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Dislich, C. (2012): <b>The role of life history traits for coexistence and forest recovery after disturbance ? a modelling perspective. Towards a better understanding of species-rich forests</b> University of Bayreuth, <i>phd thesis</i>

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Title: Über die Bedeutung von Arteigenschaften für Koexistenz und Waldregeneration nach Störungen ? Eine Modellierungsstudie zum besseren Verständnis artenreicher Wälder
Short Name: The role of life history traits for coexistence and forest recovery after disturbance
FOR816dw ID: 1091
Publication Date: 2012-04-10
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Individual: Claudia Dislich
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Abstract:
Tropical forests are well known for their exceptional species richness ? high diversity of<br/> plant species constitute the basis for an equivalently rich fauna. An astonishing variety<br/> of plant life strategies has evolved, manifesting itself also in different compositions of life<br/> history traits in trees. This thesis investigates the role of tree life history traits (growth,<br/> mortality and recruitment) on different processes structuring species-rich forests. Our<br/> study system is a montane rainforest located in the Tropical Andes hotspot of biodiversity<br/> in southern Ecuador. Here, we find a mosaic of steep ridges and deeply incised<br/> valleys, covered with predominantly broadleaf forest. Forest structure and species composition<br/> differ considerably depending on altitude and topographic position. The forest<br/> cover is frequently interrupted by scars of landslides, which constitute an important type<br/> of natural disturbance in this ecosystem.<br/> We utilize ecological models as tools to gain deeper insights into key processes driving<br/> the maintenance of tree species richness and affecting forest recovery after landslides.<br/> The first part of this thesis concerns the question of species coexistence. We develop<br/> a theoretical model to analyze how different trade-offs between life history traits (tree<br/> growth, seed dispersal, tree mortality) affect tree species coexistence. We find that the<br/> considered trade-offs alone are not sufficient to explain long-term species coexistence.<br/> Additional ?stabilizing? mechanisms seem to be indispensable to facilitate coexistence in<br/> species-rich forests. Such mechanisms could result from biotic interactions, that alter<br/> the relation between inter- and intra-specific competition depending on (local) species<br/> abundances (e.g. density-dependent mortality). Other possible coexistence mechanisms<br/> likely to be relevant to our particular study system are driven by external, abiotic factors<br/> like a complex topography resulting in locally differing habitat types (each supporting a<br/> different set of species), or the character of a prevailing disturbance regime (e.g. shallow<br/> landslides).<br/> In the second part of the thesis, we investigate the growth dynamics of the ridge forest<br/> in our study system. To this end, we utilize the process-based forest growth model<br/> FORMIND. We show that after calibration, the model successfully reproduces forest<br/> dynamics on different levels of complexity (e.g. basal area and stem size distribution).<br/> We then use this forest model to investigate the influence of landslide disturbances on<br/> forest dynamics both on the local scale of a single landslide and on the landscape scale.<br/> On landslide sites, changes in environmental conditions might lead to changes in different<br/> tree life history traits. We analyze scenarios with changes in different traits (tree recruitment,<br/> tree growth, tree mortality) and find that while tree biomass can recover within the<br/> first hundred years after a landslide, the time until forest structure and species composition<br/> is restored is considerably longer (approximately 200 years). Changes in different<br/> traits result in differing spatial distributions of tree biomass: reduced tree growth leads<br/> to a more homogeneous distribution of biomass, whereas reduced recruitment and increased<br/> mortality yield a more heterogeneous biomass distribution (?patchy? vegetation).<br/> On the landscape level, overall forest biomass is substantially reduced by landslides (8 -<br/> I<br/> 14%), compared to only 2 -3% of the area marked by visible traces of landslides. Thus<br/> this particular type of disturbance considerably influences the total forest carbon balance.<br/> In a complementary investigation we study abiotic and biotic factors that potentially<br/> trigger landslide occurrence in our study system. For this, we develop an extension of<br/> a standard physically-based model of slope stability. We find that due to the predominantly<br/> shallow tree roots, some of the observed landslides might be triggered by the<br/> vegetation itself.<br/> This thesis demonstrates that ecological models are useful tools to gain deeper insights<br/> into important processes shaping forest communities. They can be applied for theoretical<br/> questions such as the question of species coexistence, as well as for more applied,<br/> management related questions like predicting forest recovery after disturbances.
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THESIS
Degree: phd
Degree Institution: University of Bayreuth
Total Pages: 129
Metadata Provider:
Individual: Claudia Dislich
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Download File: http://www.tropicalmountainforest.org/publications.do?citid=1091


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