Refine
Year of publication
Document Type
- Doctoral Thesis (22)
Has Fulltext
- yes (22)
Is part of the Bibliography
- no (22)
Keywords
- Abrasio dentium (1)
- Aquatisches Ökosystem (1)
- Artbildung (1)
- Backenzahn (1)
- Bioakkumulation (1)
- Biogeographie (1)
- Biogeography (1)
- Biokonzentration (1)
- Biomagnifikation (1)
- Capoeta damascina (1)
Institute
Capoeta damascina (Teleostei: Cyprinidae) is one of the most common freshwater fish species, found throughout the Levant, Mesopotamia, Turkey and Iran. According to the state of knowledge prior to this study, C. damascina, which is distributed over a wide range of isolated water bodies, was not a well-defined species. It was questionable whether it represents a single species or a complex of closely related species with high intraspecific and comparatively low interspecific variability. The goal of this study was to investigate the taxonomy, systematic position of the C. damascina species complex and the phylogenetic relationships among its members, based on morphological features as well as molecular phylogeny. Samples obtained from throughout the geographic range of this species complex were subjected to comparative morphological analyses in order to define, properly diagnose and separate species within the C. damascina complex. To elucidate phylogenetic relationships among members of the C. damascina species complex, samples were subjected to genetic analyses, using two molecular markers targeting the mitochondrial cytochrome oxidase I (COI, n = 103) and the two adjacent divergence regions (D1-D2) of the nuclear 28S rRNA genes (LSU, n = 65). Based on morphological and molecular genetic data, six closely related species were recognized within the C. damascina complex: C. buhsei, C. caelestis, C. damascina, C. saadii, C. umbla and an undescribed species, Capoeta sp.1. Analyses of the morphometric and meristic data obtained in this study revealed phenotypic variability among the various populations within a species and among the different species. Such differences in morphological characters reflect genetic differences, environmentally induced phenotypic variation or both, as the meristic phenotype of fish is sometimes a consequence of environmental parameters acting on the genotype. Based on phylogenetic analyses, two main lineages were identified within the C. damascina species complex: a western lineage represented by C. caelestis, C. damascina and C. umbla and an eastern lineage represented by C. buhsei, C. saadii and Capoeta sp.1. The close phylogenetic relationships between C. damascina and C. umbla and the sharing of same haplotypes between one specimen of C. damascina from Euphrates and another of C. umbla from Tigris reflect one of three possibilites: recent speciation, mitochondrial introgression or a combination of both. The results obtained in this study indicate that speciation of the above-mentioned six taxa is quite recent and that their dispersal and present-day distribution can be related to Pleistocene events. The drying out of the Persian Gulf, probably during one of the first glacials of the Pleistocene, led the ancestor of the C. damascina species complex in Mesopotamia to reach the rivers of the Gulf and of Hormuz basins and differentiate there, giving rise to the eastern lineage (ancestor of C. buhsei, C. saadii and Capoeta sp.1). As connections presumably existed among the different river drainages and basins in Iran during the wet periods of the Pleistocene, the ancestor of C. buhsei, C. saadii and Capoeta sp.1 was subsequently able to colonize the various Iranian drainages and differentiate there, giving rise to C. buhsei, C. saadii and Capoeta sp.1. After the separation from the eastern lineage, the western lineage, represented by the ancestor of C. damascina, C. umbla and C. caelestis, most likely reached the Levant from the Tigris-Euphrates system during the Pleistocene glacials, when river connections existed in the regions of the upper courses of Ceyhan Nehri (southern Turkey) and some western affluents to the Euphrates. From Ceyhan Nehri, it dispersed into other rivers in southern Turkey during Pleistocene periods of low sea levels until it reached Göksu Nehri and evolved into C. caelestis. The sister population differentiated into C. damascina and C. umbla. Based on the results obtained in this study, it is likely that C. damascina colonized the Levant and southern Turkey during the Pleistocene glacials. This is well supported by the low genetic variability among the C. damascina populations. Direct connections existed among the river drainages in the Levant during the Pleistocene periods of low sea level, thus serving as a pathway for the dispersal of C. damascina. The results of this study provide a coherent picture of the taxonomic position, phylogenetic relationships and evolutionary history of the C. damascina species complex and explain present patterns of distribution considering paleogeographic events.
Taxonomy, phylogeny and zoogeography of the hexaploid Torini of the Middle East and North Africa
(2017)
Fishes of the tribe Torini Karaman, 1971 (Teleostei: Cyprinidae) are a diverse group of primary freshwater fishes, distributed in Africa, the Middle East, and Indomalaya. They are an important component of the native freshwater-fish fauna of the Middle East and North Africa, and occur in most large river systems of the Levant, Arabia, Mesopotamia, southern Iran, and Morocco. They belong to the subfamily Cyprininae, are characterised by being tetraploid or hexaploid, having large scales, and a smooth and ossified last unbranched ray in the dorsal fin. As primary freshwater fishes they are not able to tolerate marine conditions and depend on direct freshwater connections for their dispersal. This makes them an ideal model for zoogeographic studies.
Prior to this study, the diversity of the Torini species in the Middle East and North Africa was not well understood. The validity of several genera and species was unclear, and the generic assignment of several species changed frequently.
In this PhD project the taxonomy, phylogeny, and zoogeography of the Torini of the Middle East and North Africa were investigated with morphological, as well as molecular methods. More than 1550 fish specimens were examined morphologically. Some of the specimens, including the types of most nominal species, were already available from museum collections. The remaining specimens were collected during expeditions to Ethiopia, Iran, Jordan, Morocco and Syria. Tissue samples were collected for molecular genetic analyses. The mitochondrial genes for cytochrome b, NADH dehydrogenase subunit 4 and the tRNAs for serine and histidine were sequenced from more than 120 specimens, representing 20 species of Torini and two small, diploid African barbs (Cyprinidae, tribe Smiliogastrini). Molecular data were analysed with Bayesian inference and other methods.
The analyses confirmed that the hexaploid Torini of Africa and the Middle East form a monophyletic group. In the Middle East and North Africa the Torini are represented by the genera Arabibarbus, Carasobarbus, Mesopotamichthys, and Pterocapoeta. These genera are each morphologically diagnosable, monophyletic, and genetically distinct. The species 'Labeobarbus' reinii cannot be assigned to any of these genera, because it is morphologically dissimilar and genetically clearly separated from each of them. A generic name for this species is presently not available and until the description of a new genus it is preliminarily assigned to the genus 'Labeobarbus'.
Out of the 28 species-group taxa described from the Middle East and North Africa until now, 15 are valid: Arabibarbus arabicus, A. grypus, A. hadhrami, Carasobarbus apoensis, C. canis, C. chantrei, C. exulatus, C. fritschii, C. harterti, C. kosswigi, C. luteus, C. sublimus, Mesopotamichthys sharpeyi, Pterocapoeta maroccana, and 'Labeobarbus' reinii.
The phylogenetic relationships between the Middle Eastern and North African Torini are well resolved, based on the analysis of mitochondrial DNA sequences from nearly all relevant species.
The interspecific and intraspecific morphological and genetic diversity is shaped by the zoogeographic history. Conclusions can be drawn about the events that shaped the evolution of this group. The Torini originated in the Indomalayan biogeographical realm and colonised the Middle East and Africa during the Miocene via the Gomphotherium landbridge. The Indomalayan Torini are tetraploid, whereas those of the Middle East and Africa are hexaploid. Molecular phylogenetic analyses showed that the hexaploid Torini cluster within the tetraploid Torini. This makes the tetraploid Torini a paraphyletic group with respect to the hexaploid Torini. Morocco was colonised in two independent waves. The first came from sub-Saharan Africa and is represented by Pterocapoeta maroccana. The second originated in the Middle East and gave rise to C. fritschii, C. harterti, and probably 'L.' reinii. The Tigris-Euphrates system is the largest freshwater system in the Middle East. Its central position between the Orontes River and Jordan River in the West, the Iranian tributaries to the Persian Gulf in the East, and the Arabian Peninsula in the South made it an important crossroad for the colonisation of the Middle East by Torini and other freshwater biota. During the Miocene the predecessors of the Jordan and Orontes rivers were connected to the Tigris-Euphrates system. The Jordan River was separated from the Euphrates before the Orontes. Arabia was colonised in two waves. The first (A. arabicus, A. hadhrami, C. exulatus) dates to the Pliocene, whereas the second (C. apoensis) ended as recently as the late Pleistocene or early Holocene.
In this study I analysed past and recent Daphnia populations from Lake Constance and Greifensee. Herefore, I first established a set of microsatellite markers applicable to European Hyalodaphnia species (chapter 1). Primers were also identified for species specific fragment lengths. 32 markers were then available to characterize the resting egg banks of Daphnia galeata and D. hyalina. Chapter 2 presents the reconstruction of the taxonomic composition in these two ecologically different lakes. This part of my work shows that the eutrophication that occurred in both lakes in the mid of the last century has strongly influenced the Daphnia populations. In both lakes Daphnia galeata established and hybridized with the indigenous D. hyalina. Interspecific hybridization resulted in introgression on the mitochondrial and nuclear level. In chapter 3 resting eggs from the sediments of the 1960s, 1970s, 1980s, 1990s and 2000s were characterized with microsatellite markers. The aim was to specify the extent of interspecific hybridization and nuclear introgression assuming that the genetic exchange between both species has an impact on their adaptation to their habitat. In life history experiments D. galeata and D. galeata x hyalina clones hatched from different time periods showed significant differential responses to food quality. Therefore, the question had to be answered how the Daphnia resting egg bank and the planktonic population are connected. In chapter 4 hatching experiments were conducted to bridge this gap of scientific knowledge in the life cycle of cyclic parthenogenetic waterfleas. Only D. galeata individuals were able to establish a clonal lineage after maturity. All observed recombinant individuals did not reproduce at all or firstly went through another sexual phase of reproduction i.e. produced resting eggs. In order to compare the findings of chapter 4 with the taxon composition of the recent planktonic population of Daphnia in Lake Constance, samples were taken over one season (between May 2005 and September 2006). During the season, the taxonomic composition of Daphnia changes severely with D. galeata being most abundant during the warm season and D. hyalina in the cold season. Moreover, some individuals were detected, that did not follow this pattern. With mitochondrial analysis those individuals were identified as mitochondrial introgressants and processed to life history experiments. Significant differences in the somatic growth rate under different temperatures (5°C, 12.5°C and 20°C) were related to the origin of the mitochondrial genome rather than the nuclear taxonomic assignment of the individual.
The findings of this study show that all organisms exposed to rapid ecological changes and their microevolutionary reaction to those.
Molekulare Systematik und Phylogeographie der Formengruppe Ancylus fluviatilis O. F. Müller 1774
(2001)
Ziel dieser Dissertation war es, die genetische Variation innerhalb der Formengruppe Ancylus fluviatilis (Gastropoda: Basommatophora) zu untersuchen, und eine auf molekula ren Markern basierende Phylogenie zu erstellen. Die phylogenetischen Untersuchungen beinhalteten auch die Stellung der Familie Ancylidae innerhalb der Basommatophora. Außerdem wurde die geographische Verteilung der genetischen Variation untersucht und die phylogeographischen Prozesse, die zu dieser Verteilung geführt haben, analysiert. Die gefundene genetische Konstitution wurde im Zusammenhang mit bereits vorhandenen Daten über chromosomale und fortpflanzungsbiologische Besonderheiten von A. fluviatilis diskutiert. Für 147 Individuen aus 62 Populationen des gesamten Verbreitungsgebiets von A. fluviatilis wurden mitochondriale 16S rDNASequenzen ermittelt. Es konnten 67 Haplotypen unterschieden werden. Die Haplotypen zeigen eine große genetische Diversität innerhalb der Formengruppe (bis zu 8.2% paarweise Sequenzdivergenz). Es lassen sich neun genetisch stark divergente Linien unterscheiden. In einer Population konnten dynamische dinukleotide Mikrosatelliten in der mtDNASequenz nachgewiesen werden, die eine Längenvariation von vier bis achtfachem Grundmuster aufweisen. Als wahr scheinlicher Mechanismus für diese Längenvariation wird "slippedstrandmispairing" angenommen. Mit Hilfe von nukleären RAPDMarkern wurde die genetische Trennung der mitochon drialen Linien bei syntop vorkommenden Linien auch auf nukleärer Ebene nachgewiesen. Die Formengruppe A. fluviatilis setzt sich somit aus einem Komplex reproduktiv isolierter Linien zusammen. Im Zusammenhang mit der bereits nachgewiesenen allotetraploiden Konstitution zumindest einer Linie und der resultierenden hohen Selbstbefruchtungsrate sind sowohl sympatrische als auch allopatrische Diversifizierungsereignisse für die Differenzierung der Linien verantwortlich. Drei der neun genetischen Linien sind geographisch weitverbreitet und kommen zum Teil syntop vor. Phylogeographische Analysen anhand von "nested clades" zeigten, daß isolation by distance zwar das Grundmuster für die Verbreitung von A. fluviatilis darstellt, daß dieses aber durch Expansionsereignisse, die die Besiedlung über weite Distanzen einschließen, überlagert sein kann. Zeitliche Abschätzungen ergaben für die Formengruppe A. fluviatilis ein Alter von mindestens 20 Millionen Jahren. Die rezent vorkommenden Linien sind schätzungsweise zwischen 8 und 14 Millionen Jahren alt. Für die phylogenetischen Untersuchungen innerhalb der Basommatophora wurde die 16S rDNA von weiteren Gattungen sequenziert. Die resultierende molekulare Phylogenie belegt die monophyletische Entstehung der Formengruppe A. fluviatilis sowie eine gemeinsame Abstammung der Gattungen Ferrissia und Ancylus. Die Familie Ancylidae bildet eine Schwestergruppe zur Familie Planorbidae und läßt sich somit nicht aus dieser ableiten. Die Gattung Burnupia zeigt sich als nahe verwandt zur Gattung Acroloxus (Familie Acroloxidae) und gehört somit nicht, wie bisher angenommen, zu den Ancylidae.
Here I analyse 23 populations of D. galeata, a large-lake cladoceran, distributed mainly across the Palaearctic. I detected high levels of clonal diversity and population differentiation using variation at six microsatellite loci across Europe. Most populations were characterised by deviations from H-W equilibrium and significant heterozygote deficiencies. Observed heterozygote deficiencies might be a consequence of simultaneous hatching of individuals produced during different times of the year or of the coexistence of ecologically and genetically differentiated subpopulations. A significant isolation by distance was only found over large geographic distances (> 700 km). This pattern is mainly due to the high genetic differentiation among neighbouring populations. My results suggest that historic populations of Daphnia were once interconnected by gene flow but current populations are now largely isolated. Thus local ecological conditions which determine the level of biparental sexual reproduction and local adaptation are the main factors mediating population structure of D. galeata. The population genetic structure and diversity in D. galeata was investigated at a European scale using six microsatellite loci and 12S rDNA sequence data to infer and compare historical and contemporary patterns of gene flow. D. galeata has the potential for long-distance dispersal via ephippial resting eggs by wind and other dispersing vectors (waterfowl), but shows in general strong population differentiation even among neighbouring populations. A total of 427 individuals were analysed for microsatellite and 85 individuals for mitochondrial (mtDNA) sequence data from 12 populations across Europe. I detected genetic differentiation among populations across Europe and locations within sampling regions for both genetic marker systems (average values: mtDNA FST = 0.574; microsatellite FST = 0.389), resulting in a lack of isolation by distance. Furthermore, several microsatellite alleles and one haplotype were shared across populations. Partitioning of molecular variance was inconsistant for both marker systems. Microsatellite variation was higher within than among populations, whereas mtDNA data yielded an inverse pattern. Relative high levels of nuclear DNA diversity were found across Europe. The amount of mitochondrial diversity was low in Spain, Hungary and Denmark. Gene flow analysis at a European scale did not reveal typical pattern of population recolonization in the light of postglacial colonization hypotheses. Populations, which recently experienced an expansion or population-bottleneck were observed both in middle and northern Europe. Since these populations revealed high genetic diversity in both marker systems, I suggest these areas to represent postglacial zones of secondary contact among divergent lineages of D. galeata. In order to reveal the relationship between population genetic structure of D. galeata and the relative contribution of environmental factors, I used a statistical framework based on canonical correspondence analysis. Although I detected no single ecological gradient mediating the genetic differentiation in either lake regions, it is noteworthy that the same ecological factors were significantly correlated with intra- and interspecific genetic variation of D. galeata. For example, I found a relationship between genetic variation of D. galeata and differentiation with higher and lower trophic levels (phytoplankton, submerged macrophytes and fish) and a relationship between clonal variation and species diversity within Cladocera. Variance partitioning had only a minor contribution of each environmental category (abiotic, biomass/density and diversity) to genetic diversity of D. galeata, while the largest proportion of variation was explained by shared components. My work illustrates the important role of ecological differentiation and adaptation in structuring genetic variation, and it highlights the need for approaches incorporating a landscape context for population divergence.
Zur Evolution der Hirnmorphologie und Anpassungen an Extremhabitate im Taxon Poecilia (Teleostei)
(2020)
Diese Dissertation befasst sich mit den Auswirkungen kontrastierender Umweltbedingungen auf die Gehirnmorphologie von neotropischen Fischen der Gattung Poecilia, welche unterschiedlichen abiotischen sowie biotischen Stressoren ausgesetzt sind. Da das Gehirn der Teleostei ein energetisch kostspieliges Organ und viel plastischer ist als z. B. bei Säugetieren, stellt sich die Frage, wie die Gehirnanatomie durch divergierende ökologische Faktoren in verschiedenen Umgebungen geformt wird, die ´extreme´, ´ressourcenbeschränkte und günstige´ Umgebungen repräsentieren. Zur Beantwortung dieser Frage wurden intraspezifische Studien an freilebenden und Laborindividuen von Poecilia-Arten durchgeführt, um die evolutionäre und ökologische Formgebung des Gehirns besser verstehen zu lernen. Im ersten Teil der Arbeit wurden Gehirnvolumina verglichen zwischen reproduktiv isolierten Populationen des neotropischen Fisches Poecilia mexicana (Ntotal = 95), die in Dunkelheit leben (Cueva Luna Azufre), in einem nahegelegenen Oberflächenhabitat (El Azufre), welcher giftigen Schwefelwasserstoff enthält und einer Kombination aus beiden Stressoren Dunkelheit und H2S (Cueva del Azufre). In einer zweiten Studie wurde auf anatomische („konvergente“) Veränderungen im Teleost-Gehirn entlang eines natürlichen Gradienten von Sulfidkonzentrationen getestet. Hierfür wurden Gehirne (Ntotal = 100) von P. mexicana verglichen, die in drei Flusssystemen im Süden Mexikos unabhängig voneinander eine erhöhte Toleranz gegenüber Schwefelwasserstoff (H2S) entwickelt haben. Dazu gehörten eine phylogenetisch alte H2S-adaptierte Form (P. sulphuraria) und zwei P. mexicana Formen, welche frühere Stufen der Anpassung an H2S darstellen. Zur Überprüfung des Einflusses anderer abiotischer und biotischer Faktoren auf die Morphologie der Gehirnregionen wurde eine weitere Studie durchgeführt. Hierbei wurden die phänotypischen Variationen der Gehirnregionen und der Körpermorphologie von Poecilia vivipara-Populationen (Ntotal = 211) aus Lagunen des Restinga de Jurubatiba Nationalpark untersucht, die sich in abiotischen Umgebungsbedingungen, insbesondere in Salzgehalt, Wassertransparenz, Phosphat und Nitrat sowie biotischen Faktoren wie Prädatorendichte unterschieden. Die erste Studie zeigte lebensraumabhängige Unterschiede bei freilebenden Fischen. Bei Fischen, die in Dunkelheit ohne H2S (LA) oder in Oberflächenhabitaten mit H2S lebten, wurden vergrößerte telenzephale Lappen, kleinere Augen und optische Tekta gefunden. Fische aus der sulfidischen Höhle (CA) zeigten zusätzlich vergrößerte Corpus cerebelli. Der Vergleich mit den Gehirnen von Labor aufgezogenen weiblichen Fischen (Ntotal = 25) zeigt eine allgemeine Verringerung der Gehirngröße sowie eine geringe Abweichung der Gehirngröße zwischen Labor aufgezogenen und freilebenden Fischen. Auch in der zweiten Studie zeigten alle in H2S-haltigen Lebensräumen lebenden Fische kleinere Augen, ein kleineres optisches Tektum und ein kleineres Gehirnvolumen, jedoch größere Corpus cerebelli und Hypothalamusvolumen als Fische aus nicht-sulfidischen Lebensräumen. Flusssystem-spezifische Effekte wurden für die telenzephalen Lappen, das gesamte Gehirn und die Augengröße festgestellt, da die Geschlechter je nach Quelle des Flusssystems unterschiedlich auf das Vorhandensein von H2S reagierten. Die dritte Studie zeigt auch, dass andere Umwelteinflüsse bemerkenswerte Verschiebungen im Gehirn und in den Gehirnregionen verursachen können. Fische, die im Süßwasser leben, zeigten eine verringerte Gesamthirngröße, telenzephale Lappen, Corpus cerebelli und Hypothalamusvolumen. Darüber hinaus zeigten Fische aus Salzwasserlagunen (hypersalin), ein verringertes Volumen des optischen Tektum, während telenzephale Lappen, Corpus cerebelli und Hypothalamusvolumen im Vergleich zu Süßwasserfischen vergrößert waren. Im Brackwasser lebende Fische wiesen im Vergleich zu Süß- und Salzwasserfischen die größten Gehirnregion-Volumen auf. Darüber hinaus zeigten die Ergebnisse über die Lagunen hinweg auch Unterschiede in der Morphologie der Kopf- und Augendurchmesser. Bei Augengröße, Kopfgröße, optischem Tektum Volumen, Hypothalamusvolumen und dem Gesamthirnvolumen wurde ein sexueller Dimorphismus beobachtet. Die dargestellten Ergebnisse verdeutlichen, dass die gefundenen Muster nahezu mit denen von H2S-Fischen identisch sind. Die ausgeprägten Unterschiede in den Hirnregionen zwischen freilebenden Fischen können als Teil der Mosaikentwicklung interpretiert werden. Die Ergebnisse der Laborpopulation zeigen jedoch eine hohe phänotypische Plastizität. Diese Studie unterstreicht damit die Bedeutung der Kombination der Untersuchung von freilebenden mit im Labor lebenden Individuen zur Beantwortung von Fragen der Gehirnentwicklung. Kleinere Augen und ein kleineres optisches Tektum, aber größere telenzephale Lappen wurden auch bei Fischen aus einem sulfidischen Oberflächenhabitat in der Nähe einer der Höhlen gefunden und sind den Ergebnissen zufolge das Resultat begrenzter Sehkraft in trüben sulfidischen Lebensräumen.
...
Das Ziel der vorliegenden Studie war die vergleichende morphometrische Untersuchung der Molarenmorphologie rezenter Hominoidea. Im Mittelpunkt der Fragestellung stand die dreidimensionale Analyse des hominoiden Facettenmusters, neben dem quantitativen Vergleich der Relieftopographie und der konstruktiven Veränderung der Kauflächen mit zunehmender Abnutzung, im Hinblick auf die funktionellen Möglichkeiten zur effektiven Nahrungsaufschließung.
Die qualitative Analyse umfasst, neben der dentalmorphologischen Beschreibung, die digitale Fotodokumentation und die Klassifizierung der verschieden weit abgenutzten Molaren in vergleichende Abkauungsgrade.
Die quantitative Auswertung der virtuellen Zahnmodelle schließt die Vermessung der größten Länge, Breite und Höhe, die Berechnung des prozentualen Dentin- und Facettenflächenanteils, des Relief-Index sowie die Neigung und Orientierung der antagonistischen Facetten des Oberund Unterkiefers mit ein. Die Berechnung der korrespondierenden Facettenwinkel in einem einheitlichen Koordinatensystem erlaubt die Kalibrierung der okkludierenden Flächenareale und die Berechnung dreidimensionaler Richtungsvektoren, die die buccale und linguale Mandibelbewegung widerspiegeln. Je nach der Art der Verzahnung der in Okklusion tretenden Höckerflanken lassen sich aus dem räumlichen Zusammenspiel der Funktionselemente quetschende und scherende Komponenten differenzieren.
Die Ergebnisse, die am Rezentmaterial (244 Einzelzähne) gewonnen wurden, sind auf 16 ausgewählte Einzelzähne aus Sangiran und Punung (Java, Indonesien) der Sammlung VON KOENIGSWALD der Abteilung Paläoanthropologie und Quartärpaläontologie des Forschungsinstituts Senckenberg, übertragen worden.
Entsprechend der zu Anfang aufgeworfenen Fragestellung konnte ein für jede Gattung charakteristisches Reliefmuster der Okklusalfläche und dessen Veränderung im Laufe der Abkauung etabliert werden. Infolge des Abschleifens der konvexen Höckerspitzen kommt es zu einer unterschiedlich schnellen und intensiven Reliefverflachung. Die Reliefunterschiede zwischen den Gattungen bleiben im Laufe der Abnutzung erhalten. Gorilla besitzt das am stärksten ausgeprägte okklusale Relief und zeigt die intensivste Abnutzung der Kauflächen und grenzt sich von Pan und Hylobates und insbesondere von Pongo deutlich ab. Pongo besitzt das flachste okklusale Relief und zeigt eine geringere Abnutzung der Kauflächen.
Auf der Grundlage der rekonstruierten Facettenwinkel lässt sich das homologe Facettengrundmuster der Hominoidea weiter differenzieren. Alle Gattungen stimmen in der Position der Facettenareale weitgehend überein. Dieses homologe Facettenmuster resultiert aus der relativ zyklischen Kaubewegung. Die Relieftopographie und Profilierung der Kaufläche sind für die individuelle Bewegungsführung entscheident. Es konnte gezeigt werden, dass aus der unterschiedlichen Steilheit der Zahn-zu-Zahn-Kontakte, unter Berücksichtigung der auf der dreidimensionalen Orientierung der Facetten basierenden Bewegungsbahnen, verschiedene Funktionalitäten resultieren. Durch die Unterschiede in der räumlichen Facettenausdehnung prägt sich ein gattungsspezifisches Grundmusters aus, welches direkt mit der Funktion korreliert und die hohe Effizienz bei der unterschiedlichen Nahrungsaufbereitung bewirkt. Jene quantitativ erfassten Flächen und Bewegungen können funktionell interpretiert werden und stellen eine eindeutige Verbindung zu den in der Literatur aufgeführten Ernährungsweisen der Hominoidea her. Die Kauflächen der vier rezenten Gattungen können unter unterschiedlichen Nutzungsbedingungen im Hinblick auf eine spezifische Ernährungsweise verstanden werden.
Es wurde gezeigt, dass die dreidimensionale Ausrichtung homologer Facetten zu unterschiedlicher Funktionalität führen kann und demzufolge über die zweidimensionale Analyse hinausgeht.
Gorilla nutzt die Vielzahl steiler und kleiner Kontaktflächen zum Zerschneiden der überwiegenden faserigen Nahrungsbestandteile durch hohe Scherkräfte. Aufgrund der stark profilierten Kaufläche folgt die Bewegungsführung restriktiv dem Furchungsverlauf.
Pongo besitzt infolge der Konstruktion der Kaufläche große Kontaktareale, die in flachem Winkel aufeinandertreffen und so ein effizientes Quetschen oder Zermahlen der überwiegenden Früchtenahrung erlauben. Das flache Kauflächenprofil ermöglicht einen größeren Spielraum in der Bewegungsführung.
Pan und Hylobates besitzen ein Repertoire aus schneidenden und quetschenden Funktionselementen und somit einen geringeren Spezialisierungsgrad.
Die Beurteilung der Konstruktion und Funktion der pleistozänen Einzelmolaren im Vergleich mit den erarbeiteten Rezentmodellen ergibt eine Ähnlichkeit mit dem modernen Pongo. Die flache Relieftopographie, die geringe Steilheit der Winkel und die zusätzlichen Schmelzrunzelungen lassen auf ein Quetschen der Nahrung schließen. Eine phylogenetische Aussage zur Differenzierung zwischen Homo oder Pongo konnte aufgrund der kleinen und als exemplarisch anzusehenden Zahl fossilen Materials nicht eindeutig erfolgen.
Amphibians have existed on the planet for over 300 million years and are today one of the most diverse vertebrate classes in the world with over 7000 known species and still many more to be discovered. However, several studies assume that approximately one third of the world´s known living amphibians are directly threatened with extinction, making it the most endangered vertebrate class. In relation to the relatively small land mass that is occupied by the state of Panama, it supports one of the most diverse amphibian faunas. However, in many cases the ecological role of single species in a wider context and their habitat preferences are still poorly understood and subject to ongoing research. Modern taxonomic approaches in other tropical regions have shown that former assumptions of amphibian diversity were distinct underestimations of the actual species diversity; a situation that is probably also true for Panama. Concurrently, the collection of amphibian diversity data and the description of new species is a race against time. The amphibian fauna of the world and that of Panama in particular, has suffered from an unprecedented loss of diversity over the last 30 years. The reasons are manifold and include destruction, alteration, and fragmentation of their natural habitats as the main causes, but also the deadly amphibian disease chytridiomycosis caused by the fungal pathogen Batrachochytrium dendrobatidis (Bd). In Panama and Costa Rica, this Emerging Infectious Disease (EID) spread in a wave-like manner from west to east causing mass die-offs and reduced amphibian diversity even in well-preserved habitats. The disease has primarily affected stream-associated highland species. The last large-scale evaluation of the conservation status of Panama´s amphibians through the IUCN Red List of Threatened Species in 2004 concluded that approximately 30% of the known species are acutely threatened with extinction. Furthermore, around 17% of the amphibian species that have been known back then lacked adequate data to be assessed. In view of Panama´s already overwhelming amphibian diversity, as well as the variety of habitats and the large number of sites that have not been examined with regard to amphibians before, I started this study with the conviction that the inventory of Panama´s amphibian diversity is far from being completed. Furthermore, when I started this study, it was uncertain if there would be any surviving amphibian species in areas where chytridiomycosis had emerged. The loss of whole amphibian communities in upland western Panama following Bd arrival led to a shift of amphibian research to lowland sites in central and eastern Panama aiming primarily on pathogen arrival and the documentation of epizootic outbreak and subsequent population decline. The situation of amphibian communities in areas post-decline was therefore largely unknown. Accordingly, the main goals of my study were to add to the taxonomic inventory of amphibians in Panama and to assess the situation of amphibian populations in habitats where chytrid-driven declines have been observed. To address these tasks I conducted fieldwork in western Panama with a focus on mountainous elevations between 1000 and 3475 m asl. Additionally, I visited different lowland sites between sea level and 1000 m asl to collect comparative material. In the period between 2008 and 2013, I conducted five collection trips to Panama that add up to a total of approximately 13 months in the field. I have sampled nine regions in western Panama and collected 767 specimens together with student collaborators, 531 of which were collected under my personal field number. Additional data obtained from those specimens include 68 male anuran call recordings, 102 standardized color descriptions of specimens in life, and 259 tissue samples that to date yielded 185 16S mtDNA sequences. This comprises the most comprehensive data set for amphibians of Panama and the first large-scale DNA barcoding approach for western Panama to date. After a preliminary DNA barcoding and subsequent comparative examination of morphological und bioacoustic data of all specimens collected, the number of taxonomic problems that needed to be addressed was higher than I previously anticipated. For most genetic lineages deeper taxonomic analyses were required to reach conclusive results. A selection had to be made with which lineages to proceed in the analyses, in view of the substantial financial and time expenditure that would be needed for a complete taxonomic revision. Therefore, I chose to run deeper analyses on one genus from each of the three amphibian orders in Panama. The genera selection depended largely on the availability of sufficient material and the scientific relevance of the respective genus.
I selected the genus Diasporus from the order Anura. These small frogs are omnipresent in many habitats and thus relatively easy to find. In addition, the genus is underrepresented in taxonomic studies. This is the first taxonomic study on the genus Diasporus to include a molecular phylogeny and the first comparison of advertisement calls between several populations from western Panama. In total, I collected 67 Diasporus specimens throughout western Panama and compared them morphologically with 49 additional specimens from Central America in collections, including the primary types of D. diasporus and D. hylaeformis. Additional comparative data were taken from literature. The DNA barcoding analysis of a fragment of the 16S rRNA gene included 43 own sequences that were complemented with 15 relevant GenBank sequences. In addition, I compared the advertisement calls of 26 male individuals among each other and with call descriptions from the literature. The DNA barcoding approach revealed several unnamed genetic lineages, but in some cases also resulted in the lumping of morphologically and bioacoustically distinct specimens. Generally, the morphological examination of the collected material revealed almost no specific characters that could be used to distinguish between genetic lineages. However, it was possible to identify species using a combination of several morphological characteristics. Which ones are relevant in the individual case depends on the respective species. My extensive collection of call recordings made it possible to test for the first time the intraspecific call variation of D. hylaeformis in dependency of various parameters. This analysis showed that the dominant frequency depends significantly on the body size of the calling male; the smaller the calling male, the higher the frequency of the call. A similar relationship was observed between the call rate and temperature: the lower the temperature during calling, the lower the call rate. I suppose that these general patterns, which have already been observed in other anuran genera, are also true in other Diasporus species that could not be tested in this study. Taking into account the intraspecific variation of Diasporus advertisement calls, I consider comparative call analyses to be the best way to distinguish between species. This is especially true in syntopic species. Integration of the three lines of evidence (i.e., morphology, DNA barcoding, and bioacoustics) led to the identification of four new species, two of which (i.e., D. citrinobapheus and D. igneus) colleagues and I have already formally described.
I conducted an integrative taxonomic analysis of the western Panamanian representatives of the genus Bolitoglossa from the order Caudata, the larger of the two Panamanian salamander genera. Bolitoglossa is very species-rich with a centre of diversification in the high mountains of Costa Rica and western Panama. I collected 53 Bolitoglossa specimens and compared them to twelve specimens in collection, including the holotype and one paratype of B. gomezi. The dataset was complemented with information from the literature. Among the sampled specimens were two species considered to be endangered that have not been collected or observed for several decades; B. magnifica has not been seen for 34 years and B. anthracina has not been seen for 22 years. Further, I collected salamanders at several new locations. To date, my 16S mtDNA barcoding analysis represents the densest taxon sampling for Panamanian Bolitoglossa composed of 21 own sequences that were combined in the final alignment with 47 GenBank sequences. Even though the molecular phylogeny is based only on a single marker, the received trees largely coincide with previous studies and the nodes received high statistical support. In these trees, I retrieve all previously defined subgenera and species groups. On the basis of this molecular phylogeny, I placed B. anthracina, here sequenced for the first time, in the B. subpalmata species group. Due to the fact that B. anthracina is a large and dark colored species it had previously been placed by implication in the B. schizodactyla species group along with other large black salamanders of the B. nigrescens species complex. Moreover, I found deep divergent genetic lineages among geographically separated populations of B. minutula. However, until now there were no additional morphological characteristics detectable to distinguish between these lineages. Additionally, my colleagues and I described a new deep divergent lineage in the B. robinsoni species group as B. jugivagans, a species new to science. In contrast, I found only minor genetic differences between specimens of B. sombra and B. nigrescens. After combining morphometric data and tooth counts from literature of both species with additional data from specimens of B. sombra that I collected near the type locality, the distinguishing features blurred. In particular, including much larger specimens of B. sombra, not yet known at the time of its description, showed that the tooth count difference is dependent on the size and age of the specimen examined. Larger specimens have more maxillary and vomerine teeth. Based on this evidence I regard B. sombra as a junior synonym of B. nigrescens. Further, I revised the Panamanian distribution of the two relatively common lowland salamanders, B. colonnea and B. lignicolor. Besides filling the gaps in the fragmentary known distributions of these species, I assessed the molecular and morphological variation of both species among populations in Panama. While there was little variation in B. lignicolor, I found divergent genetic lineages among geographically distinct populations of B. colonnea that require further taxonomic examination.
Caecilians (order Gymnophiona) are among the least investigated terrestrial vertebrates. After I received a first specimen of the predominantly South American genus Oscaecilia (family Caeciliidae) in western Panama, I started to work more extensively on the taxonomy of Caeciliidae in Central America. The specimens from western Panama were not readily assignable to a single described species, but shared characters with O. elongata and O. osae. While O. osae was only known from the holotype, the type material of O. elongata was destroyed during World War II. On the basis of the original description, the unique feature in O. elongata within Oscaecilia is the absence of subdermal scales in the posterior part of the body. In a referred specimen of O. elongata mentioned in the original description from eastern Panama, this characteristic cannot be examined as it consists of head and neck only. Therefore, I used non-destructive high-resolution, synchrotron-based X-ray micro CT imaging (HRμCT) to examine cranial characters in the specimens in question and took normal radiographs to count vertebrae and to make subdermal scales visible. I found that the fragmented specimen from eastern Panama likely belongs to the well-sampled species O. ochrocephala and has not much in common with O. osae or the specimens from western Panama. Contrarily, O. osae and the specimens from western Panama share many morphological characters, but also show some differences. Genetic barcoding revealed that both species are close relatives, but the genetic distance could not be finally resolved, because 16S sequences obtained from blood samples of living O. osae were of poor quality. Thus, I compare the Oscaecilia from western Panama to O. osae in this study, but postpone a taxonomic decision until further material becomes available. Further, I designate O. elongata a nomen dubium, because the type material is lost, the type locality is not defined in more detail than “Panama”, and the original description does not allow for a definite assignment. Since previous molecular studies only considered O. ochrocephala, the monophyly of Oscaecilia was never tested before. So far, the genus Oscaecilia is based largely on a single cranial character, the eyes covered with bone. Here, I combined two 16S mtDNA sequences of O. osae from Costa Rica and two sequences from O. sp. from western Panama with two sequences of O. ochrocephala and ten sequences of four species of the genus Caecilia, the sister genus of Oscaecilia. The resulted phylogeny contains two well-supported clades, one clade containing two species of Caecilia, one from Panama and one from western Ecuador and all species of Oscaecilia tested. The other clade consists of two species of Caecilia from the Amazon basin. I therefore assume that the split in both clades is due to the rise of the Andes, what led to today’s cis-trans-Andean distribution of the two clades. For now, to restore monophyly, I suggest to place Oscaecilia within the synonymy of Caecilia until more taxa have been tested. When assessing the conservation status of the amphibian species in mountainous western Panama, I first compiled a list of known species that I potentially could have found during my fieldwork. Using the IUCN categories, I analyzed how many of the endangered species I actually found and how these are distributed over families and species groups. Surprisingly, my rediscoveries of lost species were not equally distributed among the four families that comprise most endangered amphibian species (i.e., Bufonidae, Craugastoridae, Hylidae, and Plethodontidae). While I discovered ten of eleven endangered hylids and six of nine endangered plethodontids, I found only one of four endangered bufonids and none of the nine endangered craugastorids. I assume that the secretive living plethodontids, for which no Bd related declines have been documented, were just overlooked in the past decades. In contrast, I propose that hylids, in which Bd related population decline is well documented, developed distinct evolutionary solutions permitting coexistence with the pathogen. The situation is obviously different in bufonids and craugastorids, where I found no signs of population recoveries at present. So far, the only surviving populations of species from these families exist in climatic or physiographic niches that have probably shielded them from Bd. My data confirm the current view that the risk for naïve amphibian populations to decline during Bd epizootics is predicted by ecological traits (e.g., aquatic index, vertical distribution) and not dependent on taxonomic affiliation. However, I propose that only certain amphibian families (e.g., hylids and centrolenids) have the ability to acquire immunity solutions to coexist with the pathogen during enzootic stages. This is a very new perspective on the worst infectious disease in amphibians worldwide, allowing for new research approaches to understand the host-pathogen dynamics. Moreover, I examined where the share of surviving endangered amphibian species is particularly high in mountainous western Panama. As was to be expected, most of the endangered species are found within the boundaries of protected areas. One exception is the unprotected Cerro Colorado region in the Comarca Ngöbe-Buglé that provides habitat for a wide variety of endangered and undiscovered amphibian species. Nonetheless, planned open pit mining would destroy the forests in a large part of the area. This demonstrates once again that human activities are the biggest threat to amphibians in Panama and elsewhere.
The documentation of life on Earth, that is, the inventorization of nature and the naming and classification of organisms found therein, is a major task for biologists today and a fundamental precondition for nature conservation efforts. This study aimed at contributing to the inventory of amphibians and reptiles in selected, previously understudied ecoregions of Bolivia. I strove to document diversity patterns and seek possible ecological and historical reasons for these patterns. Special attention was paid to the Chiquitano Region situated in the eastern lowlands of Bolivia in a climatic transition zone between the humid evergreen Amazon Forests and the deciduous thorn-scrub vegetation of the Gran Chaco. In congruence with its location in the transition zone, the Chiquitano Region displays a mosaic of habitats: The vegetation is dominated by the endemic Chiquitano Dry Forest, which is probably the largest extant patch of Seasonal Dry Tropical Forest, with enclaves of savanna, the western outliers of the Cerrado biome of central Brazil. Taxonomic revisions: The taxonomic data in this study are used as a tool to measure biodiversity, to assess biogeographic relationships, and to evaluate conservation needs. Since all is predicated on the taxonomic decisions made, an adequate taxonomy is essential, and taxonomy can be regarded as the foundation of this study. The methodology encompassed a variety of herpetological field techniques, such as different survey methods, preparation and documentation of voucher specimens, recording of frog calls, and herpetological laboratory techniques, such as morphology, molecular procedures with mtDNA, phylogenetic analyses, and bioacoustic analysis and descriptions of frog calls. A total of 1251 specimens belonging to 200 species were obtained during this study, including 87 amphibian and 123 reptile species. This constitutes about 36% of the herpetofauna currently known for Bolivia, about 34% of the amphibians currently known for Bolivia and about 40% of the reptiles, respectively. In the course of this study, a new species of frog was described from the study site Caparu in the eastern lowlands of Bolivia; this species, Hydrolaetare caparu Jansen, Gonzales & G. Köhler 2007, differs from the other two congeners in external morphology (e.g., lateral fringes and relative length of fingers, size of palmar tubercle, webbing of toes, and colouration) and advertisement call. Two new colubrid snake species were also described from the study site San Sebastián. Thus far, both are known only from the Chiquitano Region, Provincia Ñuflo de Chávez. Phalotris sansebastiani Jansen & G. Köhler 2008 differs from all the other species in the genus in having a triangular projection of the red snout colouration reaching onto the parietals. Xenopholis werdingorum Jansen, Gonzales & G. Köhler 2009 can be identified as a member of the genus Xenopholis by its vertebral morphology. It differs from the other two species of Xenopholis in having a unique uniform dorsal colour pattern, and from X. scalaris in having two prefrontals and a narrow septum within the neural spine and perpendicular to its long axis as evident in the x-ray images. A review of a small collection of pitvipers from different lowland localities and from the Inter-Andean dry valleys of the region of Pampagrande revealed one new species of Bothrops and one of Bothrocophias (both to be formally described elsewhere). The two pitviper species differ morphologically and genetically from their congeners. The results of a brief review of a small collection of frogs of the genus Scinax (Anura: Hylidae) from different localities in the lowlands, together with analyses of their bioacoustics, suggest an unknown cryptic diversity in Bolivian species of Scinax cf. fuscomarginatus and allies. However, further studies are necessary to clarify the taxonomic status of these populations. In addition, this study provides new data on the morphology (e.g., pholidosis) of snakes, many of them previously known only from few museum specimens. Keys to the Bolivian lizard species of Cercosaura and the Bolivian snake species of Chironius, Clelia, Liophis, Lystrophis, Phalotris, and Xenodon are presented here for the first time. New information on distribution includes many range extensions of amphibian and reptile species, such as five new country records (one frog species, four snake species) and six new departmental records (two frog species, four snake species). Observations on ecology and natural history: Several observations on ecology and natural history were made during field work. Visual signaling, an aspect of territorial behavior that was already known for several species of the genus Phyllomedusa, could be described for the first time for Phyllomedusa boliviana (Jansen & J. Köhler 2007). Furthermore, during audio surveys of an anuran community at the study site San Sebastián from 2005 to 2007, a decline of certain amphibian populations was observed in the rainy season 2006/2007 (Jansen et al., in press). This is possibly related to an extreme drought in the dry season of 2006 where 158 consecutive days without rainfall were recorded. In addition, a new method for measuring intensity of anuran choruses by means of a continuous sound pressure metre was developed (Jansen 2009). The method was suitable to detect calling phenology (during one night), as well as differences in calling activity (between two nights). Biodiversity and biogeographical relationships: Species lists were compiled at the six study sites Pampagrande, Los Volcanes, San Sebastián, Caparú, El Espinal und El Corbalan. The total amphibian and reptile species numbers observed ranged from 37 to 101 with the highest species numbers in San Sebastián (101) and Caparú (89) and the lowest in Los Volcanes (37) and El Espinal (41). A preliminary species list of the herpetofauna of the Chiquitano Region was presented, including 60 amphibian and 84 reptile species. The majority of the amphibians of the Chiquitano Region are classified predominantly as inhabitants of open formations (41 species, 68.3%). Interestingly, even the majority of species recorded from the Chiquitano Dry Forest (32 species) are usually associated with open formations (22 species, 66.7%), followed by the number of species associated with open and forest formations (8 species, 24.4%). Only two of the observed species (6.0%) are predominant forest dwellers. The amphibian assemblage of the Chiquitano Region is most similar in composition to that of the Cerrado biome: 46 species (76.7%) occur in the Cerrado as well, and three species are regarded as Cerrado endemics (5.0%). The Chiquitano Region shares considerably fewer amphibian species with the other biomes (Amazon: 22 species, 36.7%; Gran Chaco: 13 species, 21.7%; Caatinga: 16 species, 26.7%). The reptile assemblage also has significant affinities to the Cerrado, which can be seen in the high proportion of reptile species distributed in that biome (68 species; 81.0%). Affinities to the other biomes are as follows: Amazon (48 species, 57.1%), Chaco (37 species, 40.1%), and Caatinga (30 species, 35.7%). When arranged in mutually exclusive biome categories, reptiles and amphibians showed similar patterns so that the majority of both amphibians and reptiles of the Chiquitano Region can be regarded as widespread. The high proportion of reptile species probably endemic to this region (5 species, 6.0%) is remarkable (i.e. Tropidurus xanthochilus, Apostolepis phillipsi, Phalotris sansebastiani, Xenopholis werdingorum, and Micrurus diana). In an analysis of the biodiversity patterns and biogeographical relationships of the herpetofauna of the study sites, these sites were compared with literature data from 37 localities and included in a presence/absence matrix with a total of 657 amphibian and reptile species in the surrounding South American biomes Amazon, Cerrado and Gran Chaco. The biogeographic relationships between these sites were evaluated using the Coefficient of Biogeographic Resemblance (CBR), cluster analysis, and multidimensional scaling (MDS) of sites. The analyses were first conducted on amphibians and reptiles combined, and than group-specific each for amphibians, reptiles, lizards, and snakes, separately. A “bias-reduced analysis” was developed for a better understanding of the affinities of the amphibians. In this analysis, e.g., the distinct habitat types of the Chiquitano Region, the Chiquitano Dry Forest and the Cerrado were taken into account. Analyses of the biodiversity patterns revealed that the sites in the Amazon comprise highest species numbers, as expected, followed successively by the sites in the Cerrado biome and sites in-between the two biomes. Within the eastern lowlands of Bolivia, the Chiquitano Region is the most rich in species. Comparing it with the other South American sites, the Chiquitano Region has a surprisingly high alpha diversity, especially in amphibians. The microgeographic variation in species composition (beta diversity) in the Chiquitano Region is also remarkably high and obviously related to the mosaic character of the vegetation and habitats. However, the bias-reduced analysis revealed that the amphibian fauna of the open areas and savannas at Hacienda San Sebastián (with 36 species in the Cerrado and pastureland) was one of the most species-rich savanna sites known for amphibians in South America. Considering that the Hacienda San Sebastián site is only ca. 3300 ha (= 1.29 amphibian species per km2), this outcome is particularly suprising. The results of the analyses of the biogeographical relationships suggest that the herpetofauna of Bolivia’s lowlands, including the Beni, the Pantanal and the Chiquitano Region, is as distinct from the herpetofauna of the Gran Chaco, Amazon, and Cerrado as these biomes are from each other. The Chiquitano herpetofauna in particular represents a unique and well-defined herpetofaunal assemblage when compared to all surrounding localities and biomes. This is supported by high CBR-values, findings from the cluster analysis, as well as a clear separation of the Chiquitano sites in the MDS. Biogeographic relations exist in all the surrounding biomes, but are strongest to Cerrado, followed by the Amazon. This study strongly suggests that the Chiquitano herpetofauna is composite and has multiple affinities. This is congruent with a well-defined Chiquitano flora, avifauna and mammalian fauna, suggesting a similar history. The bias-reduced analysis revealed a more detailed picture of the biogeographic relations of the Chiquitano Region, especially the Chiquitano Dry Forest. I argue here that the Chiquitano Dry Forest herpetofauna is a “young”, and “former savanna herpetofauna”. Whereas the Chiquitano Dry Forest is rather poor in amphibian and reptile species, and endemics are lacking from this forest type, the isolated Cerrado enclaves are especially diverse in species and probably contain locally endemic species, such as Phalotris sansebastiani and Xenopholis werdingorum. The colonization of the young Chiquitano Dry Forest may have taken place from savannas by mainly open area species, and only briefly through the Amazon. The results emphasise the importance of bias-reduction in studies of biogeography, e.g., by using group-specific analyses or by taking into account criterias as area size and heterogeneity of compared sites. The different biogeographic patterns of reptiles and amphibians of the Andean valleys indicate a different history of these two groups. In regard to reptiles, dispersals and withdrawals into the valleys in warm humid and dry cool periods in the Pleistocene seem likely, supported by a relation between the valleys and the dry lowland (e.g., Chaco). However, it is more plausible that, during these climatic fluctuations, amphibians migrated to adjacent, more humid regions, such as Yungas. The study verified the known patterns of sister-species pairs in the Inter-Andean Dry Forest and the lowlands. Additionally, pairs of populations with slight differences in morphology were found in the valleys and in the lowlands (Cercosaura parkeri and Xenodon rhapdocephalus). Further studies must test the taxonomic status of these populations. The discovery of new species of Bothrops and Bothrocophias from the Andean valleys has several implications, and possible reasons for the high endemism in the dry valleys are discussed. Conservation and outlook: The high local alpha and beta diversity of the Chiquitano herpetofauna shows that this is a region of complex faunal interaction, which reflects the present heterogeneity of the region, but which is possibly also related to a complex geological and environmental history. The Chiquitano Region can be assessed as a region of distinct regional herpetofaunal diversity charaterised by small scale diversity patterns. It therefore merits recognition as a unique ecoregion, and conservation effort should be increased. Further research is necessary to solve the taxonomic problems addressed in this study. Moreover, future work should be directed towards the development and institution of longterm monitoring programs to evaluate the effects of climate change and changes in land-use on biodiversity, especially that of the Chiquitano Region.