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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.
Lipophile, sedimentgebundene Substanzen sind für endobenthische Tiere in hohem Maße bioverfügbar und können von diesen aufgenommen und angereichert werden. Für benthivore Fische besteht damit das Risiko, diese Chemikalien mit der Nahrung aufzunehmen. Die Aufkonzentrierung sedimentgebundener Chemikalien über zwei oder mehr trophische Ebenen (Biomagnifikation) kann somit durch die Bestimmung der Biokonzentration von Chemikalien in Fischen nach der OECD-Richtlinie 305 (OECD 1996) nicht adäquat erfasst werden. Zur standardisierten Bestimmung der Bioakkumulation und Biomagnifikation wurde eine einfache, zwei trophische Stufen umfassende Labornahrungskette etabliert. Diese bestand aus dem endobenthischen Oligochaeten Tubifex tubifex (MÜLLER) als Beute und dem Dreistachligen Stichling (Gasterosteus aculeatus LINNÉ) als Prädator. Die Experimente wurden mit 14C-markiertem Hexachlorbenzol und Terbutryn in dotiertem künstlichem Sediment und rekonstituiertem Wasser durchgeführt. Um den Einfluss einzelner Expositionspfade an der Gesamtanreicherung der Modellchemikalien zu quantifizieren, wurden die Fische gegenüber dotiertem Wasser bzw. dotiertem Sediment (Biokonzentrationsszenario), vorexponierten Würmern (Biomagnifikationsszenario) und Kombinationen dieser Aufnahmepfade (Bioakkumulationsszenario) exponiert. Sedimentgebundenes HCB wurde im Bioakkumulationsszenario sowohl in den Tubificiden (BAFWurm/Sediment (FG/FG) = 7,8) als auch in den Fischen (AFFisch/Wasser (FG/FG) = 52500; AFFisch/Sediment (FG/FG) = 47; AFFisch/Wurm (FG/FG) = 3,2) deutlich angereichert. Da die Gewebekonzentration von HCB im Räuber, auch auf Basis lipidnormierter Konzentrationen, die Konzentration in seiner Beute überstieg (AFFisch/Wurm (lipidnormiert) = 1,3), kann von einer Aufkonzentrierung der Chemikalie entlang der Labornahrungskette ausgegangen werden (Biomagnifikation). Es konnte gezeigt werden, dass die Exposition gegenüber der Kombination sämtlicher Aufnahmepfade zu deutlich höherer Anreicherung in den Fischen führte als im Falle einzelner Expositionspfade. Ein Vergleich der Ergebnisse der einzelnen Expositionsszenarien erlaubt den Schluss, dass HCB von den Fischen im Bioakkumulationsszenario zu ungefähr gleichen Teilen über das Wasser (45%) und über die Nahrung (41%) aufgenommen wurde, während die Anwesenheit kontaminierten Sediments nur mit 14% zur Gesamtanreicherung beitrug. 14C-Terbutryn wurde im Bioakkumulationsszenario - auf Basis der Gesamtradioaktivität - sowohl in den Tubificiden (AF Wurm/Sediment (FG/FG) = 4,4) als auch in den Fischen (AFFisch/Wasser (FG/FG) = 323; AFFisch/Sediment (FG/FG) = 10; AFFisch/Wurm (FG/FG) = 1,4) angereichert. Allerdings wurde Terbutryn in den Stichlingen zum überwiegenden Teil zu einem polareren Metaboliten transformiert (84%). Daher müssen zur Abschätzung der Anreicherung von Terbutryn die auf den Gehalt an Ursubstanz korrigierten Gewebekonzentrationen und Anreicherungsfaktoren betrachtet werden. Hierbei wird deutlich, dass Terbutryn nicht entlang der Labornahrungskette aufkonzentriert wurde (AFFisch/Wurm = 0,09). Ein Vergleich der Ergebnisse der einzelnen Expositionsszenarien zeigt, dass der Hauptaufnahmepfad von 14C-Terbutryn in Stichlingen das umgebende Wasser ist, während die Anwesenheit kontaminierten Sediments und die Aufnahme über die Nahrung eine untergeordnete Rolle spielen. Da die Messung der Bioakkumulation und Biomagnifikation von sedimentassoziierten Substanzen sehr aufwendig ist, werden zur Abschätzung ihres Risikopotentials vermehrt mathematische Modelle entwickelt und eingesetzt, die eine Chemikalienanreicherung in Nahrungsketten vorhersagen sollen. Im Rahmen der vorliegenden Arbeit wurden die Vorhersagen dreier Modelle mit den experimentell ermittelten Daten verglichen. Hierdurch sollte sowohl die Eignung des entwickelten Testsystems als auch der verwendeten Modelle als nützliche Instrumente des environmental risk assessment überprüft werden. Die Vorhersagen der drei Modelle bei Applikation auf die Daten der Labornahrungskette stimmen gut mit den experimentell bestimmten Konzentrationen von HCB und Terbutryn in den Tubificiden und Fischen überein. Für HCB sagen alle drei Modelle eine Biomagnifikation in der Labornahrungskette vorher. Die Modelle unterschätzen die gemessenen Konzentrationen in den Fischen mit einem Faktor von 1,1 - 1,7 nur geringfügig. Die Konzentration in den Tubificiden wird vom Gobas/Morrison-Modell sehr präzise vorhergesagt (Unterschätzung um Faktor 1,1), während sie im Campfens/Mackay-Modell (Faktor 2,1) und Gobas-Modell (Faktor 6,3) deutlicher unterschätzt wird. Speziell die dem Campfens/Mackay- und Gobas-Modell zugrunde liegenden Annahmen zur Anreicherung in benthischen Organismen erwiesen sich für HCB und Tubificiden als unzureichend zu sein, da die Modelle hierbei nur die Aufnahme aus dem Porenwasser berücksichtigen. Für Terbutryn sind die Modellvorhersagen sehr viel ungenauer als für HCB, da vor allem die starke Metabolisierung von Terbutryn in den Stichlingen unterschätzt wird. Dies resultiert in einer Überschätzung der Terbutryn-Konzentration in den Fischen (Faktor 5,8 - 6,4). Allerdings bleiben zwei Punkte festzuhalten: 1) Die Modelle sagen keine Biomagnifikation von Terbutryn in der Labornahrungskette vorher. 2) Die Modellvorhersagen bestärken die Annahme, dass die Anreicherung von Terbutryn in den Fischen dominiert ist von der Aufnahme aus dem umgebenden Wasser über die respiratorische Oberfläche. Die analysierten Modelle können bei entsprechender Weiterentwicklung als nützliche Instrumente für eine erste Abschätzung des Risikos der Bioakkumulation sedimentgebundener, hoch lipophiler Substanzen in aquatischen Nahrungsketten im Rahmen der Risikoabschätzung (environmental risk assessment) dienen. Zum gegenwärtigen Entwicklungsstand ist die Labornahrungskette jedoch den Modellen vorzuziehen, da sie die konservativeren Daten liefert. Für eine abschließende Beurteilung der vorgestellten Methoden bedarf es allerdings einer Verbreiterung der Datenbasis.
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.
In der vorliegenden Untersuchung wurden Populationen der Gattung Corbicula im Rhein mit Individuen aus der Mosel, der Weser sowie aus Frankreich, Spanien, Nordamerika und dem Nahen und Fernen Osten sowohl mit genetischen als auch morphologischen Methoden untersucht. Aus diesen Daten sollte ermittelt werden, wie viele Taxa bei der rezenten Besiedelung Europas auftraten und welche Migrationsrouten hierbei nachgewiesen werden konnten. Es konnte gezeigt werden, dass im Rhein zwei hybridisierende genetische Linien auftraten, wobei keine Rückkreuzung mit den Eltern nachgewiesen werden konnte. Die Hybride waren morphologisch nicht zu unterscheiden. Hinweise auf einen unterschiedlichen Chromosomensatz dieser Linien bzw. eine Polyploidie konnte nicht gefunden werden. In der Rhone wurde eine weitere Linie entdeckt. Eine der genetischen Linien im Rhein konnte im Vergleich zu Individuen aus Fernost als C. fluminea identifiziert werden. Die Herkunft der beiden Linien aus Rhein und Rhone blieb unklar, da sie nicht Individuen aus Israel oder Nordamerika zugeordnet werden konnten. Eine Polytomie der MP- und ML-Analysen war nicht auf einen zu geringen Datensatz zurückzuführen, vielmehr konnte gezeigt werden, dass Corbicula im Pleistozän eine Radiation durchief. Schalenmorphologisch konnten die genetischen Linien aus dem Rhein nicht durchgehend den zwei auftretenden Morphen zugeordnet werden. Gleichzeitig schienen diese Individuen die Extreme einer weltweiten Variabilität der Schalenform darzustellen. Ein morphologischer Vergleich von Schalen aus der Sammlung Senckenberg zeigte keine Unterschiede zwischen Individuen, die als C. fluminalis und C. fluminea bezeichnet waren. Vielmehr scheint die Schalenform nicht genügend conchologischen Merkmale zu besitzen, um die genetischen Linien zu unterscheiden. Die Besiedelung Europas durch die Körbchenmuschel erfolgte mehrfach unabhängig in verschiedenen Flusssystemen Südwest- und Mitteleuropas Anfang der 1980er Jahre. Auf- grund der hier nachgewiesenen Isolationswirkung von Stauwehren der Bundeswasserstrassen auf Makroinvertebraten und der Ergebnisse der DAF-Fingerprints von Corbicula- Populationen wurde die Mosel vermutlich von Frankreich aus besiedelt.
The rate of species extinctions due to anthropogenic activities has dramatically increased within the past few centuries (Dirzo & Raven, 2003; Novacek & Cleland, 2001). Although the mechanisms and ultimate causes leading to the extinction of species remain largely unclear (Frankham et al., 2002), five threats to global biodiversity have frequently been referred to as the most important: habitat destruction and fragmentation, global climate change, hunting and overuse of food resources, biological invasions and environmental pollution (Dudgeon et al., 2006; Lewis, 2006; Novacek & Cleland, 2001). Different research fields, as conservation biology, ecology and ecotoxicology, investigate the effects of these factors on organisms and found strong evidence for their negative impact on regional and global biodiversity.
In most cases, natural populations will be impacted not only by one threat, but rather a combination of them (Buckley & Roughgarden, 2004; Kappelle et al., 1999). Multiple environmental stress factors can have cumulative negative effects on the survival of populations (Sih et al., 2004). To understand, how natural populations respond to combinations of different stress factors is thus of crucial importance in order to understand our present and future impact on all scales of biodiversity (Warren et al., 2001).
The effects of anthropogenically introduced chemicals on organisms and ecosystems are investigated in the field of ecotoxicology. Research in this area has led to a large body of information concerning the impact of chemical stress on the fitness of model species in the laboratory. In contrast to this, there is an obvious lack of knowledge on the effects of contaminants on natural populations and communities (Bickham et al., 2000; Bourdeau et al., 1990). For instance, ecotoxicologists have just started to investigate the impact of environmental pollution on the genetic variability of natural populations (Bickham et al., 2000; Whitehead et al., 2003). Genetic variation provides the raw material for populations in order to adapt to changing environmental conditions and is thus the substrate for evolution and long-term survival of populations and species (Frankham, 2005). The amount of genetic variation in populations is positively correlated with the effective population size (Frankham, 1996). Habitat destruction and fragmentation has divided the ranges of many species into small and isolated refuges. Without migration from adjacent habitats, isolated populations will decrease in their level of genetic diversity through random loss of alleles (Hedrick, 2000). Frankham (1995) for instance, showed that 32 of the 37 endangered species (which occur in small populations per definition) of different animals and plant taxa display reduced levels of heterozygosity compared to closely related and more frequent species.
In strongly human impacted landscapes, both factors, environmental pollution and habitat destruction, can be expected to occur frequently together. It is thus of crucial importance to investigate the impact of reduced genetic diversity and inbreeding on the response to chemical stress. In addition, chemical exposure has frequently been discussed to have an impact on the extent of genetic variability in exposed populations (Guttman, 1994; Staton et al., 2001; van Straalen & Timmermans, 2002). However, evidence for this 'genetic erosion hypothesis' remained scarce to date, most likely because of the difficulty to single out the impact of pollution stress from a background of multiple factors which influence patterns of genetic variability in natural populations (Belfiore, 2001; Staton et al., 2001; van Straalen & Timmermans, 2002).
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.
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.
