiotic and biotic environmental factors affect the occurrence of Swiss stone pine-associated pathogenic and mutualistic fungi by combining field measurements of environmental factors with a DNA metabarcoding approach. I identified potentially important fungal interaction partners of the pine and determined drivers shaping their occurrences. My results reveal that generalist fungi were not affected by abiotic and biotic environmental factors. However, specialist pathogens showed patterns according to the Janzen-Connell framework (i.e. accumulation of pathogen close to adult plants). Interestingly, I found evidence for an “inverse” Janzen-Connell effect, i.e. high abundance of a specialist mutualist close to adult plants, potentially mitigating effects of soil pathogens close to parent trees. Further, I found that pine-associated fungi are distributed widely within and beyond the range of their host plant, adding knowledge on how mutualisms and antagonisms might be affected when plants move their distributional range upwards.
Finally, I investigated how known and unknown plant-associated fungi affect the regeneration of Swiss stone pine in an environmental context. My results suggest that seedling establishment was most strongly affected by abiotic environmental factors, such as light availability and maximum summer temperature. Further, the results indicate that seedling survival was affected by biotic environmental factors, i.e. fungal agents, with high abundances of a known fungal pathogen co-occurring with low seedling survival rates. My results also reveal that known mycorrhizal partners as well as a large number of unknown fungal operational taxonomic units (OTUs) were associated with the survival of seedlings. My findings highlight the importance of plant-fungal interactions for plant recruitment and offer a feasible approach for the identification of hidden plant-fungal associations in highly complex DNA metabarcoding datasets. This approach offers a valuable tool for investigating plant-microbe interactions, ultimately helping to understand plant population dynamics.
My dissertation adds to a deeper understanding on the linkage between plant regeneration and species interactions, especially on how plant-animal and plant-fungal interactions in concert with environmental factors shape plant recruitment. My study reveals the importance of animal-mediated seed dispersal and fungal pathogens in plant recruitment with consequences for potential range shifts of plant species. My thesis has important implications for conservation and management efforts by informing on key species interactions under environmental change.
Plant parasitic species of Asterinaceae and Microthyriaceae (Dothideomycetes, Ascomycota, Fungi) are inconspicuous foliicolous fungi with a mainly tropical distribution. They form black colonies on the surface of living leaves. Members of Asterinaceae and Microthyriaceae are characterized by shield-shaped, flat ascomata (thyriothecia) which grow completely superficially on the leaf cuticle. Microthyriaceae, Asterinaceae and other families of thyriothecia-forming ascomycetes belong to the class Dothideomycetes due to the presence of bitunicate asci. However, until today no consistent taxonomic concept nor molecular phylogenetic studies exist for the families of thyriothecioid ascomycetes. In the present thesis, 42 species belonging to 13 different anamorphic and teleomorphic genera of Asterinaceae, Microthyriaceae and ‘Pycnothyriales’ recently collected in Western Panama, are identified, described in detail and illustrated with drawings, transmission and scanning electron microscopical photographs. Among the 42 species, 37 species belong to the Asterinaceae, four species to the Microthyriaceae and one species to the from group ‘Pycnothyriales’. Two species of Asterinaceae are new to sience: Asterina gaiadendricola with an Asterostomella anamorph and Asterina schlegeliae with a Mahanteshamyces anamorph. Among the remaining species of Asterinaceae, 28 species represent new records for Panama: Asterina cestricola, A. ciferriana, A. consobrina, A. corallopoda, A. davillae with anamorph, A. diplocarpa, A. diplopoda, A. ekmanii, A. fuchsiae, A. manihotis, A. phenacis, A. radiofissilis with anamorph, A. siphocampyli, A. sponiae, A. stipitipodia with anamorph, A. styracina, A. tonduzii with anamorph, A. weinmanniae, A. zanthoxyli, Asterostomella dilleniicola, Asterolibertia licaniicola, Asterolibertia nodulosa, Cirsosia splendida with its Homalopeltis chrysobalani anamorph and Prillieuxina winteriana with its Leprieurina winteriana anamorph. The remaining 11 species of Asterinaceae probably respresent new species: Asterina spp. 1-8, Asterolibertia sp., Halbanina sp. and Mahanteshamyces sp. The four species of Microthyriaceae are new records for Panama: Maublanica uleana, Platypeltella irregularis, Platypeltella smilacis and Xenostomella tovarensis. The species Hemisphaeropsis magnoliae in the form group ‘Pycnothyriales’ is a new record for Panama. During this study, voucher material of 44 additional species of plant parasitic thyriothecioid ascomycetes was examined. Thereby, the number of species of Asterinaceae known for Panama since 2006 raises from four to 30, for Microthyriaceae respectively from zero to four and for ‘Pycnothyriales’ from zero to one. 21 of the presented species are new records for Central America and two species are new records for the American Continent. The presented 42 species parasitize 47 host plant species in 39 genera belonging to 28 plant families. For 23 fungal species, new host plant species are discovered. From those, seven belong to host plant genera not reported before to be parasitized by a member of Asterinaceae and Microthyriaceae: Burmeistera (Campanulaceae), Curatella and Davilla (Dilleniaceae), Greigia (Bromeliaceae), Hirtella (Chrysobalanaceae), Oxandra and Xylopia (Annonaceae). In this study, the first molecular phylogenetic approach in Asterinaceae is provided. For the first time, DNA was isolated from fresh material of Asterina spp. and their respective anamorphic stages on leaves in Panama. The hypothesis derived from SSU and LSU rDNA neighbour-joining analysis supports the monophyly of the Asterinaceae and suggests a close relationship to Venturiaceae within the class Dothideomycetes. The data obtained from the ppMP project (plant parasitic microfungi of Panama) indicate a constant but low abundance of plant parasitic thyriothecioid ascomycetes in natural plant communities in Panama, with Asterinaceae as the most species-rich and diverse family. Further collection activities in tropical regions worldwide will certainly increase our knowledge about species diversity and ecology of tropical plant parasitic thyriothecioid ascomycetes.
This study comprises a survey on ecology, morphology and taxonomy of parasitic fungi infecting Pteridophytes and Orchidaceae found by the author on several field trips to Western Panama as part of the project plant parasitic micro-fungi of Western Panama (ppMP). In Panama, approximately 9500 species of vascular plants are found. Of these, Orchidaceae are with ca. 1150 (ca. 12%) species by far the most speciose family. The Pteridophytes in Panama comprise ca. 940 species in 31 families. Most fungal pathogens on Orchidaceae in tropical regions were described from plants in culture or from material intercepted at borders by plant quarantine services and not from their natural habitats. Therefore, little is known about distribution and ecology of these pathogens in their natural range. The author determined and classified several hundred Orchidaceae-species and Pteridophytes at the sites selected in the context of the project. This work facilitated the identification of many host plants (at least to genus-level) even in sterile condition in the field. About 65 species of Pucciniales are known to infest Orchidaceae and ca. 38% of them are described from tropical America. All available types of Pucciniales on Orchidaceae in tropical America were studied and compared with 91 specimens of rust fungi on orchids collected by the author in Panama. Several hundred additional specimens housed in the BPI, almost all intercepted from plant quarantine services, were used for comparison. As result of this work, it is suggested to combine Uromyces stenorrhynchi Henn. to Sphenospora and, as this is the oldest epithet, to synonymize S. kevorkianii Linder, S. mera Cumm. and S. saphena Cumm. with it. Further, it could be demonstrated that Uredo aurantiaca Montemartini, U. cyrtopodii Syd. & P. Syd., U. epidendri Henn., U. guacae Mayor, U. gynandrearum Corda, U. lynchii (Berk.) Plowr., U. neopustulata Cumm. (≡U. pustulata Henn.), U. nigropuncta Henn., U. oncidii Henn., U. ornithidii F. Kern., Cif. & Thurst., and presumably U. scabies Cke., are anamorphs of this variable species. U. gynandrearum is the oldest anamorph-name for all these taxa. Therefore, it can be established that this rust infects more than 80 species of Orchidaceae in three subfamilies. In total, the anamorph of this species was collected by the author on 17 different species of Orchidaceae in Panama which, apart from one species, are all new hosts to science. The molecular data obtained by the author confirm this view, although more data, especially from material from the whole range of distribution of U. gynandrearum, are necessary. Puccinia spiranthicola Cumm. was found to be a synonym of P. cinnamomea Diet. & Holw. and was found by the author on three different Orchidaceae in two subfamilies. Uredo pleurothallidis Keissl. is now considered a synonym of U. wittmackiana Henn. and the latter as the anamorph of Puccinia oncidii Cumm. In the anamorph genus Uredo, a new species was found infecting at least five different species of Sobralia and Elleanthus (Sobraliinae) at different localities. Molecular data indicate it to be related to the currently polyphyletic Phakopsoraceae. For the rusts with suprastomatal sori on Orchidaceae, now separated from Hemileia and placed in the genus Desmosorus (nom. inval.), the current concept with only one taxon is rejected and the establishment of three subspecies is suggested. The complicated taxonomy is discussed and makes it necessary to validate the genus-name and make a new combination. Another Hemileia-anamorph species was found by the author and is considered to be new to science. This is the first species of this alliance in America on Orchidaceae. Molecular data obtained by the author confirm the separation of Desmosorus from Hemileia and the position of the new species. For rusts on Pteridophytes, a new species of Milesia, (teleomorph: Milesina) and a new anamorphic species of Uredinopsis was found, both on hosts hitherto not known. In Calidion, the presumable anamorph-genus of Uncol, the species C. cf. cenicafeae Salazar & Buriticá was found on several new hosts. Further, the teleomorph was found. Morphologically, this teleomorph did not agree with the description of Uncol by the author of the genus, although the anamorph characteristics left no doubt that it is Calidion. Apparently, the description of Uncol is inadequate, but cannot be improved, as the type is unavailable. Molecular data obtained by the author show this species to be closest to Desmosorus. For Uredo superficialis Speg., the anamorph of Desmella, nine new hosts in eight different fern families were found by the author and the collaborators of the ppMP-project. Ecological data indicate that this species includes different host specific races, which, however could not be distinguished morphologically. For all these rusts, a thorough discussion of the ecology in their habitats is given. In total, 21 LSU rDNA sequences from 6 different rust species on Orchidaceae and Pteridophytes were obtained and analyzed with the Maximum Parsimony and Minimum Evolution method. Here, the position of several groups could be confirmed, and some anamorphs could be assigned to different teleomorphic relationships. Within the Ascomycota and their anamorphs, several hitherto unknown species and species not known from these hosts or not known from Panama were found and analyzed. On Orchidaceae, the following fungi belonging to the Ascomycota are described, illustrated and discussed: In the Phyllachorales, a hitherto not known Phyllachora sp. was found on Oncidium warszewiczii Rchb. f. and was compared with the other species of this order currently known from Orchidaceae. In the Asterinaceae s. l. Lembosia cf. epidendri Meir. Silva & O. R. Pereia was found on Maxillaria crassifolia (Lindl.) Rchb. f., which is a new host and new host alliance for this fungus hitherto only known from Brazil. The fungus is described and compared with all species of Asterinaceae currently known on Orchidaceae. In the Meliolaceae, Meliola orchidacearum Cif. was found on Camaridium biolleyi (Schltr.) Schltr. and an Epidendrum sp. which are new hosts and new host alliances of this fungus which was hitherto only known from the Caribbean Islands. It is described, illustrated and compared with the type. In the Glomerellaceae, Glomerella cingulata and its anamorph Colletotrichum gloeosporioides were found on several hosts. The species is illustrated, described and compared with data from literature. In the anamorphic Mycosphaerellaceae, Pseudocercospora odontoglossii (Prill. & Delacr.) U. Braun, a species currently only known from culture, was found on the new host Pleurothallis imraei Lindl. It is illustrated, described and compared with data from literature. On ferns, the following other fungi are described, illustrated and discussed: A conspicuous undescribed form of Polycyclus was found by the author on Elaphoglossum ciliatum (C. Presl.) T. Moore (Dryopteridaceae) and Serpocaulon loriceum (L.) A. R. Sm. (Polypodiaceae). A conspectus of Parmulariaceae infecting ferns is given and demonstrated that Polycyclina should be synonymized under Polycyclus. Summing up, it can be assessed, especially for the Pucciniales, that the most speciose plant family in Panama carries remarkable few species of specific parasites, and that many of them seem to be distributed over a wide range of species which often are not closely related. One reason amongst others seems to be that parasites need a minimum density of host plants in a habitat to survive. As orchid species often occur with only few (and often small) individual plants at a given locality, the probability for a specific pathogen to infect a plant gets too low, hence high diversity by low abundance of hosts might be an impediment for specific pathogens. In this case, unspecific parasites, or such which are infecting larger alliances, are in advantage. Other reasons could be specific traits of orchids, like succulence and mycotrophy which might hamper fungal infections.
Fungi belonging to the Rhytismatales (Ascomycota) are parasites or endophytes of plants, some are saprophytes. Their fruiting bodies are localized in different organs of the host plants belonging to many different families of gymnosperms and angiosperms. Many species of Rhytismatales are known on species of Pinaceae, Ericaceae, and Poaceae. These fungi usually have ascomata that are more or less embedded in host tissue and open by longitudinal or radial splits. They have a more or less carbonized covering stroma, thin-walled, iodine negative asci, and ascospores usually covered by gelatinous sheaths.
In the present study, two lists of species of Rhytismatales in China are presented. One is based on literature and includes 103 species in 15 genera. The second one contains the names of the species in the present study, 57 species in 20 genera based on 90 specimens I collected in the Yunnan and Anhui province in China during July to August in 2001. 31 species in the second list are new species or new records for China, so we presently know 134 species in 22 genera of Rhytismatales for China. 28 new species of Rhytismatales are proposed, 21 species from the Yunnan province and seven from the Anhui province. Among them, three new species are proposed in three new genera, Nematococcomyces, New Genus 1, and New Genus 2, respectively. The 28 new species are Cerion sp., Coccomyces spp. 1-2, Colpoma spp. 1-2, Hypoderma spp. 1-6, Lirula sp., Lophodermella sp., Lophodermium spp. 1-5, Nematococcomyces rhododendri C.-L. Hou, M. Piepenbr. & Oberw., Neococcomyces sp., New Genus 1 sp., New Genus 2 sp., Rhytisma spp. 1-2, Soleella sp., Terriera spp. 1-2, and Therrya sp. The genus Davisomycella is proposed as a synonym of Lophodermella based on observations of the morphology, ecology, and the infected organ. The four genera Cerion, Naemacyclus, Terriera, and Therrya, and three species, Hypoderma rubi, Lophodermium uncinatum, and Naemacyclus pinastri, are reported for the first time for China. All the new taxa, the newly recorded ones, as well as six species which had not been illustrated in detail before, are carefully described and illustrated by line drawings in the present study.
The results show that species of Rhytismatales are highly diverse especially in the natural vegetation in high mountainous areas in China. Most species of Rhytismatales are conspicuously host specific. The diversity of Rhytismatales is closely related to that of the preferred hosts, which are members of Pinaceae, Ericaceae, and Cupressaceae. Based on the detailed morphological observations, the significance of different morphological characteristics for a natural classification of Rhytismatales is discussed. Genera are traditionally defined by character states of a few characteristics, namely the opening patterns of ascomata, the depth of ascomata in the host tissue, and asci and ascospore shape. Data from collections in the field, detailed morphological investigation, and molecular data show, however, that the ecology, the infected organ, the host relationship, and many other characteristics have to be combined to circumscribe natural groups.
The discussion of the systematic significance of morphological characteristics is complemented by molecular data. In the present study, partial nuclear large subunit rDNA sequences of 52 specimens representing 38 species are used to analyse phylogenetic relationships for members of Rhytismatales.
Most species of Rhytismatales are placed in a monophyletic group corresponding to the Rhytismatales in the Maximum Parsimony analysis. The delimitation of the Rhytismatales from the Helotiales is, however, difficult. Cyclaneusma minus should be transferred from the Rhytismatales to the Helotiales, and Cudonia circinans and Spathularia flavida from the Helotiales to the Rhytismatales. These tranfers have previously been proposed based on SSU rDNA analysis by other authors. New Genus 1 sp. has morphological characteristics typical for species of Rhytismatales. In the LSU rDNA analysis, however, it is more closely related to Helotiales rather than toRhytismatales. Therefore New Genus 1 sp. is placed in the Helotiales.
Tryblidiopsis pinastri is morphologically intermediate between members of Rhytismataceae and Cudoniaceae. LSU rDNA sequences in the present study show that T. pinastri is more closely related to species of Cudoniaceae. Therefore, this species is removed from the Rhytismataceae to the Cudoniaceae. The delimitation of further families could not be resolved in the present analysis.
Though many new morphological, ecological, and molecular phylogenetic findings are contributed for the first time, the systematic conclusions at generic, family, and order level can only be fragmentary in the present study. With more collections and more molecular data of the worldwide 450 known and many more unknown species of Rhytismatales at hand, a natural system combining morphological and molecular analysis can be elaborated.