156 PARALLEL SESSION HALL H III THURSDAY ANDEAN BIODIVERSITYPARALLE SESSION THURSDAY H III: ANDEAN BIODIVERSITY HOTSPOT157Session: The Andean biodiversity hotspot and its future: Biodiversity,eco system functioning & ecosystem services under environmentalchangeThursday, 24 February, 16:45, Hall H IIISession: The Andean biodiversity hotspot and its future: Biodiversity,eco system functioning & ecosystem services under environmentalchangeThursday, 24 February, 17:00, Hall H IIITHURSDAY 16:45 Hall H IIISIMULATION OF NET PHOTOSYNTHESIS OF TWO COMPETINGSPECIES, THE SOUTHERN BRACKEN AND THE PASTURE GRASSSETARIA SPHACELATA, IN A TROPICAL MOUNTAIN ECOSYSTEM.Brenner Silva 1 , Jörg Bendix 11LCRS - Marburg University, Marburg, not U, DE, brenner.silva@students.unimarburg.deThe tropical mountain <strong>for</strong>est in the Andes of Ecuador is the second hottestbiodiversity hotspot of the world and suffers from a high de<strong>for</strong>estation rate,mainly to gain pastures. However, the planted pasture grass (Setaria spacelata)is frequently overgrown by an aggressive weed (southern bracken), probablydue to recurrent burning and competition <strong>for</strong> light. As a result, pastures areabandoned and natural succession is affected. To understand the growthefficiency of bracken and its competitive strength an experimental site wasestablished in the Rio San Francisco Valley. A numerical model (The SouthernBracken Competition Model SoBraCoMo) was developed to simulate the growthof both competing species which will be presented in the talk. Validation wasconducted by means of independent measurements of daily courses. Following,the model was initialized with meteorological data <strong>for</strong> 2008 in 10 minutes steps.It will be shown that the grass Setaria was more productive, assimilating up to40% more atmospheric CO2 than the southern bracken. It contrasts with fieldobservations and points out that other factors like cattle browsing might beresponsible <strong>for</strong> the competitive strength of bracken.NEOTROPICAL C3/C4 GRASS DISTRIBUTION - PRESENT PAST ANDFUTURELaurent Bremond 1 , Charly Favier 2 , Arnoud Boom 31CBAE - UMR5059, Montpellier, FR, laurent.bremond@univ-montp2.fr, 2 ISE-mUMR5554, Montpellier, Fr, 3 Dpt Geography - University Leicester, Leicester, GBThe main environmental factors controlling C3 and C4 grass distribution in theintertropical zone are not well known. Some C3/C4 distribution models basedon photosynthetic grass physiologies have been developed but not easilyvalidated with field measurements. Nonetheless, these models are quite usefulbecause they are able to estimate the response of grasslands to past and futureCO2 atmospheric concentration changes.The aim of our study is to establish a schematic of the present altitudinal C3/C4 grass distribution in tropical South America and to then compare it witha simple photosynthetic model and with a dynamic global vegetation model(DGVM) <strong>for</strong> present, past and future climate.Grass species richness distribution data were compiled from literature andinterpreted in term of species altitudinal distribution and of C3/C4 proportions.A regression was established between mean annual temperatures and C4grasses. This relationship was then compared to simulations of the LPJ-GUESSmodel <strong>for</strong> the present climate. Finally, the photosynthetic model and the DGVMwere compared with the IPCC climate projections <strong>for</strong> 2100, and the simulationsof the PMIP2 models at 6k and 18k yrs BP.THURSDAY 17:00 Hall H IIIgtö<strong>Society</strong> <strong>for</strong> <strong>Tropical</strong> <strong>Ecology</strong> | Gesellschaft für Tropenökologie e.V. Status and future of tropical biodiversity | Frankfurt, 21 - 24 February 2011gtö
158 PARALLEL SESSION HALL H III THURSDAY ANDEAN BIODIVERSITYPARALLE SESSION THURSDAY H III: ANDEAN BIODIVERSITY HOTSPOT159THURSDAY 17:15 Hall H IIISession: The Andean biodiversity hotspot and its future:Thursday, 24 February, 17:15, Hall H IIIEFFECTS OF GRASS (SETARIA SPHACELATA) COMPETITION ANDFERTILIZATION ON ROOT LENGTH AND BIOMASS ALLOCATION OFNATIVE TREE SPECIES FROM ECUADORBernd Stimm 1 , Ximena Palomeque 1 , Paula Loaiza 1 , Sven Günter 2 , PatrickHildebrandt 1 , Helmut Blaschke 1 , Michael Weber 11TU Muenchen Forest Science, Freising, DE, stimm@<strong>for</strong>st.wzw.tum.de, 2 CATIE,Turrialba, CRAssessments on plant dynamics have focused primarily on above-groundprocesses, while below-ground processes are less well understood, in particularin tropical <strong>for</strong>ests. Within the context of restoration of degraded lands in thetropics it is well known that Setaria sphacelata is a strong abovegroundcompetitor and limits the suitable establishment of tree seedlings onpasture sites. Moreover, sometimes fertilizers are used to improve the growthper<strong>for</strong>mance of tree species in restoration ef<strong>for</strong>ts without understanding thegenuine effect on the establishment of tree species. There<strong>for</strong>e, the aim of thisstudy was to detect the effects of grass competition and fertilizer additionon the development of the root system (i.e. total root length and biomassallocation) of three native tree species (Cedrela montana, Tabebuia chrysanthaand Alnus acuminata).We established 60 rhizotrons under nursery conditions in Loja – Ecuador (4rhizotrons/treatment x 5 repetitions x 3 species) where roots were weeklytraced during several months. At the end of the experiment the tree seedlingsand grass were harvested to calculate the above and below ground biomassallocation.The results showed: 1) that with Setaria competition all tree species werestimulated to produce a higher root length to cope with the grass root system,2) tree species and grass had a clear tendency to allocate more on abovegroundthan on belowground biomass, even with fertilization. This is interpreted as astrategy of the seedlings to increase especially its height growth to escapethe grass competition earlier and improve the rate of photosynthesis underthe given environmental conditions. 3) Setaria had higher biomass allocationcompared to tree species and the intensive root system makes it a very efficientcompetitor that can impede vital growth of tree seedlings. A comparisonbetween tree species showed that Alnus was more successful producing both,higher total root length as well as higher above and below ground biomassthan Tabebuia and Cedrela. There<strong>for</strong>e, Alnus could be a good candidate to startrehabitation processes on pastures dominated by Setaria.Session: The Andean biodiversity hotspot and its future:Thursday, 24 February, 17:30, Hall H IIIAPPLICATION OF NATIVE ARBUSCULAR MYCORRHIZAL FUNGI FORREFORESTATION WITH NATIVE TREE SPECIES IN SOUTH ECUADORClaudia Krüger 1 , Narcisa Urgiles 1 , Arthur Schüßler 11LMU München, Planegg-Martinsried, DE, claudia.krueger@lrz.uni-muenchen.deEcuador shows the highest de<strong>for</strong>estation rate in South America and sustainablere<strong>for</strong>estation programs with native tree species are timely to reduce de<strong>for</strong>estationpressure on natural <strong>for</strong>ests and to re-establish stable and diverse ecosystems.Most tropical trees strongly depend on associations with arbuscular mycorrhiza(AM) <strong>for</strong>ming fungi, which are obligate symbionts of >80% of land plants. Thesefungi provide large amounts of inorganic nutrients, such as P and N to the plant.In our research area, the Reserva Biológica de San Francisco (RBSF) in South-Ecuador, the vast majority (113/115) of the investigated mountain rain<strong>for</strong>est treespecies was proven to <strong>for</strong>m AM (Kottke et al. 2008, Ecological Studies 198: 137-148).Our approach was, to relate ecosystem knowledge to sustainable managementpractices, namely af<strong>for</strong>estation attempts with native, potential crop trees. Thecapability of applying AM fungi (AMF) in a tree nursery <strong>for</strong> a more efficientre<strong>for</strong>estation of abandoned pastures (close to the RBSF) was evaluated. NativeAMF were isolated from roots of earlier experiments (Urgiles et al. 2009, NewForest 38: 229-239) and existing re<strong>for</strong>estation plots, analysed morphologically,DNA barcoded and established as stable cultures with Plantago lanceolata asa plant host (see poster Krüger et al.). Ten cultures were chosen to produce anAMF ‘cocktail’ that was used to inoculate seedlings of three tree species, Cedrelamontana, Heliocarpus americanus and Tabebuia chrysantha. Two samplings wereconducted during the 6-months nursery phase and two during 12-months afteroutplanting at the pastures.We address the question, whether the tree seedlings inoculated with AMF showimproved growth and/or mortality rates. In addition, we monitored the AMF withthe 454FLX-Titanium amplicon sequencing technology and found certain AMF topersist during the nursery phase and also after outplanting. In other experiments,each of the tree species was inoculated with a set of individual AMF and growthper<strong>for</strong>mance was studied. When combined with low fertilization up to 10-timesmore biomass was <strong>for</strong>med by certain plant-AMF combination in the nursery, ascompared to control treatments.With these approaches we distinguish AMF that preferentially associate with thenative tree seedlings, under nursery condition, and we correlate these data withthe plant per<strong>for</strong>mance in the field. The results will allow recommending a moreefficient management strategy <strong>for</strong> re<strong>for</strong>estation attempts in Ecuador.THURSDAY 17:30 Hall H IIIgtö<strong>Society</strong> <strong>for</strong> <strong>Tropical</strong> <strong>Ecology</strong> | Gesellschaft für Tropenökologie e.V. Status and future of tropical biodiversity | Frankfurt, 21 - 24 February 2011gtö