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Institute
Invasive non-native species are key components of human-induced global environmen-tal change and lead to a loss of biodiversity, alterations of species interactions and changes of ecosystem services. Freshwater ecosystems in particular are strongly affect-ed by biological invasions, since they are spatially restricted environments and often already heavily impacted by anthropogenic activities. Recent human-induced species invasions are often characterized by long-distance dispersal, with many species having extended their native distribution range within a very short time frame. However, a long term view into the past shows that biological invasions are common phenomena in nature—representing the arrival of a species into a location in which it did not originally evolve—as a result of climatic changes, geotectonic activity or other natural events. Once a species arrives in a new habitat, it may experience an array of novel selection pressures resulting from abiotic and biotic environmental factors and simultaneously act as a novel selective agent on the native fauna. Consequences of species invasions are manifold. My thesis, which combines seven studies on different aspects of biological invasions, aims to explore the influence of abiotic stressors and biotic interactions during species introductions and range expansions, as well as the consequences of biological invasions on evolutionary and ecosystem processes.
The first part of my thesis examines human-induced biological invasions, dealing with basic ecological characteristics of invaded ecosystems, novel predator-prey interactions, functional consequences of species invasions and certain behavioral traits that may contribute to the invasiveness of some species. The second part of my thesis examined distribution patterns and phenotypic trait divergence in species that historically invaded new geographical areas. I investigated variation of abiotic and biotic selection factors along a stream gradient as well as ecological and evolutionary consequences of species invasions to extreme habitats. The results highlight the importance of simultaneously considering processes involved in natural invasions and during human-induced invasions to understand the success of invading species.
We often lack detailed information on the impacts of historical biological inva-sions. Also, we are currently lacking crucial knowledge about the time scales during which different mechanisms (behavioral flexibility, plastic phenotypic changes, and ge-netic adaptation) play a role during biological invasions and affect species exchange and establishment. Comparative analyses of historical, natural invasion and recent (man-made) invasions can provide insights into the relative importance of the processes governing adaptation to abiotic stressors and selection resulting from biotic interactions. Beyond their negative effects, the establishment of invasive species and the subsequent range expansion represent “natural experiments” to investigate fundamental questions in ecology and evolution. My comparison of natural and human-induced biological invasions revealed that in many cases preadaptation to altered abiotic conditions plays a key role during early stages of invasions and range expansions. Considering the evolutionary history of invasive species and the evolutionary history of the recipient native fauna might therefore help predict the consequences of biological invasions for the ecosystem under consideration and the future success of the invading species. This knowledge can also be implemented when formulating conservation strategies, including methods to mitigate and manage human-induced biological invasions.
The phylogeny of the genus Gazella and the phylogeography and population genetics of arabian species
(2014)
Biodiversity is caused by a fundamental evolutionary process: speciation. When species can spread into new habitats and are allowed to colonize new ecological niches, speciation can become accelerated and is then called radiation. This can happen, e.g., when formerly separated land masses become connected. A prime example of such a scenario is the Arabian Peninsula that connects Africa and Asia since the Oligocene (approx. 30 Ma ago). Since then, the peninsula promoted several faunal exchanges between both continents. The mammalian genus Gazella is an excellent candidate for investigating this faunal exchange. Species are distributed on both, the African and Asian continent as well as on the Arabian Peninsula that is located in between. The aim of my thesis was to cast new light on the evolution and speciation of the genus and, furthermore, to evaluate the currently problematic taxonomy to infer suggestions for improved conservation actions for threatened gazelle species. Therefore, I investigated the taxon Gazella genetically and identified factors that promoted the speciation of this diverse genus. I assessed intraspecific genetic variability for species that inhabited the Arabian Peninsula to infer the past demography of those species and to estimate the history of species divergence and past population parameters.
In the first part of my thesis I inferred a mitochondrial phylogeny based on cytochrome b gene sequences using samples of all nine extant species of Gazella and also of closely related taxa (chapter 2). Besides the monophyly of the genus Gazella two reciprocally monophyletic clades were detected that evolved in allopatry: one predominantly African and one predominantly Asian clade. Within both clades species pairs could be inferred with species being ecologically adapted to different habitats: one species is a desert-dweller (probably the ancestral character state combination), while the other one is adapted to rather mountainous and humid habitats. These adaptations also correlate with the behavior of the species with the mountainous forms being sedentary, territorial and living in small groups and the desert forms being migratory, non-territorial and living in larger herds.
The second part of my thesis focuses on the Arabian gazelle species. In a study about G. subgutturosa I could show that the Arabian form G. marica (sand gazelle)—previously recognized as a subspecies of G. subgutturosa—is genetically distinct from the nominate form (chapter 3). Moreover, a phylogenetic tree based on cytochrome b gene sequences revealed a polyphyly of G. subgutturosa and G. marica with sand gazelles being more closely related to G. leptoceros and G. cuvieri of North Africa. Consequently, I suggested the restoration to full species level for G. marica corroborating earlier conservation practices of breeding both taxa separately in captivity.
In case of G. dorcas such a genetic differentiation could not be detected (chapter 4). Despite the large distribution range from Mali in the west to Saudi Arabia in the east only low genetic variation was detectable in mitochondrial sequence data. Statistically parsimony network analyses revealed pronounced haplotype sharing across regions. Using a coalescence approach I observed a steep population decline that started about 25,000 years ago and which is still ongoing. The decline could be correlated with human hunting activities in the Sahara. Hence, hunting of G. dorcas (already in ancient times) had a much larger impact on gazelle populations than previously thought and even led to the extinction of the Arabian form of G. dorcas.
In chapter 5 of my thesis I provided a rigorous test to genetically distinguish between the potential species G. gazella and G. arabica. Previously recognized as a single species mitochondrial sequence analyses provided first hints for the separation of both taxa. But without the investigation of nuclear loci the observed pattern could also be the result of male biased dispersal combined with female philopatry. Therefore, I amplified mitochondrial sequence markers and nuclear microsatellite loci for both taxa and found support for the earlier view of two separate species. No signs of recurrent gene flow could be detected between neighboring populations of G. arabica and G. gazella. The split of both species could be estimated one million years ago and the recommendation of breeding both taxa separately in captivity for conservation purposes is fully justified.
Several populations of G. arabica suffer from a severe decline. In chapter 6 I asked whether the population occurring on the Farasan archipelago—being at stable individual numbers for decades—may serve as potential source for future reintroduction on the Arabian mainland, although the gazelles show a reduced body size. Analyzing the genetic differentiation of Farasan gazelles, a genetic cluster could be inferred being endemic to the archipelago. However, only approx. 70% of Farasan individuals were assigned to this specific cluster, while the others showed at least intermediate or even complete assignment to the mainland cluster. This indicates ongoing introgression that is probably mediated by human translocations of gazelles from and onto the islands. Considering the uniform dwarfism of Farasan gazelles, reasons for the smaller body size might be direct consequences of resource limitations, i.e., phenotypic plasticity. If the population decline on the mainland will hold on Farasan gazelles could serve as stocks for future reintroductions.
The process of urbanization is one of the major causes of the global loss of biodiversity; however, cities nowadays also have the potential to serve as new habitats for wildlife. The European rabbit (Oryctolagus cuniculus, L. 1758) is a typical example of a wildlife species that reaches stable population densities in cities. Due to intense plant and soil damages, German city authorities aim to control high rabbit densities through the application of a yearly hunting regime (e. g., in Munich, Berlin or Frankfurt am Main). In contrast, population densities of O. cuniculus are on decline in German rural areas, i. e., numbers of yearly hunting bags decreased. The aim of my doctoral thesis was to answer the following research questions: Do population densities of the European rabbit correlate with the intensity of urbanization in and around Frankfurt am Main and if so, which factors play a role in varying densities? How are burrow construction behaviors and group sizes, daytime activity patterns and anti-predator behaviors as well as communication behaviors of this mammal affected by urbanization?
In my first study, I focused on population dynamics across 17 different study sites in and around Frankfurt. As one of yet few studies, I invented an approach that quantified the intensity of urbanization (degree of urbanity) of each study site base on four variables: (1) intensity of anthropogenic disturbance per min and ha, (2) number of residents within a radius of 500 m, (3) proportion of artificial ground cover and (4) numbers of anthropogenic objects per ha. Spearman rank correlations confirmed that with increasing degree of urbanity also rabbit and burrow densities increased. The access to dense shrubs, bushes etc. as suitable sites for burrow construction is the most determining factor for rabbit abundances, and therefore I presumed different densities along the rural-to-urban gradient to be driven by shifts in the availability of thick vegetation.
In the second study, I calculated two indices that in both cases classified burrows to be either accumulated, evenly or randomly distributed within study sites. Additionally, in cooperation with local hunters the number of burrow entrances and animals that occupy the same burrow had been determined during the hunting season. With increasing degree of urbanity burrow distribution patterns shifted from accumulated in rural areas towards more evenly distributed within the city center of Frankfurt. This is a clear sign for an increasing access to sites suitable for burrow construction along the rural to-urban gradient. Additional Spearman rank correlations revealed that the external dimensions of burrows decreased (shorter distances between entrances) and that burrows became less complex (fewer entrances) along the rural-to-urban gradient. In accordance, the number of rabbits that commonly shared the same burrow system was highest within rural areas, whereas I found mainly pairs and single individuals within highly urbanized study sites.
In the last study I compared activity patterns, burrow use and percentages of anti-predator behaviors from one hour before sunrise until one hour after sunset of rural, suburban and urban rabbit groups. A linear mixed model (LMM) and Spearman rank correlations confirmed that rabbits located at urban and suburban sites spent more time outside their protective burrows compared to their rural conspecifics. At suburban sites, individuals invested the least amount of time in anti-predator behavior. Results of this third study gave evidence that suburban rabbit populations on one hand benefit from less predation pressure by natural predators in comparison to rural sites, whereas on the other hand are exposed to less intense disturbance by humans compared to urban study sites.
The last study focused on the effects that urbanization had on the latrine-based communication behavior of rabbits. As many other mammals, O. cuniculus exchange information via the deposition of excreta in latrines, and depending on the intended receiver(s), latrines are either formed in central areas for within-group communication or at territorial boundaries, e. g., for between-group communication. The relative importance of within- vs. between-group communication depends on, amongst other factors, population densities and group sizes which I proved both to shift along the considered rural-to-urban gradient. I determined latrine sizes, latrine densities and latrine utilization frequencies relative to their distance to the nearest burrow at 15 different study sites. Latrine densities and utilization frequencies increased with increasing distance from the burrow in suburban and urban populations whereas at rural sites, largest latrines and those containing the most fecal pellets were close to the burrow, suggesting that within-group communication prevailed.
To sum up, for the first time, I was able to relate shifts in the ecology and behavior of the European rabbit as adaptations to a gradual anthropogenic habitat alteration that are typical for “urban exploiters”. Especially the suburban habitat provides high landscape heterogeneity (“edge habitat“) which is essential for high and stable rabbit populations. Moreover, here, comparably low human disturbance and predation pressure are given in contrast to the agriculturally transformed, open landscapes which are nowadays typical for most rural areas in central Europe. I argue that this mainly leads to the observed behavioral changes along the rural-to-urban gradient. Future plans for rural land management actions should aim to increase refuge availability by generating networks of ecotones. This would also benefit species that depend on similar ecosystem structures as the European rabbit and are on decline in Germany.