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Veränderungen in dem komplexen Wirkungsgefüge eines Agrarökosystems können erhebliche Auswirkungen auf die lokale Biozönose zur Folge haben. Die Überdachung von Obstkulturen mit Netzen oder Folien zum Schutz vor Hagel und Regen stellt eine solche Veränderung dar. Im Rahmen dieser Dissertation wurde anhand einer biozönotischen Risikoanalyse der Einfluss intensiver Landnutzung in Obstkulturen sowie der Einfluss von Kulturschutzeinrichtungen auf die drei Gilden tagaktive Greifvögel, insektivore Vögel und Arthropoden untersucht. Greifvögel, insektivore Vögel und räuberische Arthropoden üben als Prädatoren wichtige Regulationsfunktionen im Nahrungsnetz eines Ökosystems aus. Arthropoden stellen zudem eine wichtige Nahrungsressource dar. Arten aller drei Gilden gelten als Bioindikatoren für Veränderungen im Ökosystem. Phytophage Arthropoden können landwirtschaftlich genutzte Monokulturen erheblich schädigen, weshalb die konventionelle Landwirtschaft zur gezielten Tötung solcher Schädlinge Insektizide einsetzt. Pestizidbehandlungen haben allerdings oft auch Auswirkungen auf viele Nützlinge und andere Organismen im Agrarökosystem.
Die visuelle Erfassung beider Vogelgilden sowie das Fangen der Arthropoden mit Boden- und Flugfallen erfolgte von März bis Juli in den Jahren 2011-2013 auf fünf Untersuchungsflächen im rheinland-pfälzischen Obstanbaugebiet Mainz-Bingen. Es wurden zwei benachbarte Apfelkulturen (eine Kontrollfläche und eine Versuchsfläche mit Hagelschutznetz) und zwei benachbarte Kirschkulturen (eine Kontrollfläche und eine Versuchsfläche ab 2012 mit Folien-Netz-Überdachung) sowie eine nahegelegene Streuobstfläche im lokalen NSG Höllenberg als naturnahe Kontrollfläche untersucht. Zusätzlich wurden im ersten Untersuchungsjahr vom 15. März bis 28. Juli 2011 auf allen Flächen die Ergebnisse einer täglichen automatischen akustischen Erfassung durch ein Stereo-Aufnahmegerät („Songmeter 2“, Wildlife Acoustics) mit denen einer wöchentlichen rein visuellen Erfassung der Vögel verglichen. Es gab keine signifikanten Unterschiede in Detektionseffizienz und Arterfassung der Avifauna zwischen beiden Methoden. Die lokale α-Diversität nach Simpson unterschied sich ebenfalls nicht signifikant zwischen beiden Methoden. Das akustische Monitoring detektierte mehr seltene (=weniger als zehn Funde im Untersuchungszeitraum) Vogelarten; 29% der Arten wurden ausschließlich akustisch nachgewiesen und knapp 13% ausschließlich visuell. Sieben Vogelarten unterschieden sich signifikant in ihrer ermittelten Abundanz zwischen beiden Methoden: Bachstelze, Feldlerche, Mauersegler und die Greifvögel Mäusebussard und Turmfalke waren besser bzw. der Schwarzmilan ausschließlich mit dem visuellen Monitoring zu erfassen, während der Fasan ausschließlich durch das akustische Monitoring nachgewiesen werden konnte. Für die Abundanzschätzung von 48 Vogelarten war es unerheblich, ob sie akustisch oder visuell erfasst wurden. Da seltene Arten bei biozönotischen Untersuchungen keine wesentliche Rolle spielen und die Auswertung der Akustikaufnahmen sehr zeitaufwändig war, wurden für die Risikoanalyse nur die visuell ermittelten Daten berücksichtigt.
Für die Greifvogel-Gilde wurden sechs Arten nachgewiesen, fünf auf der Kirschkontrollfläche und jeweils vier Arten auf den anderen Flächen. Die drei häufigsten Arten waren Mäusebussard, Turmfalke und Schwarzmilan. Greifvögel wurden im Luftraum der Flächen oder auf Sitzwarten wie Zäunen, Pfählen, Bäumen und Kulturschutzeinrichtungen bei der Nahrungssuche oder beim Revierverhalten beobachtet. Es konnte kein Einfluss der Landnutzung auf Greifvögel aufgezeigt werden, Diversität und Abundanz unterschieden sich nicht zwischen den Obstkulturen und der naturnahen Streuobstfläche im NSG. Ein Einfluss von Kulturschutzeinrichtungen auf Greifvögel konnte ebenfalls nicht nachgewiesen werden, die überdachten Flächen wurden genauso oft frequentiert wie die Kontrollflächen. Greifvögel überflogen innerhalb ihrer großen Aktionsräume auch die überdachten Obstkulturen zur Nahrungssuche und wurden weiterhin bei der Ansitzjagd am Rand der Versuchsflächen gesichtet. Zudem wurde der Turmfalke beim Ansitzen unter der Folien-Netz-Überdachung der Kirschkultur sowie beim Fressen auf dieser Überdachung sitzend beobachtet. Für die Insektivoren-Gilde wurden 52 Vogelarten nachgewiesen. Die Streuobstfläche im NSG wies die höchste Artenzahl von 40 auf, gefolgt von der Apfelkontrollfläche mit 27 Arten. Die Apfelversuchsfläche wies dagegen eine geringere Artenzahl von 19 auf, während die Artenzahlen beider Kirschkulturen mit 19 und 18 annähernd gleich gewesen sind. Die zehn häufigsten Arten waren in Reihenfolge ihrer Abundanz Kohlmeise, Star, Rabenkrähe, Amsel, Mauersegler, Bachstelze, Blaumeise, Buchfink, Feldlerche und Stieglitz. Insektivore Vögel wurden überwiegend nahrungssuchend am Boden und in Bäumen der Flächen oder beim Revierverhalten wie Singen, Rufen und Vigilanz auf Sitzwarten Zäunen, Pfählen sowie Kulturschutzeinrichtungen beobachtet. Die intensive Landnutzung der Obstkulturen führte im Vergleich zur naturnahen Streuobstfläche im NSG sowohl auf der Apfel- als auch auf der Kirschkontrollfläche zu einer hochsignifikant geringeren monatlichen Vogelartenzahl. Eine signifikant niedrigere Abundanz der insektivoren Vögel wies jedoch nur die Kirschkontrollfläche auf. Es wurden negative Effekte der intensiven Landnutzung auf die monatliche Abundanz von Gartenrotschwanz, Amsel und Blaumeise nachgewiesen, welche in den Obstkulturen hochsignifikant seltener beobachtet wurden. Der Einsatz von Kulturschutzeinrichtungen führte lediglich beim Hagelschutznetz zu einer zusätzlichen signifikanten Verringerung der monatlichen Vogelartenzahl. Die Folien-Netz-Kombination zeigte keinen signifikanten Einfluss auf die Vogeldiversität. Die Gesamtabundanz der Insektivoren-Gilde blieb in beiden Obstkulturen von Kulturschutzeinrichtungen unbeeinflusst. Abundanzen einzelner Arten zeigten jedoch abweichende Ergebnisse: Die Ringeltaube wurde unter dem Hagelschutznetz der Apfelkultur im Vergleich zur Kontrollfläche gar nicht beobachtet. Die Kohlmeise kam unter der Folien-Netz-Überdachung der Kirschkultur signifikant seltener vor, während der Wiedehopf hier etwa zehnmal häufiger vorkam als auf der Kirschkontrollfläche und der Streuobstfläche im NSG Höllenberg. Entscheidender Faktor für die starke Nutzung der Kirschkulturen waren für den Wiedehopf die vorhandenen vegetationsfreien Bodenbereiche, in denen diese Art bevorzugt nach Nahrungsinsekten sucht. Störungen durch die bei Wind laut flatternde Folienüberdachung auf darunter nahrungssuchende Wiedehopfe wurden nicht beobachtet.
Für die Arthropoden-Gilde wurden 185963 Individuen aus 18 Gruppen gefangen. Der Großteil von 79% dieser Individuen ließ sich Springschwänzen, Ameisen, Zweiflüglern oder Käfern zuordnen. Weitere 20% verteilten sich auf Webspinnen, Asseln, Hautflügler, Milben, Doppelfüßer, Weberknechte, Schnabelkerfe und Ohrwürmer. Die restlichen sechs Arthropodengruppen stellten den restlichen Individuenanteil von 0,9%. Hinsichtlich der determinierten 12910 Käfer-Imagines aus 403 Arten waren Artenzahl, Diversität sowie Anzahl seltener Arten und Habitatspezialisten sandiger Lebensräume in allen drei Untersuchungsjahren auf der naturnahen Streuobstfläche im NSG Höllenberg am höchsten. Die über Bodenfallen ermittelte Arthropoden-Trockenbiomasse lag je nach Fläche bei 9 bis 26 Gramm pro Jahr und die über Flugfallen ermittelte Arthropoden-Trockenbiomasse bei 0,6 bis 4,8 Gramm pro Jahr. Obwohl im Mittel jährlich 5,8 Pestizidbehandlungen in den Kirschkulturen sowie 14,6 Behandlungen in den Apfelkulturen durchgeführt wurden und Insektizide dabei anteilig bis zu 57% ausmachten, konnte kein Einfluss der intensiven Landnutzung mit dem Einsatz von Pestiziden auf die Arthropoden-Trockenbiomasse nachgewiesen werden. Kulturschutzeinrichtungen zeigten ebenfalls keinen Einfluss auf die Arthropoden-Trockenbiomasse.
Diese biozönotische Risikoanalyse belegt, dass der Einsatz von Kulturschutzeinrichtungen zumindest bei Hagelschutznetzen langfristig nachweisbare negative Effekte auf die Diversität von insektivoren Vögeln bewirken kann, welche über die vorhandenen negativen Folgen der intensiven Landnutzung in Obstkulturen hinausgehen. Da intensiv bewirtschaftete Obstkulturen bereits ohne Kulturschutzeinrichtungen zu einer Verarmung der lokalen Biozönose führen, sollte aus ökologischer Sicht vor der Errichtung von Kulturschutzeinrichtungen verlässlich abgewogen werden, ob der zusätzliche Verlust an Biodiversität durch die Verbesserung von Flächenstrukturen der Obstkulturen kompensierbar ist.
The protected areas of Rwanda are facing various challenges resulting from the anthropogenic activities of the surrounding communities especially in the adjacent area to Cyamudongo isolated rain forest, which results in climate change, soil degradation, and loss of biodiversity. Therefore, this study aims to broaden current knowledge on the impact of sustainable Agroforestry (AF) on the Carbon (C) stock and Biodiversity conservation on the surroundings of Cyamudongo isolated rain forest and Ruhande Arboretum.
To understand this, the permanent sample plots (PSPs) were established mainly in the designed four transects of four km long originating on the boundary of the Cyamudongo isolated rain forest following the slope gradient ranging from 1286 to 2015 m asl. A total number of 73 PSPs were established in the Cyamudongo study area while 3 PSPs were established in the Ruhande AF plot. The Arc Map GIS 10.4 was used to design and map the sampling areas while GPS was used for localization of collected items. Statistical significance was analyzed through the R-software especially for wood and soil variables while for biodiversity indicator species, MVSP Software 3.0 was used to determine the Shannon Diversity indices and similarities among species.
In this study, I have obtained comprehensive results demonstrating that in all study areas, the various AF tree species contribute differently to C stock and C sequestration and the amount of C stored and removed from the atmosphere depends on different factors such as tree species, plantation density, growth stage, or the age of establishment, applied management practices, wood specific density (WSD), wood C concentration, and climatic conditions. The estimated quantity of sequestrated C for 2 years and 34 years AF species were 13.11 t C ha -1 yr-1 (equivalent to 48 t CO2 ha -1 yr-1) and 6.85 t ha-1 yr-1 (equivalent to 25.1 t CO2 ha -1 yr-1) in Cyamudongo and Ruhande respectively. The estimated quantity of C stored by the Ruhande AF plot is 232.94 t ha-1. In Cyamudongo, the overall C stored by the AF systems was 823 t ha-1 by both young tree species established by the Cyamudongo Project (35.84 t ha-1) and C stored by existed AF species before the existence of the Project (787.12 t ha-1). In all study areas, the Grevillea robusta was found to contribute more to overall stored C compared to other species under this study.
The tests revealed differences in terms of nutrient contents (C, N, C: N ratio, K, Na, Ca, and Mg) for various AF tree species of Cyamudongo and Ruhande study areas. The differences in terms of correlation for various variables of AF tree species in different study areas varied with tree species, age, stage of growth, and tree shape. By comparing the correlation coefficients for various tree variables for young and mature AF tree species, the results showed a high correlation variability for young species than mature or old species recorded in different environmental conditions of Cyamudongo and Ruhande study areas.
The recorded soil pH mean value across in Cyamudongo study area is 4.2, which is very strongly acidic. The tests revealed that the soil pH, C, C: N ratio, OM, NH4+, NO3-+NO2-, PO43-, and CEC were significantly (P < 0.05) different in various soil depths whereas the N was not statistically significant. The pH, N, C: N ratio, CEC, NH4+, PO43-, and Al3+ showed a significant difference across land uses whereas the C and NO3-+NO2- did not show any statistical difference. All tested chemical elements showed a statistical difference as far as altitude ranges are concerned. The only NH4+, PO43-, and CEC showed significant differences with time whereas all other remaining chemical elements did not show any statistical significance. The bulk density of soil was statistically different across land uses and altitude ranges. The soil pH was very strongly correlated with CEC, Mg, and Ca in cropland (CL) whereas it was strongly correlated in both AF and natural forest (NF) except for Mg, which was moderately correlated in AF. Furthermore, its correlation with K was strong in CL, moderate in AF while it was weak in NF. Finally, the pH correlation with Na was weak in both AF and CL whereas it was negligible in NF. The overall estimated soil C stock of the study area was 16848 t ha -1.
The sustainable AF practices changed significantly the frequency of reptiles, amphibians, and flowering plants while there was no statistical change observed on ferns with time. In terms of species richness, 16 flowering plants, 14 ferns, 5 amphibians, and 3 reptiles were recorded and monitored. These findings add to a growing body of literature on the impact of AF on the C stock, soil improvement, and Biodiversity. It is recommended that further researches should be undertaken for the contribution of other AF tree species to the C stock found in the agricultural landscape around all protected areas of Rwanda and the impact on them on the soil and biodiversity.
Due to their confinement to specific host plants or restricted habitat types, Auchenorrhyncha are suitable biological indicators to measure the quality of chalk grassland under different management practices for nature conservation. They can especially be used as a tool to assess the success of restoring chalk grassland on ex-arable land. One objective of this study was to identify the factors which most effectively conserve and enhance biological diversity of existing chalk grasslands or allow the creation of new areas of such species-rich grassland on ex-arable land. A second objective was to link Auchenorrhyncha communities to the different grassland communities occurring on chalk according to the NVC (National Vegetation Classification). Altogether 100 chalk grassland and arable reversion sites were sampled between 1998 and 2002. Some of the arable reversion sites had been under certain grazing or mowing regimes for up to ten years by 2002. Vegetation structure and composition were recorded, and Auchenorrhyncha were sampled three times during the summer of each year using a "vortis" suction sampler. Altogether 110 leafhopper species were recorded during the study. Two of the species, Kelisia occirrega and Psammotettix helvolus, although widespread within the area studied, had not previously been recognized as part of the British fauna. By displaying insect frequency and dominance as it is commonly done for vegetation communities, it was possible to classify preferential and differential species of distinct Auchenorrhyncha communities. The linking of the entomological data with vegetation communities defined by the NVC showed that different vegetation communities were reflected by distinct Auchenorrhyncha communities. Significant differences were observed down to the level of sub-communities. The data revealed a strong positive relationship between the diversity of leafhoppers species and the vegetation height. There was also a positive correlation between the species richness of Auchenorrhyncha and the diversity of plant species. In that context it is remarkable that there was no correlation between vegetation height and botanical diversity. There is a substantial decrease in Auchenorrhyncha species richness from unimproved grassland to improved grassland and arable reversion. The decline of typical chalk grassland and general dry grassland species is especially notable. Consequently, the number of stenotopic Auchenorrhyncha species which are confined to only a few habitat types, are drastically reduced with the improvement of chalk grassland. Improved grassland and arable reversion fields are almost exclusively inhabited by common habitat generalists. The decrease in typical chalk grassland plants due to improvement is mirrored in the decline of Auchenorrhyncha species, which rely monophagously or oligophagously on specific host plants. But even where suitable host plants re-colonize arable reversion sites quickly, there is a considerable delay before leafhoppers follow. That becomes especially obvious with polyphagous leafhoppers like Turrutus socialis or Mocydia crocea, which occur on improved grassland or arable reversion sites only in low frequency and abundance, despite wide appearance or even increased dominance of their host plants. These species can be considered as the most suitable indicators to measure success or failure of long term grassland restoration. A time period of ten years is not sufficient to restore species-rich invertebrate communities on grassland, even if the flora indicates an early success.
The diversity within amphibian communities in cultivated areas in Rwanda and within two selected, taxonomically challenging groups, the genera Ptychadena and Hyperolius, were investigated in this thesis. The amphibian community of an agricultural wetland near Butare in southern Rwanda comprised 15 anuran species. Rarefaction and jackknife analyses corroborated that the complete current species richness of the assemblage had been recorded, and the results of acoustic niche analysis suggested species saturation of the community. Surveys at many other Rwandan localities showed that the species recorded in Butare are widespread in cultivated and pristine wetlands. The species were readily distinguishable using morphological, bioacoustic, and molecular (DNA barcoding) features, but only eight of the 15 species could be assigned unambiguously to nominal species. The remaining represented undescribed or currently unrecognized taxa, including three species of Hyperolius, two Phrynobatrachus species, one Ptychadena species, and one species of Amietia. The diversity of the Ridged Frogs in Rwanda was investigated in two studies (Chapters III and IV). Three species of Ptychadena were recorded in wetlands in the catchment of the Nile. They can be distinguished by morphological characters (morphometrics and qualitative features) as well as by their advertisement calls and genetics. The Rwandan species of the P. mascareniensis group was shown to differ from the topotypic population as well as from other genetic lineages in sub-Saharan Africa and an old available name, P. nilotica, was resurrected from synonymy for this lineage. Two further Ptychadena species were identified among voucher specimens from Rwanda deposited in the collection of the RMCA, P. chrysogaster and P. uzungwensis. Morphologically they can be unambiguously distinguished from each other and the three other Rwandan species. A key based on qualitative morphological characters was developed, which allows unequivocal identification of specimens of all species that have been recorded from Rwanda. DNA was isolated from a Rwandan voucher specimen of P. chrysogaster, and the genetic analysis corroborated the species" distinct status.
A species of Hyperolius collected in the Nyungwe National Park was compared to all other Rwandan species of the genus and to morphologically or genetically similar species from neighbouring countries. Its distinct taxonomic status was justified by morphological, bioacoustic, and molecular evidence and it was described as a new species, H. jackie. A species of the H. nasutus group collected at agricultural sites in Rwanda was described as a new species in the course of a revision of the species of the Hyperolius nasutus group. The group was shown to consist of 15 distinct species which can be distinguished from each other genetically, bioacoustically, and morphologically.
The aerial performance, i.e. parachuting, of the Disc-fingered Reed Frog, Hyperolius discodactylus, was described. It represents a novel observation of a behaviour that has been known from a number of Southeast Asian and Neotropical frog species. Parachuting frogs, including H. discodactylus, exhibit certain morphological characteristics and, while airborne, assume a distinct posture which is best-suited for maneuvering in the air. Another study on the species addressed the validity of the taxon H. alticola which had been considered either a synonym of H. discodactylus or a distinct species. Type material of both taxa was re-examined and the status of H. alticola reassessed using morphological data from historic and new collections, call recordings, and molecular data from animals collected on recent expeditions. A northern and a southern genetic clade were identified, a divide that is weakly supported by diverging morphology of the vouchers from the respective localities. No distinction in advertisement call features could be recovered to support this split and both genetic and morphological differences between the two geographic clades are marginal and not always congruent and more likely reflect population-level variation. Therefore it was concluded that H. alticola is not a valid taxon and should be treated as a synonym of H. discodactylus.
Taxonomy and Systematics of Spiny-Backed Treefrogs, Genus Osteocephalus (Amphibia: Anura: Hylidae)
(2015)
The pan-Amazonian treefrog genus Ostecephalus is poorly understood both on a taxonomic and phylogenetic level. The status of several frogs already or not yet referred to the genus is unclear and the relationships among the genus and with respect to related genera is not understood. In this work O. cabrerai (Cochran and Goin, 1970) from Colombia and Peru is redescribed and O. festae (Peracca, 1904) from the foothills of the Andes in Ecuador is revalidated. Hyla inframaculata Boulenger, 1882, from the lower Amazon in Brazil, is reallocated to Osteocephalus and O. elkejungingerae (Henle, 1981) from the Andean foothills in Peru is shown to be a synonym of Hyla mimetica (Melin, 1941), the valid name being O. mimeticus. Hyla vilarsi Melin, 1941 is considered a valid species in the genus Osteocephalus and revalidated from the synonymies of several other frogs. Three new species, O. castaneicola from northern Bolivia and southern Peru, O. duellmani from a sub-Andean mountain range in southern Ecuador, and O. camufatus from central Amazonian Brazil, are described. A phylogenetic analysis based on up to nine mitochondrial genes and one nuclear one reveals the paraphyly of the genus as previously understood with respect to the genus Tepuihyla. A new taxonomy is proposed, securing the monophyly of Osteocephalus and Tepuihyla by rearranging and redefining the content of both genera. A new genus, Dryaderces, is erected for the sister group of Osteocephalus. The colouration of newly metamorphosed individuals is proposed as a morphological synapomorphy for Osteocephalus. Five monophyletic species groups within Osteocephalus are recognized, three species of Osteocephalus (O. germani, O.rnphasmatus, O. vilmae) and three species of Tepuihyla (T. celsae, T. galani, T. talbergae) synonymized and three species (Hyla helenae to Osteocephalus, O.rnexophthalmus to Tepuihyla and O. pearsoni to Dryaderces gen. n.) reallocated. Furthermore, nine putative new species are flagged (an increase to 138% of the current diversity), an indication that species numbers are largely underestimated, with most hidden diversity centred on widespread and polymorphic nominal species. The evolutionary origin of breeding strategies within Osteocephalus is discussed in the light of this new phylogeny and a novel type of amplexus (gular amplexus) is described.
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.
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.
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.
Galerucinae, Latreille 1802 is the second largest subgroup of chrysomelidae. 1837 Chervrolat described the taxon Ootheca, which has originally only one listed species. Nearly 200 years all galerucinae with a "compact" bodyshape, a broad pronotum, a convex dorsum , short antennae and short legs were assigned to Ootheca. When I started a revision of Ootheca, this taxon included 38 species. Comparing morphological characters of the exoskeleton combined with the depiction/description of characteristic structures of the male genitalia allowed a detailed description of the genus Ootheca and its species. After the revision 9 valid species remained in Ootheca, 4 are described to be new, 13 species were transferred to other valid described genera and 10 species remained, because of a lack of unambiguous assignment. The examination of the median lobe additionally enables me to describe three sister taxa: Oothecoides (6 species), Ootibia (5 species ) und Oosagitta (6 species).
Microbial pollution of surface waters poses substantial risks for public health, amongst others during recreational use. Microbial pollution was studied at selected sampling sites in rivers Rhine, Moselle and Lahn (Germany) on the basis of commonly used fecal indicator organisms (FIO) indicating bacterial (Escherichia coli, intestinal enterococci) and viral (somatic coliphages) fecal contamination. In addition, blaCTX-Mantibiotic resistance genes (ARG) were quantified at twosites in river Lahn and were used as markers for tracking the spread of antibiotic resistance in the aquatic environment. The impact of changes in climate-related parameters on FIO was examined by studying monitoring results of contrasting flow conditions at rivers Rhine and Moselle. Analyses at all studied river sites clearly indicate that high discharge and precipitation enhance the influx of FIO, ARG and thus potentially (antibiotic resistant) pathogens into rivers. In contrast, a decrease in hygienic microbial pollution was observed under high solar irradiation and increasing water temperatures. Based on identified contributing key factors, multiple linear regression (MLR) models for five sites at a stretch of river Lahn were established that allow a timely assessment of fecal indicator abundances. An interaction between abiotic and biotic factors (i.e. enhanced grazing pressure) considerably contributed to the formation of seasonal patterns among FIO abundances. This was enhanced during extraordinary low flow conditions in rivers with pronounced trophic interactions, clearly hampering a transfer of model approaches between rivers of different biological and hydrological characteristics. Bacterial indicatorswere stronger influenced by grazing pressure than phages. Hence, bacterial indicators alone do not sufficiently describe viral pollution in rivers. BlaCTX-Mgenes were omnipresent in Lahn River water and corresponded to distribution patterns of FIO, indicating fecal sources. Agriculture and waste watertreatment plant effluents contributed to ARG loads and participants in non-bathing water sports were found to be at risk of ingesting antibiotic resistant bacteria (ARB) including ARG, bearing the risk of infection or colonization. Results of the present study highlight the need to be aware of such risks not only in designated bathing waters. ARG abundance at both riverine sampling sites could largely be explained by E. coliabundance and may thus also be incorporated into multiple regression models using E. colispecific environmental predictors. It can be expected that the frequency of short-term microbial pollution events will increase over the next decades due to climate change. Several challenges were identified with regard to the implementation of early warning systems to protect the public from exposure to pathogens in rivers. Most importantly, the concept of the Bathing Water Directive (Directive 2006/7/EC) itself as well as the lack of harmonization in the regulatory framework at European Union (EU) level are major drawbacks and require future adjustments to reliably manage health risks related to microbial water pollution in waters used in multifunctional ways.