224SMP044RNase J and RNase E <strong>in</strong> S<strong>in</strong>orhizobium meliloti: specific andcommon roles <strong>in</strong> rRNA maturation, RNA modification,motility and quorum sens<strong>in</strong>gK. Baumgardt 1 , S. Thalmann 1 , R. Madhugiri 1 , A. Schikora 2 , K.-H. Kogel 2 ,G. Klug 1 , A. Becker 3 , E. Evguenieva-Hackenberg* 11 Justus-Liebig-Universität Giessen, Institut für Mikrobiologie undMolekularbiologie, Gießen, Germany2 Justus-Liebig-Universität Giessen, Institute of Phytopathology andApplied Zoology, Gießen, Germany3 Albert-Ludwigs-Universität Freiburg, Institute of Biology III, Freiburg,GermanyS<strong>in</strong>orhizobium meliloti Rm2011, a nitrogen-fix<strong>in</strong>g plant symbiont,harbours RNase E and RNase J, two pr<strong>in</strong>cipal RNases of Bacillus subtilisand Escherichia coli, respectively (1). To address the mechanisms forposttranscriptional regulation of gene expression <strong>in</strong>S. meliloti, weanalyzed mutants with m<strong>in</strong>i-Tn5 <strong>in</strong>sertions <strong>in</strong> the genes encod<strong>in</strong>g RNase Eand RNase J (2) <strong>in</strong> comparison to the wild type. Only the RNase J mutantbut not the RNase E mutant was impaired <strong>in</strong> growth, motility and rRNAmaturation (3). However, small RNAs, tRNAs and mRNAs were affected<strong>in</strong> both mutants. Small RNAs and tRNAs have identical lengths butmigrate differently <strong>in</strong> denatur<strong>in</strong>g gels when compared to the wild type,suggest<strong>in</strong>g hypermodification of RNA <strong>in</strong> the two mutants. Consistent withthis, the gene SMc00649 encod<strong>in</strong>g a probable RNA methylase was upregulated<strong>in</strong> the mutant stra<strong>in</strong>s. Additional microarray and qRT-PCRanalyses revealed specific and overlapp<strong>in</strong>g effects on mRNA level. Thedetected down-regulation of genes <strong>in</strong>volved <strong>in</strong> motility and chemotaxis <strong>in</strong>the two mutants suggested differences <strong>in</strong> the quorum-sens<strong>in</strong>g response <strong>in</strong>comparison to the wild type. Indeed, production of AHLs was <strong>in</strong>creased <strong>in</strong>the mutant stra<strong>in</strong>s, while overproduction of RNase E resulted <strong>in</strong> a strongdecrease of the AHL amounts. Analysis of genes <strong>in</strong>volved <strong>in</strong> AHLs productionshowed that balanced expression of RNase E ans RNase J is important for theposttranscriptional control of quorum sens<strong>in</strong>g <strong>in</strong> S. meliloti.1. Evguenieva-Hackenberg E, Klug G. (2009) New aspects of RNA process<strong>in</strong>g <strong>in</strong> prokaryotes.Curr. Op<strong>in</strong>.Microbiol. 14(5):587-92.2. Pobigaylo, N, Wetter, D, Szymczak, S, Schiller, U, Kurtz, S, Meyer, F, Nattkemper, TW, Becker, A.(2006) Construction of a large signature-tagged m<strong>in</strong>i-Tn5 transposon library and its application tomutagenesis ofS<strong>in</strong>orhizobium meliloti.Appl Environ Microbiol, 72, 4329-4337.3. Madhugiri R, Evguenieva-Hackenberg E. (2009) RNase J is <strong>in</strong>volved <strong>in</strong> the 5'-end maturation of 16SrRNA and 23S rRNA <strong>in</strong>S<strong>in</strong>orhizobium meliloti.FEBS Lett, 583, 2339-2342.SMP045Change of microbial community composition due togeothermal use of the subsurfaceA. Westphal* 1 , A. Jesußek 2 , M. Alawi 1 , A. Dahmke 2 , H. Würdemann 11 GeoForschungsZentrum Potsdam, ICGR, Potsdam, Germany2 Universität Kiel, Angewandte Geowissenschaften, Kiel, GermanySeasonal heat storage systems for district heat<strong>in</strong>g and build<strong>in</strong>gclimatisation are of <strong>in</strong>creas<strong>in</strong>g importance to secure a susta<strong>in</strong>able energyuse and supply. For an efficient and permanent reliable use of geothermalenergy the impact on the environment has to be evaluated.Our presentation encompasses a study of a lab-scale column experiment toquantify the effects of different temperatures on solution, precipitation andmicrobially catalysed redox processes.Four different tempered columns (10, 25, 40, 70°C) were operated andsodium actetate was added cont<strong>in</strong>uously. To characterize the microbialbiocenosis of the <strong>in</strong>itial sediment samples, fluid samples from the upperexit and also over the profile (9 sampl<strong>in</strong>g ports) were collected. Allsamples were analysed based on partial 16S rDNA. Among f<strong>in</strong>gerpr<strong>in</strong>t<strong>in</strong>gmethods (PCR-DGGE) for the characterization of the microbialbiocenosis, qPCR and FISH will be applied for the quantification ofmicroorganisms and the determ<strong>in</strong>ation of their metabolic activity.Sulfate reduction <strong>in</strong> all columns was detected with the highest reductionrates at 40°C. First f<strong>in</strong>gerpr<strong>in</strong>t<strong>in</strong>g results show a shift of the dom<strong>in</strong>antmicroorganisms due to the different temperatures. Additionally, themicrobial composition <strong>in</strong> the 10°C column changed clearly <strong>in</strong> between thedifferent sampl<strong>in</strong>g ports of the column. Methane production was measured at25°C correlat<strong>in</strong>g with Archaea occurrence.Lab-scale column experiments showed an alteration <strong>in</strong> the microbial biocenosisdue to geothermal <strong>in</strong>duced temperature effects. The identification ofmicroorganisms enables the correlation to metabolic classes and provides<strong>in</strong>formation about biochemical processes <strong>in</strong> the used groundwater system andtherewith the impact on plant operation as well as environment.Consequently, plasmids play a major role <strong>in</strong> enhanc<strong>in</strong>g the geneticdiversity and adaptation of bacteria as agents of horizontal gene transfer(HGT). IncP-9 plasmids are very important vehicles for degradation andresistance genes that are assumed to contribute to the adaption of bacterialcommunities <strong>in</strong> environments contam<strong>in</strong>ated with xenobiotic compoundssuch as biofilters that are used for microbial degradation of pesticides. Inthis study the abundance and diversity of IncP-9 plasmids <strong>in</strong> six differentbiofilters (three replicates per biofilter) from Belgium was analyzed.Anewly developed primer system target<strong>in</strong>g therep-oriVregion (S1: 610 bp)was used for PCR amplification from total community DNA. Southern blothybridization confirmed the presence of IncP-9 plasmid specific sequences<strong>in</strong> all biofilters with one exception. In order to obta<strong>in</strong> <strong>in</strong>sights <strong>in</strong>to thediversity of the IncP-9 plasmids, amplicons obta<strong>in</strong>ed from biofilters 1(Leefdaal), 2 (Pcfruit) and 5 (Kortrijk), that showed the strongest IncP-9signals, were cloned and sequenced. In addition, a quantitative real timePCR system (S2: ~200 bp) was established <strong>in</strong> order to quantify IncP-9abundance. The log10 transformed ratio of IncP-9 to16S rRNA genecopies varied from -3.1 to -2.65. To validate the specificity of the qPCRprimer system, the amplicons were also cloned and sequenced. Bothsystems specifically amplified IncP-9 sequences from total communityDNA. While all sequences amplified with both primer systems frombiofilter 5 showed a high sequence similarity to IncP-9 (pNL15),sequences obta<strong>in</strong>ed from biofilter 1 and biofilter 2 were more diverse,affiliated to the IncP-9a (pMT3 - biofilter 2), IncP-9b (pWW0 - biofilter1), IncP-9d (pNAH7; only obta<strong>in</strong>ed with S1- biofilter 2) and IncP-9 (pNL15 - biofilters 1 and 2). In addition several novel sequences onlydistantly affiliated to the clusters def<strong>in</strong>ed by Sevastsyanovich et al., 2008were obta<strong>in</strong>ed from biofilters 1 and 2. Interest<strong>in</strong>gly only a small number ofidentical sequences were picked up with both systems <strong>in</strong>dicat<strong>in</strong>g asurpris<strong>in</strong>gly high sequence diversity of IncP-9 plasmids <strong>in</strong> biofilters.This work was supported by the EU project METAEXPLORE and the DFG project SM59/8-1Sevastsyanovich, Y.R., R. Krasowiak, L.E.H. B<strong>in</strong>gle, A.S. Ha<strong>in</strong>es, S.L. Sokolov, I.A. Kosheleva,A.A. Leuchuk, M.A. Titok, K. Smalla, and C.M. Thomas.2008. Diversity of IncP-9 plasmids ofPseudomonas. Microbiology 154, 2929-2941.SMP047M<strong>in</strong>erals and charcoal - factors shap<strong>in</strong>g microbial communitycomposition and bacterial response to phenanthrene <strong>in</strong>artificial soilsD. Bab<strong>in</strong>* 1 , G.-C. D<strong>in</strong>g 1 , G.J. Pronk 2 , H. Heuer 1 , K. Heister 2 , I. Kögel-Knabner 2 , K. Smalla 11 Julius Kühn-Institut, Bundesforschungs<strong>in</strong>stitut für Kulturpflanzen, Institut fürEpidemiologie und Pathogendiagnostik, Braunschweig, Germany2 Technische Universität München, Lehrstuhl für Bodenkunde, Freis<strong>in</strong>g,GermanyIn soil, different organic, <strong>in</strong>organic and biological constituents arecontact<strong>in</strong>g each other and form<strong>in</strong>g large biogeochemical <strong>in</strong>terfaces. Their<strong>in</strong>teractions are poorly understood and therefore this study explored the<strong>in</strong>fluences of soil m<strong>in</strong>erals and charcoal on microbial communities. Due toproblematic comparison of natural soils, <strong>in</strong> a microcosm experiment sevenartificial soils were composed vary<strong>in</strong>g <strong>in</strong> clay m<strong>in</strong>erals (illite,montmorillonite), metal oxides (ferrihydrite, boehmite) and charcoal. Thesame aliquots of the microbial fraction extracted from Cambisol were usedas <strong>in</strong>itial microbial community and autoclaved manure as nutrient sourcefor each artificial soil. Incubation took place under constant environmentalconditions up to 18 months (sampl<strong>in</strong>g on day 1, 9, 31, 90, 180, 460, 450).Total community DNA was extracted and the 16S rRNA gene and ITSamplicons for Bacteria or Fungi, respectively, were used <strong>in</strong> denatur<strong>in</strong>ggradient gel electrophoresis (DGGE) to generate molecular f<strong>in</strong>gerpr<strong>in</strong>ts.DGGE analysis showed that m<strong>in</strong>eral composition and charcoal <strong>in</strong>fluencethe establishment of microbial communities <strong>in</strong> artificial soils, even after along <strong>in</strong>cubation time. Especially the charcoal soil showed pronounceddifferences <strong>in</strong> the DGGE pattern compared to other artificial soils withoutcharcoal.To explore the response of the established microbial communities topersistent organic pollutants, one-year old artificial soils were spiked withphenanthrene (2 g/kg) and <strong>in</strong>cubated for another 70 days. By DGGE, shifts<strong>in</strong> the bacterial but not fungal communities were revealed between nonspikedand phenanthrene-contam<strong>in</strong>ated samples. Interest<strong>in</strong>gly, bacterialcommunities of different artificial soils showed dist<strong>in</strong>ct phenanthreneresponses. By plat<strong>in</strong>g, higher bacterial counts were found <strong>in</strong> soils treated withphenanthrene.In conclusion, m<strong>in</strong>erals and charcoal <strong>in</strong> artificial soils shaped the compositionof microbial communities and the bacterial response to phenanthrene.SMP046Characterization of IncP-9 <strong>in</strong> different biofilters from Belgiumcontam<strong>in</strong>ated with pesticidesS. DealtryJulius Kühn-Institut , EP, Braunschweig, GermanyConjugative plasmids seem to be one of the mobile genetic elements mostresponsible for the rapid adaptation to environmental selective pressure.BIOspektrum | Tagungsband <strong>2012</strong>
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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Instruments that are music to your
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General Information2012 Annual Conf
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SPONSORS & EXHIBITORS9Sponsoren und
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11BIOspektrum | Tagungsband 2012
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13BIOspektrum | Tagungsband 2012
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16 AUS DEN FACHGRUPPEN DER VAAMFach
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22 AUS DEN FACHGRUPPEN DER VAAMMitg
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24 INSTITUTSPORTRAITin the differen
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26 INSTITUTSPORTRAITProf. Dr. Lutz
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28 CONFERENCE PROGRAMME | OVERVIEWS
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30 CONFERENCE PROGRAMME | OVERVIEWT
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32 CONFERENCE PROGRAMMECONFERENCE P
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34 CONFERENCE PROGRAMMECONFERENCE P
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36 SPECIAL GROUPSACTIVITIES OF THE
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38 SPECIAL GROUPSACTIVITIES OF THE
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40 SPECIAL GROUPSACTIVITIES OF THE
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42 SHORT LECTURESMonday, March 19,
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44 SHORT LECTURESMonday, March 19,
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46 SHORT LECTURESTuesday, March 20,
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48 SHORT LECTURESWednesday, March 2
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50 SHORT LECTURESWednesday, March 2
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52ISV01Die verborgene Welt der Bakt
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54protein is reversibly uridylylate
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56that this trapping depends on the
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58Here, multiple parameters were an
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60BDP016The paryphoplasm of Plancto
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62of A-PG was found responsible for
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64CEV012Synthetic analysis of the a
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66CEP004Investigation on the subcel
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68CEP013Role of RodA in Staphylococ
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70MurNAc-L-Ala-D-Glu-LL-Dap-D-Ala-D
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72CEP032Yeast mitochondria as a mod
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74as health problem due to the alle
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76[3]. In summary, hypoxia has a st
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78This different behavior challenge
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80FUP008Asc1p’s role in MAP-kinas
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82FUP018FbFP as an Oxygen-Independe
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84defence enzymes, were found to be
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86DNA was extracted and shotgun seq
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88laboratory conditions the non-car
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90MEV003Biosynthesis of class III l
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92provide an insight into the regul
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94MEP007Identification and toxigeni
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96various carotenoids instead of de
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98MEP025Regulation of pristinamycin
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100that the genes for AOH polyketid
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102Knoll, C., du Toit, M., Schnell,
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104pathogenicity of NDM- and non-ND
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106MPV013Bartonella henselae adhesi
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108Yfi regulatory system. YfiBNR is
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110identification of Staphylococcus
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112that a unit increase in water te
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114MPP020Induction of the NF-kb sig
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116[3] Liu, C. et al., 2010. Adhesi
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118virulence provides novel targets
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120proteins are excreted. On the co
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122MPP054BopC is a type III secreti
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124MPP062Invasiveness of Salmonella
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126Finally, selected strains were c
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128interactions. Taken together, ou
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130forS. Typhimurium. Uncovering th
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132understand the exact role of Fla
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134heterotrimeric, Rrp4- and Csl4-c
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136OTV024Induction of systemic resi
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13816S rRNA genes was applied to ac
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140membrane permeability of 390Lh -
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142bacteria in situ, we used 16S rR
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144bacteria were resistant to acid,
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1461. Ye, L.D., Schilhabel, A., Bar
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148using real-time PCR. Activity me
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150When Ms. mazei pWM321-p1687-uidA
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152OTP065The role of GvpM in gas ve
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154OTP074Comparison of Faecal Cultu
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156OTP084The Use of GFP-GvpE fusion
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158compared to 20 ºC. An increase
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160characterised this plasmid in de
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162Streptomyces sp. strain FLA show
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164The study results indicated that
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166have shown direct evidences, for
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168biosurfactant. The putative lipo
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170the absence of legally mandated
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172where lowest concentrations were
- Page 174 and 175: 174PSV008Physiological effects of d
- Page 176 and 177: 176of pH i in vivo using the pH sen
- Page 178 and 179: 178PSP010Crystal structure of the e
- Page 180 and 181: 180PSP018Screening for genes of Sta
- Page 182 and 183: 182In order to overproduce all enzy
- Page 184 and 185: 184substrate specific expression of
- Page 186 and 187: 186potential active site region. We
- Page 188 and 189: 188PSP054Elucidation of the tetrach
- Page 190 and 191: 190family, but only one of these, t
- Page 192 and 193: 192network stabilizes the reactive
- Page 194 and 195: 194conditions tested. Its 2D struct
- Page 196 and 197: 196down of RSs2430 influences the e
- Page 198 and 199: 198demonstrating its suitability as
- Page 200 and 201: 200RSP025The pH-responsive transcri
- Page 202 and 203: 202attracted the attention of molec
- Page 204 and 205: 204A (CoA)-thioester intermediates.
- Page 206 and 207: 206Ser46~P complex. Additionally, B
- Page 208 and 209: 208threat to the health of reefs wo
- Page 210 and 211: 210their ectosymbionts to varying s
- Page 212 and 213: 212SMV008Methanol Consumption by Me
- Page 214 and 215: 214determined as a function of the
- Page 216 and 217: 216Funding by BMWi (AiF project no.
- Page 218 and 219: 218broad distribution in nature, oc
- Page 220 and 221: 220SMP027Contrasting assimilators o
- Page 222 and 223: 222growing all over the North, Cent
- Page 226 and 227: 226labelled hydrocarbons or potenti
- Page 228 and 229: 228SSV009Mathematical modelling of
- Page 230 and 231: 230SSP006Initial proteome analysis
- Page 232 and 233: 232nine putative PHB depolymerases
- Page 234 and 235: 234[1991]. We were able to demonstr
- Page 236 and 237: 236of these proteins are putative m
- Page 238 and 239: 238YEV2-FGMechanistic insight into
- Page 240 and 241: 240 AUTORENAbdel-Mageed, W.Achstett
- Page 242 and 243: 242 AUTORENFarajkhah, H.HMP002Faral
- Page 244 and 245: 244 AUTORENJung, Kr.Jung, P.Junge,
- Page 246: 246 AUTORENNajafi, F.MEP007Naji, S.
- Page 249 and 250: 249van Dijk, G.van Engelen, E.van H
- Page 251 and 252: 251Eckhard Boles von der Universit
- Page 253 and 254: 253Anna-Katharina Wagner: Regulatio
- Page 255 and 256: 255Vera Bockemühl: Produktioneiner
- Page 257 and 258: 257Meike Ammon: Analyse der subzell
- Page 259 and 260: springer-spektrum.deDas große neue