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Korrelation zwischen der genetischen und der funktionellen Diversität humaner Bitterrezeptoren
(2013)
Der Mensch besitzt ~25 funktionelle Bitterrezeptoren (TAS2R), die für die Wahrnehmung potenziell toxischer Substanzen in der Nahrung verantwortlich sind. Aufgrund der großen genetischen Variabilität der TAS2R-Gene könnte es eine Vielzahl funktionell unterschiedlicher TAS2R-Haplotypen geben, die zu Unterschieden der Bitterwahrnehmung führen. Dies konnte bereits in funktionellen Analysen und sensorischen Studien für einzelne Bitterrezeptoren gezeigt werden. In dieser Arbeit wurden die häufigsten Haplotypen aller 25 Bitterrezeptoren verschiedener Ethnien funktionell charakterisiert. Das Ziel war eine umfassende Aussage über die funktionelle Diversität der TAS2Rs, die die molekulare Grundlage für individuelle Bitterwahrnehmung bildet, treffen zu können. Fehlende Varianten wurden aus genomischer DNA kloniert oder durch gezielte Mutagenese bereits vorhandener TAS2R-Konstrukte generiert. Die funktionelle Analyse erfolgte mittels Expression der TAS2R-Haplotypen in HEK293TG16gust44 Zellen und anschließenden Calcium-Imaging-Experimenten mit zwei bekannten Agonisten. Die Haplotypen der fünf orphanen TAS2Rs wurden mit über hundert Bitterstoffen stimuliert. Durch die gelungene Deorphanisierung des TAS2R41 in dieser Arbeit, wurden für die 21 aktivierbaren TAS2Rs 36 funktionell-unterschiedliche Haplotypen identifiziert. Die tatsächliche funktionelle Vielfalt blieb jedoch deutlich hinter der genetischen Variabilität der TAS2Rs zurück. Neun Bitterrezeptoren wiesen funktionell homogene Haplotypen auf oder besaßen nur eine weltweit vorherrschende Variante. Funktionell heterogene Haplotypen wurden für zwölf TAS2Rs identifiziert. Inaktive Varianten der Rezeptoren TAS2R9, TAS2R38 und TAS2R46 sollten die Wahrnehmung von Bitterstoffen wie Ofloxacin, Cnicin, Hydrocortison, Limonin, Parthenolid oder Strychnin beeinflussen. Unterschiedlich sensitive Varianten, besonders der Rezeptoren TAS2R47 und TAS2R49, sollten für Agonisten wie Absinthin, Amarogentin oder Cromolyn ebenfalls zu phänotypischen Unterschieden führen. Wie für den TAS2R16 bereits gezeigt, traten Haplotypen des funktionell heterogenen TAS2R7 und TAS2R41 ethnien-spezifisch auf, was auf lokale Anpassung und verschiedene Phänotypen hinweisen könnte. Weiterführend muss nun eine Analyse der funktionell-variablen TAS2Rs in sensorischen Tests erfolgen, um ihre phänotypische Relevanz zu prüfen. Die Analyse der funktionsmodulierenden Aminosäurepositionen, z.Bsp. des TAS2R44, TAS2R47 oder TAS2R49, könnte weiterführend zum besseren Verständnis der Rezeptor-Ligand- und Rezeptor-G-Protein-Interaktion beitragen.
Human-induced alterations of the environment are causing biotic changes worldwide, including the extinction of species and a mixing of once disparate floras and faunas. One type of biological communities that is expected to be particularly affected by environmental alterations are herb layer plant communities of fragmented forests such as those in the west European lowlands. However, our knowledge about current changes in species diversity and composition in these communities is limited due to a lack of adequate long-term studies. In this thesis, I resurveyed the herb layer communities of ancient forest patches in the Weser-Elbe region (NW Germany) after two decades using 175 semi-permanent plots. The general objectives were (i) to quantify changes in plant species diversity considering also between-community (β) and functional diversity, (ii) to determine shifts in species composition in terms of species’ niche breadth and functional traits and (iii) to find indications on the most likely environmental drivers for the observed changes. These objectives were pursued with four independent research papers (Chapters 1-4) whose results were brought together in a General Discussion. Alpha diversity (species richness) increased by almost four species on average, whereas β diversity tended to decrease (Chapter 1). The latter is interpreted as a beginning floristic homogenization. The observed changes were primarily the result of a spread of native habitat generalists that are able to tolerate broad pH and moisture ranges. The changes in α and β diversity were only significant when species abundances were neglected (Chapters 1 and 2), demonstrating that the diversity changes resulted mainly from gains and losses of low-abundance species. This study is one of the first studies in temperate Europe that demonstrates floristic homogenization of forest plant communities at a larger than local scale. The diversity changes found at the taxonomic level did not result in similar changes at the functional level (Chapter 2). The likely reason is that these communities are functionally “buffered”. Single communities involve most of the functional diversity of the regional pool, i.e., they are already functionally rich, while they are functionally redundant among each other, i.e., they are already homogeneous. Independent of taxonomic homogenization, the abundance of 30 species decreased significantly (Chapter 4). These species included 12 ancient forest species (i.e., species closely tied to forest patches with a habitat continuity > 200 years) and seven species listed on the Red List of endangered plant species in NW Germany. If these decreases continue over the next decades, local extinctions may result. This biotic impoverishment would seriously conflict with regional conservation goals. Community assembly mechanisms changed at the local level particularly at sites that experienced disturbance by forest management activities between the sampling periods (Chapter 3). Disturbance altered community assembly mechanisms in two ways: (i) it relaxed environmental filters and allowed the coexistence of different reproduction strategies, as reflected by a higher diversity of reproductive traits at the time of the resurvey, and (ii) it enhanced light availability and tightened competitive filters. These limited the functional diversity with respect to canopy height and selected for taller species. Thirty-one winner and 30 loser species, which had significantly increased or decreased in abundance, respectively, were characterized by various functional traits and ecological performances to find indications on the most likely environmental drivers for the observed floristic changes (Chapter 4). Winner species had higher seed longevity, flowered later in the season and had more often an oceanic distribution compared to loser species. Loser species tended to have a higher specific leaf area, to be more susceptible to deer browsing and to have a performance optimum at higher soil pH values compared to winner species. Multiple logistic regression analyses indicated that disturbances due to forest management interventions were the primary cause of the species shifts. As one of the first European resurvey studies, this study provides indications that an enhanced browsing pressure due to increased deer densities and increasingly warmer winters are important drivers. The study failed to demonstrate that eutrophication and acidification due to atmospheric deposition substantially drive herb layer changes. The restriction of the sample to the most base-rich sites in the region is discussed as a likely reason. Furthermore, the decline of several ancient forest species is discussed as an indication that the forest patches are still paying off their “extinction debt”, i.e., exhibit a delayed response to forest fragmentation.
To date, positive relationships between diversity and community biomass have been mainly found, especially in terrestrial ecosystems due to the complementarity and/or dominance effect. In this thesis, the effect of diversity on the performance of terrestrial plant and phytoplankton communities was investigated to get a better understanding of the underlying mechanisms in the biodiversity-ecosystem functioning context. In a large grassland biodiversity experiment, the Jena Experiment, the effect of community diversity on the individual plant performance was investigated for all species. The species pool consisted of 60 plant species belonging to 4 functional groups (grasses, small herbs, tall herbs, legumes). The experiment included 82 large plots which differed in species richness (1-60), functional richness (1-4), and community composition. Individual plant height increased with increasing species richness suggesting stronger competition for light in more diverse communities. The aboveground biomass of the individual plants decreased with increasing species richness indicating stronger competition in more species-rich communities. Moreover, in more species-rich communities plant individuals were less likely to flower out and had fewer inflorescences which may be resulting from a trade-off between resource allocation to vegetative height growth and to reproduction. Responses to changing species richness differed strongly between functional groups and between species of similar functional groups. To conclude, individual plant performance can largely depend on the diversity of the surrounding community. Positive diversity effects on biomass have been mainly found for substrate-bound plant communities. Therefore, the effect of diversity on the community biomass of phytoplankton was studied using microcosms. The communities consisted of 8 algal species belonging to 4 functional groups (green algae, diatoms, cyanobacteria, phytoflagellates) and were grown at different functional richness levels (1-4). Functional richness and community biomass were negatively correlated and all community biomasses were lower than their average monoculture biomasses of the component species, revealing community underyielding. This was mainly caused by the dominance of a fast-growing species which built up low biomasses in monoculture and mixture. A trade-off between biomass and growth rate in monoculture was found for all species, and thus fast-growing species built up low biomasses and slow-growing species reached high biomasses in monoculture. As the fast-growing, low-productive species monopolised nutrients in the mixtures, they became the dominant species resulting in the observed community underyielding. These findings suggest community overyielding when biomasses of the component species are positively correlated with their growth rates in monocultures. Aquatic microcosm experiments with an extensive design were performed to get a broad range of community responses. The phytoplankton communities differed in species diversity (1, 2, 4, 8, and 12), functional diversity (1, 2, 3, and 4) and community composition. The species/functional diversity positively affected community biomass, revealing overyielding in most of the communities. This was mainly caused by a positive complementarity effect which can be attributed to resource use complementarity and/or facilitative interaction among the species. Overyielding of more diverse communities occurred when the biomass of the component species was correlated positively with their growth rates in monoculture and thus, fast-growing and high-productive species were dominant in mixtures. This and the study mentioned above generated an emergent pattern for community overyielding and underyielding from the relationship between biomass and growth rate in monoculture as long as the initial community structure prevailed. Invasive species can largely affect ecosystem processes, whereas invasion is also influenced by diversity. To date, studies revealed negative and positive diversity effects on the invasibility (susceptibility of a community to the invasion by new species). The effect of productivity (nutrient concentration ranging from 10 to 640 µg P L-1), herbivory (presence/absence of the generalist feeder) and diversity (3, 4, 6 species were randomly chosen from the resident species pool) on the invasibility of phytoplankton communities consisting of 10 resident species was investigated using semi-continuous microcosms. Two functionally diverse invaders were chosen: the filamentous and less-edible cynaobacterium C. raciborskii and the unicellular and well-edible phytoflagellate Cryptomonas sp. The phytoflagellate indirectly benefited from grazing pressure of herbivores whereas C. raciborskii suffered more from it. Diversity did not affect the invasibility of the phytoplankton communities. Rather, it was strongly influenced by the functional traits of the resident and invasive species.