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

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

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225SMP048Interactions between bacteria antagonistic towards Rhizoctoniasolani, lettuce and <strong>in</strong>digenous rhizosphere communities <strong>in</strong> threesoil typesS. Schreiter*, E. Scholz, U. Zimmerl<strong>in</strong>g, P. Zocher, R. Grosch, K. SmallaJulius Kühn Institute, Institute for Epidemiology and PathogenDiagnostics, Braunschweig, GermanyRhizoctonia solani is a soil-borne plant pathogen which causes bottom rotdisease and leads to a massive loss of lettuce and potato every year. Thelack of effective fungicides makes it difficult to control this and other plantpathogens. So it is necessary to f<strong>in</strong>d alternative strategies. A promis<strong>in</strong>gapproach is the use of natural antagonists of the plant pathogen. Underlaboratory and greenhouse conditions, two isolates, Pseudomonas jesseniiRU47 and Serratia plymuthica 3Re4-18, showed the ability to reducedisease symptoms. But the efficiency of biocontrol agents was reported asvery variable and the reason for this variability is largely unknown.Therefore, a better understand<strong>in</strong>g of the <strong>in</strong>teraction of the microbialcommunity, the plant rhizosphere and the bulk soil is required for asuccessful exploitation of this antagonistic potential. With<strong>in</strong> the frame of aDFG-Project a field experiment has been set up with a uniqueexperimental plot system <strong>in</strong> Großbeeren compar<strong>in</strong>g three different soiltypes. This made it possible to analyze the <strong>in</strong>fluence of the soil type<strong>in</strong>dependently from other factors such as climate and cropp<strong>in</strong>g history.First results showed a different survival of the two antagonistic stra<strong>in</strong>s <strong>in</strong>the tree soil types. Also the damages caused by the pathogen are different<strong>in</strong> the soil types. We assume that these observations are related withdifferences <strong>in</strong> the microbial communities of the three soils. Indeed highlysignificant differences between the soil types were revealed by denatur<strong>in</strong>ggradient gel electrophoresis analysis of bacterial and fungal communities.Look<strong>in</strong>g at the rhizosphere, it could be confirmed that after three weeks,when lettuce is especially susceptible to the pathogen, the antagonisticstra<strong>in</strong>s are dom<strong>in</strong>ant populations. The antagonists compensated the damagecaused by the pathogen similarly <strong>in</strong> all soils as revealed by dry weight andrat<strong>in</strong>g of the lettuce. Also the antagonistic stra<strong>in</strong>s did not affect the<strong>in</strong>digenous microbial community. Therefore a negative ecological effect is notexpected. The antagonistic stra<strong>in</strong>s had a positive <strong>in</strong>fluence on lettuce<strong>in</strong>dependent from the <strong>in</strong>digenous microbial community and the pathogen so thebiological mechanism rema<strong>in</strong>s unknown. In conclusion the stra<strong>in</strong>s arepromis<strong>in</strong>g biocontrol agents to compensate the lack of effective fungicides.SMP049Effects of resource quality and quantity on fungalcommunities <strong>in</strong> an agricultural soilJ. Moll* 1 , K. Goldmann 1 , D. Krüger 1 , F. Buscot 1,21 UFZ-Helmholtz Centre for Environmental Research GmbH, Soil Ecology,Halle, Germany2 University of Leipzig, Institute of Biology I, Leipzig, GermanyDue to their high diversity and a wide decomposition potential, fungi arewell adapted to the heterogeneous soil environment and are a majorcomponent of soil microbial communities.In the frame of the DFG-funded (German Research Foundation) researchunit FOR 918 „Carbon flow <strong>in</strong> belowground food webs assessed byisotope tracers“ we <strong>in</strong>vestigate the role of saprobiotic fungi <strong>in</strong> the transferof organic carbon from plant orig<strong>in</strong> to belowground food webs of anagricultural soil. To tackle how carbon quality and availability <strong>in</strong>fluencethe fungal communities, a field experiment has been <strong>in</strong>stalled where twocrops, maize (Zea mays L.) und wheat (Triticum aestivum L.), arecultivated <strong>in</strong> a design cross manipulat<strong>in</strong>g addition of maize litter. Soil fromthree depths was sampled <strong>in</strong> July, September and December <strong>in</strong> 2009 and2010 to analyze seasonal shifts <strong>in</strong> the fungal community composition.ARISA (automated ribosomal <strong>in</strong>tergenic spacer analysis) which was usedas DNA-f<strong>in</strong>gerpr<strong>in</strong>t method resulted <strong>in</strong> 198 OTUs (operational taxonomicunits). Univariate statistical analysis revealed that fungal species richnessvaries accord<strong>in</strong>g to the crop and the manipulated carbon <strong>in</strong>put <strong>in</strong> terms ofadded litter. Furthermore fungal species richness was highest <strong>in</strong> September<strong>in</strong> both years. Despite a reduced carbon availability <strong>in</strong> the B-horizon nodecl<strong>in</strong>e <strong>in</strong> species richness with <strong>in</strong>creas<strong>in</strong>g depth was found.Multivariate statistical analysis demonstrated that the soil fungalcommunity is mostly affected by soil depth, followed by the impact of theplants and related root exudates. These results <strong>in</strong>dicate strong reactions ofthe fungi to different nutrient supplies.In follow up microcosm experiments with variable nutrient availabilityfungal key players actively assimilat<strong>in</strong>g carbon will be identified us<strong>in</strong>grRNA-SIP (stable isotope prob<strong>in</strong>g).SMP050M<strong>in</strong>imal nutrient requirements of Myxococcus xanthusDK1622R. Pietsch*, L. Blaß, E. He<strong>in</strong>zleSaarland University, Biochemical Eng<strong>in</strong>eer<strong>in</strong>g, Saarbrücken, GermanyThe soil bacterium Myxococcus xanthus DK1622 naturally feeds on lysedmicroorganisms by secretion of proteases [1, 2]. S<strong>in</strong>ce the growth is pooron def<strong>in</strong>ed media like A1 or M1 [3, 4, 5], but good on case<strong>in</strong> and case<strong>in</strong>hydrolysates, we studied the degradation and uptake of related peptides. Itslack of a hexose uptake system [1] does not allow utiliz<strong>in</strong>g mono- orpolysaccharides. Isoleuc<strong>in</strong>e, leuc<strong>in</strong>e and val<strong>in</strong>e are essential because theycannot be synthesized [3], but their uptake is enabled by the branchedcha<strong>in</strong> am<strong>in</strong>o acid transport system [6].Like <strong>in</strong> the degradation of -case<strong>in</strong> by Lactococcus lactis [7], uptake ofpeptides should be possible with a maximal length of 18 am<strong>in</strong>o acids viathe oligopeptide permease [8]. The biological fate of peptides <strong>in</strong> theculture supernatant of M. xanthus was followed via Matrix-assisted laserdesorption/ionisation mass spectrometry (Maldi-MS) with bradyk<strong>in</strong><strong>in</strong> 1-7as <strong>in</strong>ternal standard (any occurrence of m/z=757 <strong>in</strong> supernatant). Thesequences of s<strong>in</strong>gle peptides were confirmed by tandem measurements(MS/MS) with collision <strong>in</strong>duced decay and a novel software tool(PeptideChopper 2.0) which aligns the found masses of peptides andfragment ions to all four case<strong>in</strong> subtype sequences.Ma<strong>in</strong> degradation detectable by Maldi-MS takes place at -case<strong>in</strong> 59-92and 144-162. We identified ma<strong>in</strong> and alternative degradation pathways byboth C- and N-term<strong>in</strong>al exopeptidases. A k<strong>in</strong>etic model was developed todescribe the degradation of peptides.To observe whether uptake of peptides with a length of n<strong>in</strong>e am<strong>in</strong>o acids ispossible without further degradation, synthesized -case<strong>in</strong> peptides 74-82and 145-153 which conta<strong>in</strong> all am<strong>in</strong>o acids essential for growth were<strong>in</strong>cubated with concentrated proteases from the culture supernatant to f<strong>in</strong>dthe putative degradation products. In a second experiment, they were usedas the only carbon and nitrogen sources.This way, we elucidated degradation pathways of -case<strong>in</strong> by M. xanthusDK1622. Offer<strong>in</strong>g a high amount of synthetic peptides conta<strong>in</strong><strong>in</strong>g all essentialam<strong>in</strong>o acids is not sufficient for efficient growth of M. xanthus DK1622 even ifthey are parts of the major degradation pathways of casitone.1. L. J. Shimkets, M. Dwork<strong>in</strong> and H. Reichenbach <strong>in</strong> “The Procaryotes”, ed. M. Dwork<strong>in</strong> (Spr<strong>in</strong>ger, NewYork) (2006), p. 60.2. A. Konovalova, T. Petters and L. Søgaard-Andersen, FEMS Microbiol Rev 34 (2010), p. 99.3. A. P. Bretscher and D. J. Kaiser, J Bacteriol 133 (1978), p. 763.4. S. S. Witk<strong>in</strong> and E. Rosenberg, J Bacteriol 103 (1970), p. 641-649.5. M. Dwork<strong>in</strong>, J Bacteriol 84 (1962), p. 250-257.6. H. B. Bode, M. W. R<strong>in</strong>g, G. Schwär, M. O. Altmeyer, C. Kegler, I. R. Jose, M. S<strong>in</strong>ger and R. Müller,Chem Bio Chem 10 (2009), p. 128-140.7. E. R. S. Kunji, G. Fang, C. M. Jeronimus-Strat<strong>in</strong>gh, A. P. Bru<strong>in</strong>s, B. Poolman and W. N. Kon<strong>in</strong>gs MolMicrobiol 27 (1998), p. 1107-11188. K. Savijoki, H. Ingmer and P. Varmanen Appl Microbiol Biotechnol 71 (2006), p. 398SMP051Insights <strong>in</strong> anaerobic hydrocarbon biodegradation undermethanogenic conditionsF. Gründger* 1 , F. von Netzer 2 , N. Jimenez-Garcia 3 , T. Lüders 2 , H.-H. Richnow 3 , M. Krüger 11 Bundesanstalt für Geowissenschaften und Rohstoffe, Geomikrobiologie,Hannover, Germany2 Helmholtz Zentrum München, Institut für Grundwasserökologie, Neuherberg,Germany3 Helmholtz Zentrum für Umweltforschung, Isotopenbiogeochemie, Leipzig,GermanyEnrichment, isolation and characterisation of hydrocarbon degrad<strong>in</strong>gmicroorganisms are of great importance to understand the biochemicalmechanisms responsible for oil biodegradation <strong>in</strong> contam<strong>in</strong>atedenvironments and <strong>in</strong> petroleum reservoirs. With respect to decreas<strong>in</strong>gconventional energy resources this understand<strong>in</strong>g also helps <strong>in</strong> the searchfor methods of enhanced hydrocarbon recovery, like the microbialconversion of oil or coal to recoverable methane.The ma<strong>in</strong> focus of this work therefore is the biodiversity of hydrocarbondegraders and their metabolic processes of methanogenesis. We started to<strong>in</strong>vestigate the physiological characteristics and activities of microbialconsortia enriched from freshwater and mar<strong>in</strong>e sediments as well as fromoil and coal reservoirs.Stable isotope measurements showed the conversion of 13 C-labelledhydrocarbons <strong>in</strong>to methane. With the use of T-RFLP and Q-PCR a largebacterial diversity was detected while the archaeal was limited to three orfour dom<strong>in</strong>ant species. Both doma<strong>in</strong>s were highly abundant <strong>in</strong> allenrichment cultures. Genes <strong>in</strong>dicative of metal reduction, sulphatereduction, and methanogenesis were also detected <strong>in</strong> high numbers <strong>in</strong> these<strong>in</strong>cubations. The sequenc<strong>in</strong>g analysis revealed a low phylogenetic diversityof Archaea comprised of Euryarchaeota and Crenarchaeota. Members ofMethanosarc<strong>in</strong>ales and Methanomicrobiales dom<strong>in</strong>ated the archaeal partof the community <strong>in</strong> the enrichment cultures. The ma<strong>in</strong> bacterialrepresentatives were Syntrophus spp., Desulfovibrio spp. andSyntrophomonas spp.. Us<strong>in</strong>g stable isotope prob<strong>in</strong>g with different 13 C-BIOspektrum | Tagungsband <strong>2012</strong>

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