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- Englisch (23) (entfernen)
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- Habitat Fragmentation (2)
- Kakamega Forest (2)
- Systematik (2)
- Abwasserbehandlung (1)
- Africa (1)
- Afrika (1)
- Amazonia (1)
- Amazonien (1)
- Araneae (1)
- Arzneistoffe (1)
Institut
- Institut für Integrierte Naturwissenschaften, Abt. Biologie (23) (entfernen)
Über 10.000 verschiedene organische Substanzen wie Arzneistoffe, Inhaltsstoffe von Körperpflegemitteln und Biozide werden regelmäßig im Alltag eingesetzt. Die meisten Substanzen gelangen nach ihrer Verwendung in das häusliche Abwasser. Bisherige wissenschaftliche Untersuchungen haben ergeben, dass eine konventionelle biologische Abwasserreinigung in kommunalen Kläranlagen keine ausreichende Barriere für die Emission dieser anthropogenen Stoffe in die Oberflächengewässer darstellt.
Dies birgt unvorhersehbare Risiken für die aquatischen Lebensgemeinschaften und die Trinkwasserversorgung. Hinsichtlich ihres Vorkommens und Verhaltens in kommunalen Kläranlagen besteht daher insbesondere für erst kürzlich eingeführte und/oder in der Umwelt nachgewiesene Spurenstoffe (sogenannte "neuartige" Spurenstoffe, engl.: "emerging micropollutants") ein großer Forschungsbedarf. Um ein möglichst umfassendes Bild vom Verhalten neuartiger organischer Spurenstoffe in der kommunalen Abwasserbehandlung zu erhalten, wurden im Rahmen dieser Dissertation die folgenden Substanzklassen, welche ein weites Spektrum an physiko-chemischen Eigenschaften aufweisen, untersucht: Arzneistoffe (Betablocker und psychoaktive Substanzen), UV-Filtersubstanzen, Vulkanisationsbeschleuniger (Benzothiazole), Biozide (Antischuppenmittel, Konservierungsmittel, Desinfektionsmittel) und Pestizide (Phenylharnstoff- und Triazinherbizide).
The stands surveyed are among the last closed canopy forests in Rwanda. Their exploration began in the early twentieth century and is still ongoing. Previous studies were mainly concerned with plant sociological issues and presented references to environmental factors in anecdotal form, at best using indirect ordination methods. The present study undertakes a classification of the vegetation with numerical methods and establishes quantitative relationships of the species’ distributional structure to environmental parameters using spatially explicit procedures. For this purpose, 94 samples were taken in 100 m² hexagonal plots. Of these, 70 samples are from Nyungwe, 14 are from Gishwati, and 10 are from Cyamudongo. Given the homogeneity of the terrain and vegetation, all vegetation types encountered, all types of stands, and all vegetation strata were included. The beta diversity is expressed by an average Bray-Curtis dissimilarity of 0.92, and in JOST’S (2007) numbers equivalents, 37.90 equally likely samples would be needed to represent the diversity encountered. Within the survey, 1198 species in 127 families were collected. Among the specimens are 6 local endemics and 40 Albertine Rift endemics. Resulting from UPGMA and FCM-NC, 20 to 40 plant communities were established depending on the level of resolution. It can be inferred by means of a Mantel correlogram that the mean zone of influence of a single vegetation stand, as sampled by a 100 m² plot in Nyungwe Forest, ranges between 0.016 and 3.42 km. Of the communities compiled using FCM-NC and UPGMA, 50% consist of individual samples. Beyond undersampling, natural small-scale discontinuities are reflected by this result. Partial db-RDA resulted in an explained variation of 9.60% and 14.41% for environmental and soil factors, respectively. Utilising variation partitioning analyses based on CCA and tb-RDA, between 21.70% and 37.80% of the variation in vegetation data could be explained. The spatially structured fraction of these parameters accounts for between 30.50% and 49.80% of the explained variation (100%). The purely environmental parameters account for a share of 10.30% to 16.30%, whereby the lower limit originates from the unimodal approach and has lost its statistical significance. The soil variables, also after partial analysis, account for a share of 19.00% to 35.70%. While the residual impact of the climatic parameters is hardly significant, the effect of the soil properties is prevalent. In general, the spatially structured fraction of the parameters is predominant here. While on the broad-scale climatic factors, the altitude a.s.l. and the geology are determining factors, some soil parameters and matrix components also show their impacts here. In the mid-range of the scale, it is the forest matrix, the soil types, and the geology that determine species distribution. While in the fine range of the scale, some unrecorded parameters seem to have an effect, there are also neutral processes that determine species composition.
Die Verwendung physiologischer Indikatoren, welche die Reaktion von Organismen auf Veränderungen ihrer Umwelt widerspiegeln, bietet ein großes Potenzial für ökologische Studien. Durch die Analyse des physiologischen Zustandes von Organismen ermöglichen diese Indikatoren eine schnellere Erfassung von Veränderungen in aquatischen Ökosystemen als es durch die Betrachtung ökologischer Indikatoren, wie z. B. der Struktur der Benthosgemeinschaft oder des Reproduktionserfolges einzelner Arten, möglich ist. Dieser Zeitvorteil kann sowohl die Effektivität der Habitatbewertung als auch experimenteller Studien in der aquatischen Ökologie erhöhen. In diesem Zusammenhang konzentriert sich die vorliegende Arbeit auf physiologische Messgrößen, wie die Konzentration von Energiespeicherstoffen, den zellulären Energiestatus (Adenylate Energy Charge) oder die Stoffwechselaktivität in vivo, die den energetischen Zustand oder den aktuellen Energieverbrauch von Organismen charakterisieren, sowie auf das RNA:DNA-Verhältnis als Wachstumsindikator. Obwohl diese Indikatoren in der marinen Ökologie, und in jüngerer Zeit auch in der Ökotoxikologie, regelmäßig verwendet werden, haben sie in der limnischen Ökologie bisher wenig Anwendung gefunden. Um die Anwendung physiologischer Indikatoren in diesem Bereich zu verstärken verfolgt die Dissertation zwei Ziele. Zum einen verdeutlicht sie das Potenzial der einzelnen physiologischen Indikatoren, zum anderen stellt sie Grundlagenwissen zu ausgewählten ökophysiologischen Aspekten einheimischer und gebietsfremder Arten der Ordnung Amphipoda bereit, die als Schlüsselarten aquatischer Lebensräume als besonders geeignet für die Bestimmung physiologischer Indikatoren angesehen werden. In diesem Sinne werden in Kapitel 2 sowohl die grundlegenden Annahmen, als auch die theoretischen und methodischen Grundlagen für die Bestimmung physiologischer Indikatoren aufgezeigt und ihre Anwendbarkeit in Fallstudien verdeutlicht. Die durchgeführten Experimentalstudien (Kapitel 3−5) liefern Informationen zu (i) den art- und geschlechtsspezifischen Unterschieden in der saisonalen Variation des energetischen Zustandes natürlicher Gammarus Populationen (G. fossarum, G. pulex), (ii) den Unterschieden in der Stoffwechsel- und Bewegungsaktivität verschiedener Amphipoda-Arten (G. fossarum, G. roeselii und D. villosus), sowie (iii) den direkten Auswirkungen von Ammoniak auf die Physiologie und die Bewegungsaktivität von D. villosus. In Kapitel 6 werden abschließend die grundlegenden Schlussfolgerungen aus den durchgeführten Feld- und Laborstudien, sowie ihre Relevanz und Auswirkungen für die Anwendung physiologischer Indikatoren in der limnischen Ökologie diskutiert.
Nandi forests (South and North Nandi forests) are situated in the Rift Valley Province of Kenya very close to Kakamega forest. From previous documents it has been seen that Kakamega and Nandi forests were connected to each other forming one big "U" shaped forest block till the beginnings of 1900s. Due to human pressures, currently there are three different forests form the previous one block forest. Although they were one forest, information on Nandi forests is very scanty when it is compared to that of Kakamega forest. The species composition and diversity as well as plant communities and population structure of Nandi forests have not been studied. Information is not available about the similarity status of South and North Nandi forests. Furthermore the natural regeneration potential (seedling bank) of these forests is not well studied and documented. Hence this study aims to fill these gaps.
In this study totally 76 quadrates (49 from South Nandi and 27 from North Nandi) were used to collect data. In the South Nandi forests 27 of the quadrates were laid in the better side of the forest (at Kobujoi) and the remaining 22 were in the heavily disturbed part of this forest (Bonjoge). The quadrates were arranged on transects that have one to one and half km which were parallel to the slope. The distance between the quadrates was 100 meter and transects are 500 m apart. The size of the main quadrate was 400 m2 (20 X 20 m) which also had five small plots (3 X 3 m) distributed on the four corners and in the center. Each woody plants (climbers, shrubs and trees) having more than one meter and greater than two centimeter diameter at breast height (dbh) were measured and recorded. Seedlings and herbaceous plants were sampled in the smaller plots. Individual plants were identified at species level and when it was not possible to identify in the field voucher specimen were prepared and latter identified at the East African Herbarium, National Museum of Kenya, and Nairobi. Clustering and ordination were performed using PC-ORD and CANOCO ecological softwares, respectively. For both clustering and ordination abundance data of the species was used. Shannon diversity index and evenness were computed using PC-ORD while similarity indices, Fisher alpha, rarefaction, species richness estimation (nonparametric species richness estimators) were conducted using EstimateS. Indicator species analysis was undertaken using PC-ORD. Basal area and height class distribution at forests level or site level (Bonjoge and Kobujoi) and diameter (dbh) class distribution for selected trees species were performed to evaluate population structure.
Furthermore importance value (IV) of woody plant species was calculated. SPSS version 16 was used to undertake both parametric (when data assume normal distribution) and nonparametric (when data are not assuming normal distribution) comparison of means, correlation and regression analysis.
In this study totally 321 vascular plant species comprising 92 families and 243 genera were identified in Nandi forests (both South and North Nandi forests). In South Nandi forest 253 plant species form 82 families and 201 genera were recorded while in North Nandi 181 species comprising 67 families and 155 genera were recorded. Jackknife second order estimators gave the highest species richness estimate for both South and North Nandi forests i.e. 284 and 209, respectively. In the case of highly disturbed and less disturbed parts of South Nandi forest 138 and 172 vascular plant species were recorded, respectively. Asteraceae, Rubiaceae and Euphorbiaceae are the top three species rich families of Nandi forests. In terms of different diversity measures (i.e. alpha and beta diversity, Fisher alpha, Shannon diversity and evenness indices) South Nandi is more diverse than North Nandi forest. Sörensen and Jaccard (classic) as well as their respective abundance based similarities showed that there is a low species similarity between South and Nandi forests. The cluster analysis resulted in three different plant communities and this result is supported by the ordination result.
South and North Nandi forest has inverted "J" height class distribution showing that larger proportion of woody plant individuals are found in the lower height classes. Similar pattern is observed when the diameters of all woody plants were considered together. However, different diameter class distributions (seven types) were identified when selected tree species were analyzed separately. It has been observed that the basal area of South Nandi forest is significantly lower than that of North Nandi forest (Mann-Whitney U =358, p < 0.001). Similarly Bonjoge has significantly lower basal area (t-value=3.77, p<0.01) than that of Kobujoi. Number of woody plat seedlings in South Nandi forest is significantly higher than that of North Nandi (Mann-Whitney U = 362.5, p<0.001). In the same way Bonjoge has significantly smaller number of ssedlings than Kobujoi (t-value 4.24, p<0.001). Most of species in both forests are able to resprout from stumps after physical damage; hence this helps the regeneration of the forests in addition to seedling banks. This study enables to fill some of the information gaps about Nandi forests especially of floristic composition, population structure, natural regeneration and human impacts on this ecosystem.
Amphibian populations are declining worldwide for multiple reasons such as habitat destruction and climate change. An example for an endangered European amphibian is the yellow-bellied toad Bombina variegata. Populations have been declining for decades, particularly at the northern and western range margin. One of the extant northern range centres is the Westerwald region in Rhineland-Palatinate, Germany. To implement informed conservation activities on this threatened species, knowledge of its life-history strategy is crucial. This study therefore focused on different developmental stages to test predictions of life-history theory. It addressed (1) developmental, (2) demographic and (3) genetic issues of Bombina variegata as a model organism: (1) Carry-over effects from larval environment to terrestrial stages and associated vulnerability to predators were investigated using mesocosm approaches, fitness tests and predation trials. (2) The dynamics and demography of B. variegata populations were studied applying a capture-mark-recapture analysis and skeletochronology. The study was complemented through (3) an analysis of genetic diversity and structuring of B. variegata populations using 10 microsatellite loci. In order to reveal general patterns and characteristics among B. variegata populations, the study focused on three geographical scales: local (i.e. a former military training area), regional (i.e. the Westerwald region) and continental scale (i.e. the geographical range of B. variegata). The study revealed carry-over effects of larval environment on metamorph phenotype and behaviour causing variation in fitness in the early terrestrial stage of B. variegata. Metamorph size and condition are crucial factors for survival, as small-sized individuals were particularly prone to predator attacks. Yellow-bellied toads show a remarkable fast-slow continuum of the life-history trait longevity. A populations’ position within this continuum may be determined by local environmental stochasticity, i.e. an extrinsic source of variation, and the efficiency of chemical antipredator protection, i.e. an intrinsic source of variation. Extreme longevity seems to be an exception in B. variegata. Senescence was absent in this study. Weather variability affected reproductive success and thus population dynamics. The dispersal potential was low and short-term fragmentation of populations caused significant genetic differentiation at the local scale. Long-term isolation resulted in increased genetic distance at the regional scale. At the continental scale, populations inhabiting the marginal regions were deeply structured with reduced allelic richness. As consequence of environmental changes, short-lived and isolated B. variegata populations at the range margin may face an increased risk of extinction. Conservation measures should thus improve the connectivity among local populations and reinforce annual reproductive success. Further research on the intraspecific variation in B. variegata skin toxins is required to reveal potential effects on palatability and thus longevity.
Da die Belastung von Gewässern mit Mikroorganismen ein Gesundheitsrisiko für den Menschen unter anderem bei dessenFreizeitnutzung birgt, wurde die mikrobielle Belastung der Flüsse Rhein, Mosel und Lahn anhand von Indikatoren für fäkalbürtige bakterielle (Escherichia coli, intestinale Enterkokken) und virale Belastungen (somatische Coliphagen) untersucht. Des Weiteren wurden blaCTX-MGene als Marker für die Verbreitung von Antibiotikaresistenzen in der Lahn quantifiziert. Durch vergleichende Analysen von Monitoringdaten gegensätzlicher Abflussgeschehen in Rhein und Mosel wurde ein Einfluss von Veränderungen klimarelevanter Parameter auf die Verbreitung der fäkalen Indikatororganismen (FIO) geprüft. Die Analysen an Rhein, Mosel und Lahn zeigen deutlich, dass hohe Abflüsse und Niederschläge den Eintrag von FIO und Antibiotikaresistenzgenen (ARG) und damit potentiell antibiotikaresistenter Bakterien in Gewässer begünstigten, während unter dem Einfluss hoher Globalstrahlung und steigenden Wassertemperaturen ein Rückgang zu beobachtenwar. Basierend auf als relevant identifizierten Einflussparametern wurden multiple lineare Regressionsmodelle (MLR Modelle) entwickelt, die eine zeitnahe Vorhersage von FIO Konzentrationen an fünf Stellen eines Lahnabschnitts ermöglichen. Wechselwirkungenzwischen abiotischen und biotischen (Fraßdruck) Faktoren tragen zur Entstehung saisonaler Muster in den FIO Konzentrationenbei. Diese sind unter Niedrigwasserverhältnissen und besonders in Flüssen mit ausgeprägten trophischen Interaktionen besonders deutlich ausgeprägt und beeinflussen eine Übertragbarkeit von Modellansätzen zwischen Flüssen unterschiedlicher biologischer und hydrologischer Charakteristika. Daraus, dass Bakterien davon stärker betroffen sind als Coliphagen, lässt sich schließen, dass bakterielle Indikatoren virale Belastungen nicht ausreichend abbilden. BlaCTX-MGene waren in der Lahn parallel zu den FIO ubiquitär nachzuweisen, was auf einen fäkalen Ursprung hinweist. Landwirtschaft und kommunale Kläranlageneinleiter trugen zur Belastung mit FIO bei. Es zeigte sich, dass auch nicht badende Wassersportler mit eingeschränktem Wasserkontakt nachweislich dem Risiko ausgesetzt waren, antibiotikaresistente Bakterien (ARB) samt ihren Genen zu verschlucken, was das Risiko einer Infektion oder Kolonisierung mit den entsprechenden Bakterien birgt. Da ARG zu großen Teilen durch E. colierklärt werden konnten, könnenARG gegebenenfalls in MLR Modellemit E. colispezifischen Vorhersagevariablenintegriert werden. Kurzeitige und kurzfristig auftretende Verschmutzungsereignisse werden in Zukunft als eine Folge des Klimawandels in ihrer Häufigkeit weiter zunehmen. Identifizierte Herausforderungen hinsichtlich der Implementierung von Frühwarnsystemen zur Bewertung der mikrobiellen Wasserqualität in Flüssen liegen in den Anforderungen der Badegewässerrichtlinie (Richtlinie 2006/7/EC) und in einer unzureichenden Harmonisierung des Rechtsrahmens der Europäischen Union (EU) begründet, um Gesundheitsrisiken aufgrund mikrobieller Belastung in multifunktional genutzten Gewässern angemessen zu begegnen.
The first group that was revised within my study is Ochralea Clark, 1865 (Hazmi & Wagner 2010a). I have checked the type specimen of most species that were originally described in Ochralea and there is no doubt that this genus is clearly distinct from Monolepta. Weise (1924) has synonymised Galeruca nigripes (Olivier, 1808) with O. nigricornis Clark, 1865 and the valid name of the species is O. nigripes (Olivier, 1808). Out of ten species originally described in this genus, only this species remain valid and O. pectoralis is a new synonym of O. nigripes. Additionally, Monolepta wangkliana Mohamedsaid, 2000 is very closely related to O. nigripes and need to be transferred to Ochralea. The second genus where the revision is still published is Arcastes Baly, 1865 (Hazmi & Wagner 2010b). I have checked the genitalic characters of A. biplagiata, and most of the type species of other Arcastes. Arcastes biplagiata possesses a peculiar shape of the median lobe and asymmetrically arranged endophallic structures. These peculiar characters are very useful to delimit this genus from the others. Therefore, only three valid species remain in Arcastes, while two new synonyms are found and fourrnother species need to be transferred to other genera. While checking the genitalic characteristics of type species of Arcastes sanguinea, thernmedian lobe as well as the spermatheca of this species possesses strong differences to A. biplagiata. The species was redescribed and transferred in a monotypic new genus Rubrarcastes Hazmi & Wagner, 2010c. The fourth genus that was already revised is Neolepta Jacoby, 1884. It was originally described on base of only two species by that time, N. biplagiata and N. fulvipennis. Jacoby has not designated a type species of the genus, and Maulik (1936) did it later, with the designation of N. biplagiata. Jacoby in his original description has only commented that Neolepta is very close and similar to Monolepta Chevrolat, 1837 and Candezea Chapuis, 1879. Subsequent authors have described further eight species, and transferred one species from Luperodes to it, summing up the total number of eleven described species in Neolepta. I have checked the genitalic characters of the type, N. biplagiata and have found out that the median lobe is not incised apically and stronger sclerotised ventral carinae with an apical hook close to the apex occur. Out of all described species, only two are closely related to the genero-type, N. sumatrensis (Jacoby, 1884) new combination and N. quadriplagiata Jacoby, 1886 that will remain in this group after the revision. All other species need to be transferred to other genera, including the newly described Paraneolepta and Orthoneolepta. The last distinct paper of this thesis presented the results on Monolepta Chevrolat, 1837. The massive number of Monolepta from the entire Oriental Region, with about 260 described species names is a more long-life project and not practicable within a PhD-study. Thus I have focused on the species of Monolepta known from the Sundaland area in this work. A comprehensive revision including the study of the primary types of the described species, has never been done for Monolepta from this sub-region, while new species have also been described in the last decade (e. g. Mohamedsaid 1993, 1997, 1998, 1999, 2000a,b, 2001, 2002, 2005).
On base of the most current species lists of Mohamedsaid (2001, 2004, 2005) and Kimoto (1990), the number of valid species described from this region is about 72. After my revision, only thirteen valid species can remain in Monolepta in the sense of the generotype M. bioculata (Wagner 2007), while seven species have been found as new synonyms, three have been already transferred to other genera and further 49 species need to be transferred to other genera.
This study was conducted in Nyungwe National Park (NNP); a biodiversity hotspot Mountain rainforest of high conservation importance in Central Africa, but with little knowledge of its insect communities including butterflies, good indicators of climate change, and forest ecosystem health. The study aimed at availing baseline data on butterfly species diversity and distribution in NNP, for future use in monitoring climate change-driven shifts and the effects of forest fragmentation on the biodiversity of Nyungwe. Butterflies were collected seasonally using fruit-baited traps and hand nets along elevational transects spanning from 1700 m up to 2950 m of altitude. Two hundred forty-two species including 28 endemics to the Albertine Rift and 18 potential local climate change indicators were documented. Species richness and abundance declined with increasing elevation and higher seasonal occurrence was observed during the dry season. This was the first study on the spatial and temporal distribution of butterflies in NNP and further studies could be conducted to add more species and allow a depth understanding of the ecology of Nyungwe butterflies.
A taxonomic revision of the genus Pteris in tropical Africa revealed 26 species. An identification key to the species is provided. Morphological characters were used to prepare a cladistic analysis of the relevant taxa. Each species was evaluated concerning the IUCN red list status. Only Pteris mkomaziensis was considered as Near Threatened, and all other species only as Least Concern. An inventory of the ferns of Kakamega Forest / Kenya and Budongo Forest / Uganda revealed 85 species in Kakamega and 66 species in Budongo. Life form spectra were analysed and the ferns were studied for their value for bioindication.
Die pan-amazonische Baumfrosch-Gattung Osteocephalus ist unzureichend bearbeitet sowohl bezüglich ihrer Taxonomie, als auch ihrer Phylogenie. Der Status einer Reihe von Arten, die bereits oder noch nicht zu dieser Gattung gezählt werden, ist unklar und die Verwandtschaftsbeziehungen innerhalb der Gattung und zu verwandten Gattungen nicht geklärt. In dieser Arbeit wird O. cabrerai (Cochran and Goin, 1970) aus Kolumbien und Peru nochmals detailliert beschrieben und O. festae (Peracca, 1904) aus einem Anden-Vorgebirge in Ecuador revalidiert. Hyla inframaculata Boulenger, 1882, vom Unterlauf des Amazonas in Brasilien, wird in die Gattung Osteocephalus gestellt und Osteocephalus elkejungingerae (Henle, 1981) vom östlichen Andenrand in Peru wird mit Hyla mimetica (Melin, 1941) als O. mimeticus synonymisiert. Das Taxon Hyla vilarsi Melin, 1941, bisher als Synonym unterschiedlicher Arten betrachtet, wird als valide angesehen und in die Gattung Osteocephalus gestellt. Drei neue Arten werden beschrieben: Osteocephalus castaneicola aus Nord-Bolivien und Süd-Peru, O. duellmani von einer subandinen Bergkette in Süd-Ecuador und O. camufatus aus dem zentralamazonischen Teil Brasiliens. Eine phylogenetische Analyse auf Basis von bis zu neun mitochondrialen und einem Kern-Gen zeigt, dass Osteocephalus bezüglich der Gattung Tepuihyla paraphyletisch ist. Deshalb wird hier eine neue Taxonomie vorgeschlagen, die die Monophylie von Osteocephalus und Tepuihyla sichert. Eine neue Gattung, Dryaderces, wird für die Schwestergruppe von Osteocephalus aufgestellt. Die Färbung frisch metamorphosierter Jungfrösche wird als morphologische Synapomorphie von Osteocephalus angesehen. Fünf monophyletische Artengruppen werden innerhalb der Gattung aufgestellt, drei Arten der Gattung Osteocephalus (O. germani, O. phasmatus, O. vilmae) und drei der Gattung Tepuihyla (T. celsae, T. galani, T. talbergae) synonymisiert, außerdem drei Arten anderen Gattungen zugerechnet (Hyla helenae zu Osteocephalus, O. exophthalmus zu Tepuihyla und O. pearsoni zu Dryaderces gen. n.). Außerdem werden neun potentiell neue Arten identifiziert, was einer Artenzunahme von 138% im Vergleich zur derzeit bekannten Diversität entspräche. Daraus ist zu schließen, dass die tatsächliche Artenzahl weit unterschätzt wird. Unbeschriebene Arten verbergen sich vor allem unter den weit verbreiteten, polymorphen Nominatarten. Die Evolution der Fortpflanzungsstrategien innerhalb der Gattung wird im Licht der neuen Phylogenie diskutiert und ein neuer Amplexustyp (Kehlamplexus) beschrieben.