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VAAM-Jahrestagung 2012 18.–21. März in Tübingen

VAAM-Jahrestagung 2012 18.–21. März in Tübingen

VAAM-Jahrestagung 2012 18.–21. März in Tübingen

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223SMP040amoA-based consensus phylogeny of ammonia-oxidiz<strong>in</strong>garchaea and deep sequenc<strong>in</strong>g of amoA genes from soils of fourdifferent geographic regionsM. Pester* 1 , T. Rattei 2 , S. Flechl 1 , A. Gröngröft 3 , A. Richter 4 , J. Overmann 5 ,B. Re<strong>in</strong>hold-Hurek 6 , A. Loy 1 , M. Wagner 11 University of Vienna, Department of Microbial Ecology, Vienna, Austria2 University of Vienna, Department of Computational Systems Biology, Vienna,Austria3 University of Hamburg, Institute of Soil Science, Hamburg, Germany4 University of Vienna, Department of Chemical Ecology and EcosystemResearch, Vienna, Austria5 Leibniz-Institut DSMZ-Deutsche Sammlung von Mikroorganismen undZellkulturen, Braunschweig, Germany6 University of Bremen, Department of Microbe-Plant Interactions, Bremen,GermanyAmmonia-oxidiz<strong>in</strong>g archaea (AOA) play an important role <strong>in</strong> nitrificationand many studies exploit their amoA genes as marker for their diversityand abundance. We present an archaeal amoA consensus phylogeny basedon all publicly available sequences (status June 2010) and provideevidence for the diversification of AOA <strong>in</strong>to four previously recognizedclusters and one newly identified major cluster. These clusters, for whichwe suggest a new nomenclature, harbored 83 AOA species-level OTUs(us<strong>in</strong>g an <strong>in</strong>ferred species threshold of 85% amoA identity). 454pyrosequenc<strong>in</strong>g of amoA amplicons from 16 soils sampled <strong>in</strong> Austria,Costa Rica, Greenland, and Namibia revealed that only 2% of retrievedsequences had no database representative on the species-level andrepresented 30-37 additional species-level OTUs. With the exception of anacidic soil from which mostly amoA amplicons of the Nitrosotalea clusterwere retrieved, all soils were dom<strong>in</strong>ated by amoA amplicons from theNitrososphaera cluster (also called group I.1b), <strong>in</strong>dicat<strong>in</strong>g that thepreviously reported AOA from the Nitrosopumilus cluster (also calledgroup I.1a) are absent or represent m<strong>in</strong>or populations <strong>in</strong> soils. AOArichness estimates on the species level ranged from 8-83 co-exist<strong>in</strong>g AOAsper soil. Presence/absence of amoA OTUs (97% identity level) correlatedwith geographic location, <strong>in</strong>dicat<strong>in</strong>g that besides contemporaryenvironmental conditions also dispersal limitation across differentcont<strong>in</strong>ents and/or historical environmental conditions might <strong>in</strong>fluenceAOA biogeography <strong>in</strong> soils.SMP041Organic propagation of olive nursery plants us<strong>in</strong>g Pantoeaeucr<strong>in</strong>a stra<strong>in</strong> AG9M.D.C. Montero-Calasanz* 1,2 , C. Santamaría 2 , A. Daza 2 , E. Lang 1 , H.-P. Klenk 1 , M. Camacho 21 Leibniz Institute DSMZ- Deutsche Sammlung von Mikroorganism undZellKulturen GmbH , Department of Microbiology, Braunschweig, Germany2 IFAPA Centro Las Torres-Tomejil. Junta de Andalucia., Department ofNatural Resources and Organic Production, Alcala del Rio (Sevilla). SPAIN.,Spa<strong>in</strong>The demand for organic olive oil is <strong>in</strong>creas<strong>in</strong>g exponentially each year(MARM, 2010). However, nowadays there is not a commercial methodthat can replace the use of a synthetic hormone <strong>in</strong> organic propagation ofolive nursery plants.The goal of this work is the development of an organic olive propagationmethod based on the use of the stra<strong>in</strong> AG9 (Pantoea eucr<strong>in</strong>a), previouslycharacterized as a Plant Growth Promot<strong>in</strong>g Rhizobacteria (PGPR). Thisstra<strong>in</strong> has been used <strong>in</strong> monoxenic model systems show<strong>in</strong>g both, higherroot<strong>in</strong>g <strong>in</strong>duction and root elongation than negative controls, <strong>in</strong> mung beanand canola assays. Moreover, this bacterium has been tested <strong>in</strong> four olivecultivars, under nursery conditions, display<strong>in</strong>g higher or similareffectiveness than the hormonal treatments. These results underwrite theworth of this method.On the other hand, by means of Confocal Laser Scann<strong>in</strong>g Microscope(CLSM) and GFP tagged bacterial cells, it was confirmed that this stra<strong>in</strong> isable to colonize the plant roots permanently as an endophyte and topromote the plant growth a long-term.MARM. Anuario de Estadística. M<strong>in</strong>isterio de Medio Ambiente, MedioRural y Mar<strong>in</strong>o. Gorbierno de Espana (2010).SMP042Temperature effects of geothermal energy use on themicrobial community <strong>in</strong> subsurface environmentsF. Hegler* 1 , T. Lüders 1 , G. Bisch 2 , P. Blum 3 , C. Griebler 11 Helmholtz Zentrum München, Institute of Groundwater Ecology, Neuherberg,Germany2 University of Stuttgart, VEGAS - Institut für Wasser- undUmweltsystemmodellierung, Stuttgart, Germany3 Karlsruhe Institute of Technology (KIT), Institute for Applied Geosciences,Karlsruhe, GermanyGeothermal energy use has boomed <strong>in</strong> the last years. In w<strong>in</strong>ter, theexploitation of geothermal energy can be used to heat build<strong>in</strong>gs and <strong>in</strong>summer to cool them. Especially geothermal heat exchangers up to 100 mdepth are <strong>in</strong>stalled frequently. Although geothermal energy use is acceptedas be<strong>in</strong>g environmentally friendly, several aspects need to be considered <strong>in</strong>an evaluation of its use. While complications dur<strong>in</strong>g drill<strong>in</strong>g (e.g. lead<strong>in</strong>gto cracks <strong>in</strong> houses) or dur<strong>in</strong>g the operation of geothermal heat systems(e.g. leakage of anti-freez<strong>in</strong>g agents to the aquifer) are caused bymisjudgment or accidents, other effects cannot be avoided.Generally, temperature <strong>in</strong> the subsurface deeper than 15 m is constant overthe year. Geothermal heat exchangers may decrease or <strong>in</strong>crease thetemperature locally. Therefore, <strong>in</strong> our study we focus on the effects oftemperature changes on the subsurface environment adjacent togeothermal heat exchangers. Temperature shifts <strong>in</strong>fluence the viscosity anddensity of water but also the solubility of liquids, solids, gases andgenerally the geochemical equilibrium. Not only may geochemicalequilibria shift but also the microbial communities and fauna may be<strong>in</strong>fluenced by temperature. While temperature effects on the microbialcommunity for open, nearer surface geothermal systems are documented[1,2] the current project aims to evaluate possible shifts <strong>in</strong>duced bygeothermal heat exchangers.With this study we are present<strong>in</strong>g first results for the effect of chang<strong>in</strong>gtemperatures on the microbial community <strong>in</strong> a usually constanttemperature environment such as the subsurface.1. Brielmann, H., et al., Oberflächennahe Geothermie und ihre potentiellen Auswirkungen aufGrundwasserökologie. Grundwasser, 2011.16: p. 77-91.2. Brielmann, H., et al., Effects of thermal energy discharge on shallow groundwater ecosystems.FEMS Microbiology Ecology, 2009.68: p. 273-286.SMP043Microbial carbon decomposition under anoxic conditions <strong>in</strong>permafrost-affected soil of the Q<strong>in</strong>ghai-Xizang PlateauS. Yang*, D. WagnerAlfred Wegener Institute for Polar and Mar<strong>in</strong>e Research,Geomicrobiology, Potsdam, GermanyThe Q<strong>in</strong>ghai-Xizang Plateau (QXP) <strong>in</strong> high Asia is the third permafrostunit outside polar regions, about 54.3% of it is covered by permafrost,reta<strong>in</strong><strong>in</strong>g 23% SOM of Ch<strong>in</strong>ese soils or 2.5% of the global pool (Wang etal., 2002). Affected by India and Asian monsoon, the plateau differs <strong>in</strong>temperature and moisture gradients along the monsoon routes, mak<strong>in</strong>g thefate of SOM with<strong>in</strong> QXP soil more complicated. The SOM turnover isma<strong>in</strong>ly driven by microbial communities which decompose permafrostSOM via a sequence of microbial processes to CH 4 under anaerobicconditions (methanogenesis), which is a rather strong greenhouse gas. Inresponse to climate warm<strong>in</strong>g, QXP permafrost degradation has beenenhanced over the past decades, the methane turnover via methanogens istherefore our focus from the view of global change research. An<strong>in</strong>terdiscipl<strong>in</strong>ary project is conducted along the two different monsoongradients to l<strong>in</strong>k the<strong>in</strong>-situ methane flux with temporal and spatialvariations of permafrost soil carbon (e.g. ST, SM, SRP, SOMs, TOC, pH)and dynamics of methanogenic consortia. Attention will be paid on theanaerobic carbon decomposition, dynamics of archaeal communities andtheir reaction to global change by us<strong>in</strong>g methane produc<strong>in</strong>g rate analysisand a diverse molecular biotechniques <strong>in</strong>clud<strong>in</strong>g DGGE and t-RFLPf<strong>in</strong>gerpr<strong>in</strong>ts, clon<strong>in</strong>g, FISH and real-time PCR to quantitatively andqualitatively <strong>in</strong>vestigate the diversity, abundance and the changes of thecomposition of archaeal communities. On this basis, it is expected to beable to improve our understand<strong>in</strong>g about the potential anoxicdecomposition of permafrost SOMs under different the climate gradientsand its future development under global warm<strong>in</strong>g.Wang G.X., Ju Q., Cheng G.D., and Lai Y.M.. 2002. Soil organic carbon pool of grassland soils onthe Q<strong>in</strong>ghai-Tibetan Plateau and its global implication. Science of The Total Environment,291(1-3):207-217.BIOspektrum | Tagungsband <strong>2012</strong>

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