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To uncover the genetic structure of Populus euphratica forests along the Tarim River in Xinjiang, China, a PCR set of eight microsatellite markers was established. 18 primer pairs originally developed for P. tremuloides and P. trichocarpa were screened for amplification in P. euphratica. The eight most variable loci were selected for further genotyping experiments. Subsequently, two multiplex PCR assays, each containing four loci, were set up and optimized. Three populations containing altogether 436 trees were used to characterize the selected loci. The set was found to be moderately polymorphic (mean expected heterozygosity = 0.57). The resolution was sufficient to discriminate even siblings with high confidence (PID = 1.81x10-5). Cumulative exclusion probabilities were 0.89 (single parent), 0.98 (paternity), and 1.00 (parent pair) and proved the set’s suitability for parentage analysis. Practical and theoretical analysis of consequences of genotyping errors in this semi-clonal plant showed that the vast majority of errors (62.1%) lead to division of identical genotypes. Merging of different genotypes was found to be a very rare case (0.4%). This always leads to an overestimation of genotypes. A similarity threshold of one allele difference between two genotypes to be regarded as being identical lead to an underestimation of clonal richness and genotype number of one per cent compared to an overestimation of more than 20 per cent without such a threshold. Allowing a certain amount of variation is therefore expected to reflect the clonal structure better than an analysis that considers exact matches only. Using a combination of morphological and molecular analyses, a first study demonstrated that root suckers are clearly distinguished from seedlings in their root architecture. Root suckering starts when trees are 10–15 years old and bridges distances of up to 40 m at a time. Root suckers depend on their parent tree for at least five years and are expected to have a higher mortality than generatively grown trees. Molecular analysis of old growth stands revealed a highly variable proportion of clonal growth between different stands. In the study area, the proportion of clonality decreases with distance to the main river bed (R = 0.31 at the site closest to the main river, R = 0.97 at the site farthest away from the river). An analysis of the history of river movements at different sites indicates a dependency of clonal growth on the frequency of ground water replenishment by the yearly floods. Genetic differentiation among the stands in the study area is low (FST = 0.055), and isolation by distance was not detectable (P = 0.058). Also, the river does not function as a vector for directed gene flow in downstream direction (P > 0.11). The forests are therefore considered to be one large panmictic metapopulation with unrestricted gene flow. Clonal growth does not lead to higher final stand densities (P = 0.99) and is obviously not of crucial importance for stand survival. Furthermore, analysis of vitality measures and size differences indicate that root suckers are in disadvantage both in vitality and in survival rate compared to seedlings. In this light, a possible function of clonal growth as a luxury strategy to enhance a genetic individual’s reproduction success under good site conditions can be discussed. The genetic structure of the (meta)population bears direct implications for management and conversation of the Tugai forest in Xinjiang. Due to the low degree of differentiation and the unhindered gene flow even small, fragmented, or isolated populations have conservational value, thereby clearly answering the SLOSS question (a single large or several small protected areas) in the latter sense. More than that, non-clonal stands with the highest amount of genotypic diversity can be easily identified on satellite and aerial images. Selection of such stands for conservation is therefore possible without expensive and time-consuming molecular analyses.
Myxomycetes are fungus-like protists of the supergroup Amoebozoa found to be abundant in all terrestrial ecosystems. Mainly based on its macroscopically visible fruit bodies, our knowledge on ecology and diversity of myxomycetes is better than for most other protistean groups, but there is still a lacking knowledge about global diversity patterns since tropical regions, especially the old world tropics, are still understudied. In this thesis a combination of classical ecological analyses and modern molecular methods were used to expand the current knowledge on myxomycete diversity and biogeography in the Paleotropics. A number of surveys in the Philippine archipelago are conducted to provide and to add information about the distribution of myxomycetes in the Southeast Asian region. A combination of field collecting and ca. 2500 moist chamber cultures from four unexplored areas in the Philippines, namely, the Bicol Peninsula (746 records, 57 taxa), Puerto Galera (926 records, 42 taxa), Quezon National Park (205 records, 35 taxa), and Negros Province (193 records, 28 taxa), now brings the number of species recorded for Philippines to 150; with one record, Stemonaria fuscoides, noted as new for the Asian Paleotropics. Collecting localities that have more diverse plant communities showed as well higher species diversity of myxomycetes. In congruence with studies from the Neotropical forests, it seems also that anthropogenic disturbances and the type of forest structure affect the occurrence of myxomycetes for the Philippines. Another survey carried out in another paleotropical region, the highlands of Ethiopia, revealed a total of 151 records, with all 39 species found as new for the country. Three records of Diderma cf. miniatum with a strong bright red peridium and one record of Didymium cf. flexuosum with a conspicuous broad reticulation in the spore ornamentation were described and barcoded, since both may represent morphospecies new to science. A number of rarely recorded species, like Didymium saturnus, Metatrichia floripara, Perichaena areolata, and Physarina echinospora showed that resembling to its unique flora, the east African mountain ranges harbor a diverse and distinctive myxomycete assemblage. One incentive of this study was to compile a solid large dataset for the Paleotropical region that is comparable to data obtained from comprehensive studies performed in the Neotropical areas a decade ago. A total of eight surveys (with four comprehensive regional surveys, two from lowland and two from highland, for each region, the Neo- and the Paleotropics) were used, to compare the myxomycete assemblages of both regions. Each survey comes from a region with fairly homogenous vegetation, and includes specimens from both field and moist chamber cultures component. A statistical analysis of species accumulation curves revealed that only between 70 and 95% of all species to be expected have been found. Even for >1000 specimens per survey these figures seem hardly to increase with increasing collection effort, since a high proportion of species is always represented by a single or a few records only. Both ordination and cluster analysis suggests that geographical separation explains differences in species composition of the myxomycete assemblages much better than elevational differences. 5 The molecular component of this thesis is a phylogeographic study of the widely distributed tropical myxomycete Hemitrichia serpula. It is a morphologically distinct species with golden-yellow fructifications forming a reticulum. However, subtle variation in spore ornamentation points to cryptic speciation within this myxomycete. Using two independent molecular markers, 135 partial sequences of the small subunit (SSU) rRNA (a nuclear but extrachromosomal gene) and 30 partial sequences of the elongation factor 1 alpha gene (EF1A) (a nuclear gene), a study of 135 Hemitrichia serpula specimens collected worldwide revealed the existence of four clades that are likely to represent reproductively isolated biospecies, since each clade shows a unique combination of SSU and EF1A genotypes. A Mantel test with the partial SSU sequences indicated geographical differentiation, giving a correlation coefficient of 0.467 between the pairwise computed geographic and genetic distances, compared with the 95% confidence interval from 999 permutations (-0.013 to 0.021). Biogeographical analysis of the 40 SSU ribotypes showed clear intraspecific variation and geographic differentiation demonstrating a limited gene flow among the world population. We argue that the distribution of cryptic species in the different clade can be explained by ongoing, but still incomplete speciation. An event-based ancestral area reconstruction using the software S-DIVA employed in RASP showed that the probable origin of the ribotypes was a global dispersal event in the Neotropics. Additional species distribution models that were implemented for the three most prominent clades show different putative ranges. As such H. serpula supports the moderate endemicity hypothesis for protists. In summary, myxomycete assemblages in the Paleotropics (1) displayed a higher diversity than for Neotropical forests, (2) harbor unique taxa that differentiates those assemblages in spite of the expected similar macroecological all over the Tropics, (3) are affected by geographical barriers that likely causes speciation both at a morphospecies and biospecies level, and (4) follow the ubiquitous model in the sense that gene flow mediated by long-distance dispersal of spores is high enough that a species can fill out its entire putative range, but (5) the gene flow is not high enough to prevent variation in regional gene pools, which may lead to speciation and is better explained by the moderate endemicity model. Our data are still too limited to draw a comprehensive picture of the diversity of tropical myxomycetes, but the baseline information compiled with the aid of both classical ecology and molecular approaches from this study are first major steps towards this goal.
The present study deals with the spread and population genetics of the invasive Asian bush
mosquito Ae. japonicus in Europe and Germany. Since the first detection of Ae. japonicus
in Europe in 2000, the species spread rapidly through Europe, either actively by flying or
passively by human activities. In 2017, four confirmed populations of Ae. japonicus existed
in Europe. The largest population covered western Germany, parts of France, Switzerland,
Liechtenstein, Austria and Italy. The most northern population around Hanover, Germany,
did not spread since 2013. A very small population existed in Belgium and the second largest
population covered parts of Austria, Italy, Slovenia, Croatia and Hungary. By 2019, Ae.
japonicus had established in 15 European countries.
Most of the monitoring programmes in Europe dealing with the distribution and spread of
Ae. japoncus investigate cemeteries for juvenile stages. However, activities are not
harmonised, e.g. regarding numbers of investigated collection sites and declaration of
negative sites, making data comparison between different studies difficult. Therefore,
suggestions for a standardised Ae. japonicus monitoring method have been developed and
provided.
In the present study, 445 individuals of Ae. japonicus originating from five different
European countries were investigated for population genetic analyses by sequencing parts
of the nad4 gene and genotyping seven polymorphic microsatellite loci. In total, 16 different
nad4 haplotypes were identified with haplotype H1 being the most common and widespread
one through all populations.
Within Germany, Ae. japonicus has been spreading immensely over the last decade. Even
though the present results (2017) demonstrate incipient genetic admixture of populations as
compared to previous studies (2012-2015), no complete genetic mixture has taken place yet.
The populations of Ae. japonicus still fall into two genetic clusters, but the genetic diversity
on individual level had increased considerably (from three nad4 haplotypes in 2012 to 12
according to the present thesis). Both additional introductions and mutation are possible
reasons, but determining the origin of the German populations is not possible anymore.
In the years following the invasion of Germany, Ae. japonicus spread to southeastern
Europe. In 2013, it established in Croatia, in 2017 in Bosnia and Herzegovina and in 2018
in Serbia. In the current study, immature stages of Ae. japonicus were found at 19 sites in
Croatia, two sites in Bosnia and Herzegovina and one site in Serbia. The population genetic
analyses indicate at least two independent introductions in that area. Aedes japonicus collected west of Orahovica (Croatia) seemed to be genetically similar to samples previously
investigated from Southeast Germany/Austria and Austria/Slovenia. By contrast, samples
from east of Orahovica, together with those from Serbia and Bosnia and Herzegovina, were
characterised by another genetic make-up, but their origin could not be determined.
In 2021, individuals of Ae. japonicus were detected at two collection sites in the Czech
Republic for the first time: Prachatice close to the Czech-German border and Mikulov on
the Czech-Austrian border. Population genetics and comparison of genetic data showed a
close relationship of the Prachatice samples to a German population, while for Ae. japonicus
from Mikulov close relatives could not be identified.
In the future, the global spread and establishment of invasive mosquitoes through
international trade and travel will increase. Potential vectors, like the Asian bush mosquito
Ae. japonicus, can become a problem in Europe and Germany, especially in the course of
global warming which supports pathogen transmission. Monitoring the known populations
and identifying introduction and migration routes are therefore essential for vector
managing.