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Vascular occlusive diseases are one of the leading mortality causes in westernised countries. Occlusions of one of the major arteries can be overcome without devastating consequences provided a timely induction of compensating collateral arteries occurs. Perhaps the most outstanding feature of collateral vessel growth is the proliferation of smooth muscle cells (SMCs). Understanding the molecular mechanisms and identifying key molecular players of SMC proliferation would contribute significantly to the development of efficient therapies to intervene with all processes involving neointima formation, including collateral growth. mRNA and protein coding for co-transcription factor Egr1 were found to be up-regulated in growing collateral vessels 6, 12 or 24 hours following femoral artery ligation in mice. Since Egr1 is required for SMC proliferation in vitro and in vivo and likely to be implicated in the initiation of collateral artery growth, the key signalling mediators regulating Egr1 expression specifically in proliferating vascular SMCs were investigated. Northern blot and Western blot analysis revealed a strong up-regulation of Egr1 within 2 hours of stimulation with PDGF-AB and FGF-2. These two potent SMC mitogens involved in neointima formation were used to stimulate vascular SMCs not only to delineate the regulators of Egr1 expression but also to identify additional key mediators of SMC proliferation. FGF-2 but not PDGF-AB led to a drastic reduction of desmin amount in proliferating SMCs, correlating closely with the phenotypic modulation of SMCs in vivo. Both growth factors triggered a dramatic increase in DNA-synthesis rate with a concomitant loss of p27 exp Kip1. Stimulation with PDGF-AB and FGF-2 triggered a rapid and transient activation of PDGFRβ and FGFR1 respectively, thus providing the basis for activation of down-stream targets. Analysis of an array of signalling pathways demonstrated a strong activation of the Ras-Raf-MEK-ERK cascade in response to both factors as measured by the level of phosphorylation of prominent members MEK, ERK1/2 and c-Myc. SAPK/JNK and p38, which also belong to the superfamily of MAP kinases, did not become activated following stimulation with either PDGF-AB or FGF-2. The analysis of various PKC isoforms identified PKCδ and PKCθ to be the key mediators of PDGF-AB- and FGF-2-induced mitogenesis in proliferating SMCs. Whereas PDGF-AB potently stimulated PKB/Akt with concomitant GSK3β phosphorylation, FGF-2-induced inactivation of GSK3β was independent of PKB/Akt. Specific inhibition in order to evaluate the contribution of individual pathways to Egr1 expression and vascular SMC proliferation revealed that inhibition of the Raf-MEK-ERK module by UO126 completely abolished DNA-synthesis and Egr1 expression without a compensation by alternative pathways. Surprisingly, inhibition of PI3K led to a switch to the mitogenic RafMEK-ERK signalling cascade which resulted in an augmented Egr1 expression. In conclusion, in porcine vascular SMCs, activation of the Ras-Raf-MEK-ERK signalling module appears to be the main prerequisite for Egr1 expression and DNA synthesis induction in response to PDGF-AB and FGF-2 whereas related kinases SAPK/JNK and p38 play no significant role. Inhibition of the PI3K-Akt cascade represents an alternative way to activate ERK1/2 and induce Egr1 expression. Whereas MEK is the central regulator of mitogenic effects in proliferating vascular SMCs, the PI3K-Akt pathway most likely exerts survival function. Inactivation of MEK by its specific inhibitors identified hyperphosphorylation as ayet unknown mechanism of kinase inhibition.
Central America is one of the world’s most herpetological diverse areas in relation to its size. Nicaragua is the largest country in this region and separates Nuclear from Lower Central America. It is one of the least herpetological explored countries in Central America and few studies dealing with the herpetofauna of a potion or the entire country have been published. I here update the checklist of the Nicaraguan herpetofauna, present taxonomic revisions of some difficult species complexes, compare the similarities of the composition of the herpetofaunal communities in the major forest formations present in the country within a zoogeographical context, and identify those species with a greater vulnerability risk in Nicaragua. Taxonomy The herpetofauna of Nicaragua currently consists of 244 species representing 134 genera and 42 families with 78 amphibian species representing 35 genera and 15 families, and 166 reptile species representing 99 genera and 27 families, which includes six marine species. Sixteen species (12 amphibians and four reptiles) are endemic to the country. Of the 12 endemic amphibian species, three are here described. In addition, five genera (Anotheca, Cerrophidion, Duellmanohyla, Isthmohyla, and Rhinobothryum) and two species (Rhadinea godmani and Urotheca decipiens) are known to occur both north and south of Nicaragua although there are no voucher specimens of these taxa to confirm their presence in country. I complete a bibliographic research updating the nomenclature changes and provide a brief herpetological history of Nicaragua, a recompilation of all species described upon Nicaraguan material and their current synonymy, the first time each species was recorded from the country, and a list of all recognized subspecies occurring in Nicaragua. I discuss the taxonomic uncertainties among the Nicaraguan populations of amphibians and reptiles and take further detailed taxonomic revisions on selected Nicaraguan species groups from the genera Anolis, Bolitoglossa, and Craugastor along their known distributional range. I describe five new species of herpetofauna (three of which are based on Nicaraguan material), redescribe five species of Anolis (three of which occur in Nicaragua), and provide voucher specimens of five other species for the first time in Nicaragua. In detail: • I studied the pholidosis, morphometrics as well as hemipenis and dewlap morphology in Anolis wermuthi, an anole endemic to the highlands of northern Nicaragua. I examine patterns of geographic variation using discriminant function analysis and discuss the characters that vary both individually and among populations. The results indicate that A. wermuthi is a single species with several disjunct, slightly divergent populations. I provide a standardized description, illustrations of the everted hemipenis of an adult topotype, the male and female dewlap, and a distribution map. I also provide brief descriptions of the localities where this species occurs and some ecological notes. • I studied the pholidosis, morphometrics as well as hemipenis morphology in the Central American anole species Anolis humilis, A. quaggulus, and A. uniformis. The three taxa are distinct in hemipenis morphology. However, very little differentiation in pholidotic and morphometric characters is documented. I document interspecific variation in several characters but with overlap of the documented ranges. A discriminant function analysis based on five pholidotic characters yielded a scatter diagram that showed large overlap between the clusters of the three taxa. I provide head scalation illustrations, an identification key, a distribution map, and standardized descriptions of the commonly distributed in Nicaragua A. quaggulus as well as of the other two species. • I describe two new species of anoles (genus Anolis) from Panama formerly referred to as Anolis limifrons. The two new species, Anolis apletophallus and Anolis cryptolimifrons, differ from A. limifrons by having a large bilobed hemipenis (small and unilobed in A. limifrons). The new species differ from each other in male dewlap size and coloration. I provide illustrations of the head scalation, everted hemipenis, and dewlap, an identification key, a distribution map, and standardized descriptions of the commonly distributed in Nicaragua A. limifrons and the two new species described herein. • I describe two new species of salamanders of Bolitoglossa from southern Nicaragua. Bolitoglossa indio is known from Río Indio in the lowlands of the Río San Juan area and Bolitoglossa insularis from the premontane slopes of Volcán Maderas on Ometepe Island. The two new species are of unknown affinities but both differ from their congeners in coloration. Bolitoglossa indio is most similar to B. mexicana and B. odonnelli from which differ by having both broad dorsolateral pale brown stripes not clearly delimited in outline. Bolitoglossa insularis is most similar to B. mombachoensis and B. striatula from which differ by the absence of dark or light defined stripes on dorsum and venter. • I describe a new species of frog of the genus Craugastor from Río San Juan, Nicaragua. The new species, Craugastor chingopetaca, is assigned to the fitzingeri group and differs from most Central American species of that group by the absence of a midgular pale stripe. Within the fitzingeri group it is most similar to C. crassidigitus and C. talamancae from which it differs in several morphological characteristics such as more extensive webbing, retuse disk covers on some digits, and relative toe length. • I provide voucher specimens of Cochranella spinosa, Kinosternon angustipons, Mesaspis moreletii, Cnemidophorus lemniscatus and Adelphicos quadrivirgatum for the first time in Nicaragua. I include descriptions, illustrations, and brief ecological notes for the five new country records. Zoogeography Based on the concept of ecological formations proposed by HOLDRIDGE (1967), nine forest formations are found in Nicaragua. Of the total number of terrestrial species of herpetofauna found in Nicaragua, 131 species (55.0%) occur in Lowland Wet Forest, 21 of which (8.8%) are restricted to this forest formation, 168 species (70.6%) occur in Lowland Moist Forest, 15 of which (6.3%) are restricted to this forest formation, 84 species (35.3%) occur in Lowland Dry Forest, four of which (1.7%) are restricted to this forest formation, 47 species (19.7%) occur in Lowland Arid Forest, with no species restricted to this forest formation, 59 species (24.8%) occur in Premontane Wet Forest, three of which (1.3%) are restricted to this forest formation, 116 species (48.7%) occur in Premontane Moist Forest, 10 of which (4.2%) are restricted to this forest formation, 51 (21.4%) species occur in Premontane Dry Forest, with no species restricted to this forest formation, 13 species (5.5%) occur in Lower Montane Wet Forest, two of which (0.8%) are restricted to this forest formation, and 50 species (21.0%) occur Lower Montane Moist Forest, seven of which (2.9%) are restricted to this forest formation. The Coefficient of Biogeographic Resemblance algorithm show a distinct composition of the herpetofauna from the isolated highlands of northeastern Nicaragua, which is characterized by a high proportion of endemic species. Two other clusters are evident when analyzing the herpetofaunal similarities among Nicaragua, the Pacific versant and the central mountains and the Atlantic lowlands. In addition, the Pacific lowlands are characterized by a relatively homogeneous composition of the herpetofauna. In contrast, many species have their northern limit of distribution in the Atlantic lowlands with the ranges of most of these species ending in southern Nicaragua. The central mountains constitute the southern limit of distribution of several highland species. In general, there is a greater contribution of reptile than amphibian species to the total herpetofauna present in each forest formation. This unbalance is slightly higher in the dry than in the moist parts of the country. The similarities in the composition of the reptiles between the different forests formations seem to be relatively distinct on an elevation factor, whereas in amphibians similarities might be better explained in correlation with humidity. The total amount of amphibian and reptile species in Nicaragua has a Middle American Element dominance and varies between amphibians and reptiles, with and a greater South American Element influence in anurans and a greater Old Northern Element influence in reptiles. In general, there is a greater percentage of species with a South American Element in extreme southeastern Nicaragua with a decreasing tendency towards northern Nicaragua. Taking in account the geography and geologic history of Nicaragua as well as the known Central American dispersal routes, I identify species of probable occurrence in Nicaragua as well as those places with a greater potential to hold undescribed endemic species. Conservation In Nicaragua, no amphibian or reptile populations are entirely free from anthropogenic impact. I determine the endangerment level of all Nicaraguan amphibian and reptile species using the IUCN categorizations and the Environmental Vulnerability Scores. Seventy-six species (31.9%) of Nicaraguan amphibians and terrestrial reptiles have high vulnerability, 118 (49.6%) medium vulnerability, and 44 (18.5%) low vulnerability. Eighteen species (7.4% of the total herpetofauna) are unknown from protected areas, including 13 high vulnerability species (three are endemic), four medium vulnerability species, and one low vulnerability species. To preserve the future of Nicaragua’s amphibians and reptiles, every species should reside in at least one protected area, the protected areas must be guarded, and monitoring programs are needed to detect changes in amphibian and reptile populations, prioritizing highly vulnerable species.
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.
In der vorliegenden Arbeit konzentrierte ich mich auf mediterrane wirbellose Tierarten, welche sich als Konsequenz ihrer Lebensweise nur schlecht ausbreiten können. Nichtsdestotrotz haben es Süßwasserkrabben der Gattung Potamon und Landschnecken der Gattung Tudorella geschafft, große Gebiete zu besiedeln, die heute durch das Mittelmeer getrennt sind. Für beide Gruppen wurde spekuliert, dass Menschen an ihrer Ausbreitung beteiligt waren. Es war mein Ziel die biogeographischen Muster dieser beiden Gattungen zu analysieren und abzuschätzen, ob Menschen tatsächlich Vektoren ihrer Ausbreitung waren. Meine Analysen fanden auf drei Ebenen statt: Taxonomie, Gattung und Art.
Amphibians of Malawi : an analysis of their richness and community diversity in a changing landscape
(2009)
This study summarizes the state of the knowledge of the amphibian diversity in Malawi highlighting the possible threats impending on this fauna correlated with human encroachment and land use change. New data about diversity, distribution and ecology have been gathered, whereas the old ones have been summarised, reviewed and commented. In order to put in context the responses of the amphibian communities to land use change, the main environmental characteristics of the country at a broad space and time scale have been explored. Furthermore, the original habitats and vegetation have been described, and their status in the present day Malawi discussed. In the same way, an overview of the actual state of the knowledge about the Malawian amphibians has been provided, and their ability to act as surrogate of environmental integrity in Sub-Saharan Africa commented on the basis of the available studies. Afterwards, the results of the study of the selected areas and samples have been analysed within this newly generated context. Different field and laboratory methods were applied for the quantitative analysis of the richness and diversity of the communities. Opportunistic search was used to detect species richness, whereas the visual encounter survey was applied to detect the relative abundance of species. Several indices of diversity and similarity, and extrapolations by means of true richness estimators were used for the analysis of the alpha and beta diversities. Additional information were gathered by means of pitfall traps with drift fence, and by the recording of the advertisement calls. Supplementary methods were applied for the analysis of the taxonomic composition of the collected material. In Malawi 84 amphibian species are recorded, two of which still undescribed (Leptopelis sp. and Phrynobatrachus sp.). Three further species need to be confirmed and might be possibly present too: Amietia viridireticulata, Hemisus guineensis, and Hyperolius minutissimus. Additionally, other unrecognised cryptic species — at least one — are present within the Hyperolius nasutus complex. Most of the species belong to the order Anura (82 species; 97.6%), whereas only two species belong to the Gymnophiona (2.4%). Anurans are divided into 12 families and 23 genera, whereas the two caecilians species into one family (Caecilidae) and two genera. The more diverse family is the Hyperoliidae (21 species, 25%) followed by the families Ptychadenidae (13 species, 15%), Arthroleptidae (11 species, 13%), Phrynobatrachidae (10 species, 12%), and Bufonidae and Pyxicephalidae (9 species, 11% respectively). The remaining high family diversity (seven families, Caecilidae included) is contrasted by a low number of species (11 species in total, 14%). Based on the available distribution data, the value of species richness of the anuran communities in Malawi is comprised between 5‒45 species. In average 16.8 ± 9.0 species (N=80) are to be found, 75% of the sites have less than 21 species, and only two sites have more than 25 species. Four hot spots of amphibian diversity were identified: the Nyika Plateau (24 species), Mangochi-Malombe (25 species), Zomba Plateau (32 species) and the Mulanje Massif (45 species). In the studied areas a mean of 14.7 ± 1.6 species was observed and extrapolations by means of the true richness estimators were in good agreement with this result. Among the studied areas the richest was Palm Forest Reserve (17 species), followed by Kaningina Forest Reserve (16 species) and Vinthukutu F. R., and Vwaza W. R (15 species). The poorest area was the Misuku Mountains with 12 species only and a slightly different ranking was generated by the true richness estimators. The mean of the species present in the samples was 4.8 ± 2.1 species, considerably less than the true species richness detected in the respective areas. Basing on the ranking generated by the K-dominance plot the most diverse samples were Palm F. R. and Misuku, whereas the less diverse were Kaningina F. R. and Fort Lister, confirmed by the values of the diversity indices. The main finding of this study was the observation of the lack of a clear match between environmental degradation and amphibian diversity, and the crucial importance of temporary water bodies for the preservation of the amphibian diversity. In fact, despite most of the original habitat formerly present in Malawi have been destroyed and replaced by cultivations, the amphibian communities of different areas showed a comparable diversity at both family and species richness level, and no evident match between environmental degradation and amphibian diversity was recognisable. Differences in species richness could mostly be explained by natural factors such the elevation gradient and the presence of temporary water bodies. However, it was not possible to exclude that the communities have changed during historical time and the shift in species composition already occurred together with the modification of their relative frequencies. Most of the species showed a remarkable ecological plasticity and several species were found in a variety of both natural and altered habitats. The classification of the Malawian amphibians on the basis of ecological guilds based on the available natural history data showed the preponderance (76%) of generalist pond breeders. As a consequence, most of these amphibians possessed a scarce capacity to act as surrogates of habitat integrity. Based on the result of this study the farm bush landscape with traditional agriculture practices bears a great potential to support amphibian diversity in terms of species richness, representing a compromise between local economic development and conservation. Furthermore, the results of this study indicate the outstanding importance of the southern-east region of Malawi for the conservation of the country’s amphibians.
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.
Panama is a megadiverse country that together with Costa Rica constitutes Lower Central America (LCA). Western Panama's Cordillera Central accounts for the eastern part of the LCA highlands shared between these countries. The aim of the present study is to compile the most complete and updated picture possible of the taxonomy, diversity, and distribution of reptiles that occur from 500 m asl upwards along the Talamanca and Tabasará ranges. These two continuous mountain ridges account for the western two-thirds of the Cordillera Central between the Costa Rican border and 81°W Including specimens collected four own research travels, I morphologically examined more than 1800 specimens, analyzed 16S and/or COI barcodes of 300 specimens, and performed a thorough search in literature and databases to obtain locality records for specimens and species occurrences. My complete occurrence dataset comprises 14620 georeferenced occurrence records in three quality categories. Conceivable occurrences of species not yet documented from a given area are evaluated on the basis of existing data either as "plausible" or "possible". I provide all datasets which I generated for this study in Appendices. The previously published descriptions of Dactyloa ginaelisae Lotzkat, Hertz, Bienentreu & Köhler 2013, Norops benedikti (Lotzkat, Bienentreu, Hertz & Köhler 2011), Sibon perissostichon Köhler, Lotzkat & Hertz 2010, and Sibon noalamina Lotzkat, Hertz & Köhler 2012 are included in the present work. In the course of integrative taxonomic analyses, I classify 15 genealogical lineages revealed by DNA barcoding within 7 anole species as Deep Conspecific Lineages (DCLs) because they lack consistent morphological differences to their nominal conspecifics. I provisionally classify 18 mitochondrial lineages found within six other anole species as Unconfirmed Genealogical Lineages (UGLs) pending adequate analyses of their morphological variation. I regard the two additional UGLs Celestus sp. and Geophis sp. and the two Confirmed Genealogical Lineages (CGLs) Lepidoblepharis sp. 1 and 2 to represent undescribed species. My taxonomic analyses yield the hitherto most comprehensive survey of the variability exhibited by dozens of reptile species in western Panama. The 16S and/or COI barcodes I provide represent 65 species recognized herein and constitute the first DNA barcode reference library for LCA reptiles. The reptile fauna of Panama comprises 265 species, including the four UGLs and CGLs mentioned above and characterized for the first time in this study, as well as Dendrophidion crybelum Cadle 2012 whose presence in the country I consider plausible. My occurrence dataset reveals that 160 of these species have been documented to occur in my study area. Adding the 20 species whose occurrence therein I consider plausible, I report the total species richness of the Talamanca and Tabasará ranges as comprising 180 species representing 81 genera in 25 families. With 178.8 species per 10 000 km2, the relative species richness of the area is extremely high even in a tropical context. In view of their overall documented distribution, I regard the presence of 27 additional species in my study area as possible. For the 180 species occurring in my study area I provide standardized species accounts that, together with the taxonomic results, for the first time permit the doubtless identification of all 180 species, and illustrate 168 of these with color photographs. Concerning biogeography, my georeferenced dataset yields noteworthy distribution extensions for many species. Moreover, I present the hitherto most comprehensive, detailed, and reproducible assessments of the distribution patterns, historical origins, and conservation as well as of the occurrence among physiographic regions, climatic and altitudinal belts, political subdivisions, and protected areas, for my study area's reptile fauna. With 65 species, more than a third of the fauna is endemic to LCA. Among these, 42 Talamancan highland endemics are restricted to the LCA highlands, in the case of 16 small-scale highland endemics with documented ranges spanning less than 100 km. I assess many of these endemics as endangered. The fact that several of these species do not occur in any protected area renders the establishment of additional conservation areas necessary, especially in the central Serranía de Tabasará. Distributional range boundaries shared among different clades of highland anoles indicate physiographic and climatic barriers that may have effected in situ speciation within these lineages. As the largest study on Panamanian reptile diversity assembled to date, the present dissertation considerably increases our knowledge on the reptiles along the Cordillera Central and beyond, and thus constitutes a solid basis for future studies.
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.
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.