@phdthesis{Glos2006,
  author    = {Glos, Julian},
  title     = {Amphibian communities of the dry forest of Western Madagascar : taxonomy, ecology and conservation},
  url       = {http://nbn-resolving.de/urn:nbn:de:bvb:20-opus-18146},
  school      = {Universit{\"a}t W{\"u}rzburg},
  year      = {2006},
  abstract  = {In meiner Arbeit habe ich taxonomische, gemeinschafts{\"o}kologische und aut{\"o}kologische Aspekte im westmadagassischen Trockenwald untersucht. Ziel dieser Arbeit war es Antworten auf die Fragen zu geben wie die einzelnen Arten die Habitate in Raum und Zeit nutzen, welchen Einfluss abiotische Parameter, Austrocknungsrisiko der Laichgew{\"a}sser und Mikrohabitat haben und wie Pr{\"a}datoren die Gemeinschaft und das Verhalten einzelner Arten beeinflussen. Somit tr{\"a}gt diese Arbeit dazu bei die grundlegenden Mechanismen zu verstehen, die die Zusammensetzung einer Lebensgemeinschaft bestimmen. Im Einzelnen untersuchte ich hierzu folgende Fragestellungen: Aus welchen Arten bestehen die Anurengemeinschaften des westmadagassischen Trockenwaldes, und wie lassen sich diese Arten morphologisch voneinander abgrenzen? Welche Unterschiede finden sich zwischen den Arten bez{\"u}glich ihres Paarungssystems, ihrer life-history und ihrer Habitatwahl bzw. den Anpassungen an ihr Habitat? Gibt es spezifische Kaulquappengemeinschaften, die sich anhand biotischer und abiotischer Umweltvariablen vorhersagen lassen? Unterscheiden sich die Muster der Vorhersagbarkeit von Gemeinschaften zwischen unterschiedlichen Habitattypen innerhalb eines lokalen r{\"a}umlichen Skalenniveaus? Wie beeinflusst das Vorkommen von Raubfeinden die Verteilung von Kaulquappen und deren Verhalten auf der r{\"a}umlichen Skalenebene einzelner Laichgew{\"a}sser? Anhand welcher Umweltvariablen l{\"a}sst sich die Laichplatzwahl von Anuren in diesem Habitat vorhersagen? Wie lassen sich die Ergebnisse nutzen, um Empfehlungen zum Schutz bedrohter Arten auszusprechen? In dieser Arbeit beschreibe ich eine Froschart wissenschaftlich neu. Diese Art, Scaphiophryne menabensis, ist die seltenste Froschart in ihrem Verbreitungsgebiet, und aus meiner Arbeit resultiert die dringende Empfehlung, sie in ein bestehendes Schutzkonzept f{\"u}r den Kirindy-Wald und seine Umgebung mit einzubeziehen. Weiterhin beschreibe ich wissenschaftlich erstmalig in dieser Arbeit f{\"u}nf Kaulquappenarten und pr{\"a}sentiere Daten zu {\"O}kologie, life-history und Verhalten dieser Arten. Die wissenschaftliche Beschreibung weiterer Frosch- und Kaulquappenarten ist Gegenstand noch andauernder Studien (Scaphiophryne sp., Heterixalus carbonei und H. tricolor; Revision der Kaulquappen von Scaphiophryne). Die Ergebnisse dieser Arbeit stellen damit die Basis f{\"u}r alle weiteren {\"o}kologischen Studien an Fr{\"o}schen und Kaulquappen dieses {\"O}kosystems dar. FAZIT Die Amphibienfauna Madagaskars ist einzigartig, und sie stellt ein aufregendes Feld f{\"u}r {\"o}kologische Fragestellungen dar, sowohl als eigenst{\"a}ndiges System betrachtet als auch als Modell f{\"u}r andere Systeme. Umso mehr verwundert es, dass bislang kaum detaillierte {\"o}kologische Studien an diesem System durchgef{\"u}hrt wurden. Die vorliegende Arbeit schafft zun{\"a}chst mit der taxonomischen Beschreibung der vorkommenden Arten die Basis f{\"u}r {\"o}kologische Fragestellungen und zeigt dann auf den Ebenen sowohl der Gemeinschaft als auch einzelner Arten, wie verschiedene Umweltfaktoren die Verteilung von Anuren in Raum und Zeit beeinflussen. Es zeigt sich, dass sowohl statische Eigenschaften der Gew{\"a}sser als auch dynamische Faktoren wie Raubfeinde oder das Vorhandensein anderer Kaulquappen die Verteilung der Arten auf verschiedenen r{\"a}umlichen Skalenebenen sowie deren Verhalten beeinflussen. Somit tragen die Ergebnisse dieser Arbeit dazu bei, die grundlegenden Mechanismen zu verstehen, die die Zusammensetzung der Lebensgemeinschaften in diesem {\"O}kosystem bestimmen. Nicht zuletzt erm{\"o}glichen diese Erkenntnisse, geeignete, artenorientierte Schutzkonzepte f{\"u}r diese in ihrer Existenz stark bedrohte Anurengemeinschaft zu entwickeln und die Effekte von Habitatzerst{\"o}rung auf diese Gemeinschaft aufzuzeigen.},
  subject      = {Lurche},
  language  = {en}
}
@phdthesis{Zancolli2013,
  author    = {Zancolli, Giulia},
  title     = {Amphibian diversity along the slope of Mount Kilimanjaro: from species to genes},
  url       = {http://nbn-resolving.de/urn:nbn:de:bvb:20-opus-91792},
  school      = {Universit{\"a}t W{\"u}rzburg},
  year      = {2013},
  abstract  = {1. Since the early nineteenth century describing (and understanding) patterns of distribution of biodiversity across the Earth has represented one of the most significant intellectual challenges to ecologists and biogeographers. Among the most striking patterns of species richness are: the latitudinal and elevational gradients, with peaks in number of species at low latitudes and somewhere at mid altitudes, although other patterns, e.g. declines with increasing elevation, are often observed. Even in highly diverse tropical regions, species richness is not evenly distributed but there are "hotspots" of biodiversity where an exceptional number of species, especially endemics, are concentrated. Unfortunately, such areas are also experiencing dramatic loss of habitat. Among vertebrate taxa, amphibians are facing the most alarming number of extinctions. Habitat destruction, pollution and emergence of infectious diseases such as chytridiomycosis, are causing worldwide population declines. Responses to these drivers can be multidirectional and subtle, i.e. they may not be captured at the species but at the genetic level. Moreover, present patterns of diversity can result from the influence of past geological, climatic and environmental changes. In this study, I used a multidisciplinary and multilevel approach to understand how and to which extent the landscape influences amphibian diversity. Mount Kilimanjaro is an exceptional tropical region where the landscape is rapidly evolving due to land use changes; additionally, there is a broad lack of knowledge of its amphibian fauna. During two rainy seasons in 2011, I recorded anurans from the foothills to 3500 m altitude; in addition, I focused on two river frog species and collected tissue samples for genetic analysis and swabs for detection of chytridiomycosis, the deadly disease caused by Batrachochytrium dendrobatidis (Bd). 2. I analyzed how species richness and composition change with increasing elevation and anthropogenic disturbance. In order to disentangle the observed patterns of species diversity and distribution, I incorporated inferences from historical biogeography and compared the assemblage of Mt. Kilimanjaro and Mt. Meru (both recent volcanoes) with those of the older Eastern Arc Mountains. Species richness decreased with elevation and locally increased in presence of water bodies, but I did not detect effects of either anthropogenic disturbance or vegetation structure on species richness and composition. Moreover, I found a surprisingly low number of forest species. Historical events seem to underlie the current pattern of species distribution; the young age of Mt. Kilimanjaro and the complex biogeographic processes which occurred in East Africa during the last 20 million years prevented montane forest frogs from colonizing the volcano. 3. I focused on the genetic level of biodiversity and investigated how the landscape, i.e. elevation, topographic relief and land cover, influence genetic variation, population structure and gene flow of two ecologically similar and closely related river frog species, namely Amietia angolensis and Amietia wittei. I detected greater genetic differentiation among populations in the highland species (A. wittei) and higher genetic variation in the lowland species (A. angolensis), although genetic diversity was not significantly correlated with elevation. Importantly, human settlements seemed to restrict gene flow in A. angolensis, whereas steep slopes were positively correlated with gene flow in A. wittei. This results show that even ecologically similar species can respond differently to landscape processes and that the spatial configuration of topographic features combined with species-specific biological attributes can affect dispersal and gene flow in disparate ways. 4. River frogs of the genus Amietia seem to be particularly susceptible to chytridiomycosis, showing the highest pathogen load in Kenya and other African countries. In the last study, I collected swab samples from larvae of A. angolensis and A. wittei for Bd detection. Both species resulted Bd-positive. The presence of Bd on Mt. Kilimanjaro has serious implication. For instance, Bd can be transported by footwear of hikers from contaminated water and soil. Tourists visiting Mt. Kilimanjaro may translocate Bd zoospores to other areas such as the nearby Eastern Arc Mts. where endemic and vulnerable species may still be na{\"i}ve to the fungus and thus suffer of population declines. 5. My study significantly contributed to the knowledge of the amphibian fauna of Mt. Kilimanjaro and of East Africa in general, and it represents a valuable tool for future conservation actions and measures. Finally, it highlights the importance of using a multidisciplinary (i.e. community ecology, historical biogeography, landscape genetics, disease ecology) and multilevel (i.e. community, species, population, gene) approach to disentangle patterns of biodiversity.},
  subject      = {Kilimandscharo},
  language  = {en}
}
@phdthesis{Ernst2006,
  author    = {Ernst, Raffael},
  title     = {Anuran communities on the cutting edge : Analysing patterns and processes in anthropogenically altered tropical forests - Studies from the Guiana Shield and West Africa},
  url       = {http://nbn-resolving.de/urn:nbn:de:bvb:20-opus-18373},
  school      = {Universit{\"a}t W{\"u}rzburg},
  year      = {2006},
  abstract  = {Summary Timber harvesting is currently the most common commercial utilisation activity in tropical forests. Assessing the effects of logging on different aspects of biodiversity and general ecosystem properties is hence of prime importance if the few remaining areas of intact tropical forest are to be protected effectively and efficiently. Tropical amphibian communities are an appropriate model system for studies on the impacts of human-induced environmental changes on the dynamics of complex biological systems. This thesis elaborates on patterns of diversity changes in tropical forest amphibian communities facing habitat alterations associated with selective logging in two globally important eco-regions (C{\^o}te d'Ivoire, Upper Guinea, West Africa and Guyana, the Guiana Shield, northern South America). The thesis is organised along two main themes. After a general introduction, a section on general methodology and an introduction to the model systems studied, the first theme moves from general patterns to underlying processes. A second theme running through both chapters carries from undisturbed systems to disturbed systems. A final section integrates findings and addresses implications for conservation management of anthropogenically altered tropical forests. Several case studies at the species- population and community level are being presented and data on the direct and indirect impacts of anthropogenic habitat alteration on respective organizational levels are provided. A key statement that is stressed on throughout the studies is the fact that common measures of diversity, such as species richness and species-diversity only inadequately reflect processes of diversity change following anthropogenic disturbance. They also fail to describe actual impacts on the dynamics of complex biological systems. It is argued that commonly used measures produce an incoherent and insufficient picture of diversity patterns and the underlying processes that shape these patterns. Thus, an understanding of higher levels of diversity, such as \&\#946;-diversity and functional diversity (and hence compositional patterns) appears to be the key to effectively mitigating the impacts of human-induced disturbance on amphibian communities. It is shown that the predictability of amphibian community composition depends on the respective level of anthropogenic disturbance imposed on a particular habitat. Hence, human activities that lead to changes in the structure of a forest, such as logging, not only alter simple system descriptors, such as the number of species in a given community, but rather alter the dynamics of the entire system. In this context, functional diversity is shown to be an important aspect underlying the actual mechanism that leads to the observed change of predictability patterns. Functional differences between species, rather than number of species per se appear to be the decisive factor in sustaining desirable ecosystem states and thus in maintaining important ecosystem services. Because biological diversity appears to play a substantial role in ecosystem resilience required to safeguard essential ecosystem functions in the face of environmental change, the thesis calls for a critical revision of common diversity assessments approaches. The studies advocate the reconsideration of the uncritical use of widespread measures and descriptors of biodiversity on grounds of inconsistent patterns found throughout numerous studies, including those presented herein.},
  subject      = {Tropischer Regenwald},
  language  = {en}
}