216Fund<strong>in</strong>g by BMWi (AiF project no. 16224 N) is gratefully acknowledged.SMP008Will be presented as SMV017!SMP009Role of nitrite accumulation and m<strong>in</strong>eral nucleation sites forFe(II) oxidation by the nitrate-reduc<strong>in</strong>g Acidovorax sp. stra<strong>in</strong>BoFeN1N. Kluegle<strong>in</strong>*, U. Dippon*, C. Pantke, A. KapplerCenter for Applied Geoscience, Geomicrobiology, Tueb<strong>in</strong>gen, GermanyAnaerobic, neutrophilic nitrate-reduc<strong>in</strong>g Fe(II)-oxidiz<strong>in</strong>g bacteria can befound <strong>in</strong> anoxic environments and were suggested to play a key role <strong>in</strong> ironm<strong>in</strong>eral formation and N-cycl<strong>in</strong>g under these conditions. In order tounderstand the coupl<strong>in</strong>g of the microbial iron and nitrogen cycles <strong>in</strong> anoxicenvironments as well as the effect of m<strong>in</strong>eral nucleation sites on ironm<strong>in</strong>eral formation, we conducted batch experiments with the nitratereduc<strong>in</strong>g,iron(II)-oxidiz<strong>in</strong>g bacterium Acidovorax sp. BoFeN1, which wasisolated from anoxic littoral sediments <strong>in</strong> Lake Constanze [1].Dur<strong>in</strong>g denitrifaction nitrite can be formed, which is known to oxidizeFe(II) abiotically [2]. This raises the question whether the oxidation offerrous iron is <strong>in</strong>deed enzymatically catalyzed or whether it is just achemical reaction as a consequence of microbial nitrite formation dur<strong>in</strong>gacetate oxidation by the mixotrophic Fe(II)-oxidiz<strong>in</strong>g stra<strong>in</strong>s. In order toshed light on this question we grew stra<strong>in</strong> BoFeN1<strong>in</strong> the absence andpresence of iron and quantified nitrite formation dur<strong>in</strong>g denitrification.Additionally, we <strong>in</strong>cubated BoFeN1 with nitrous oxide (N 2O) as electronacceptor and either acetate or acetate/Fe(II) as electron donors tocircumvent the problem of nitrite formation. These experiments showedthat microbially formed nitrite contributes significantly to Fe(II) oxidationand has to be considered <strong>in</strong> the overall Fe(II) oxidation budget.In order to identify the <strong>in</strong>fluence of m<strong>in</strong>eral surfaces of microbial Fe(II)oxidation products, we used 57 Fe-specific Mössbauer spectroscopy and57 Fe(II)-spiked growth medium <strong>in</strong> comb<strong>in</strong>ation with seed<strong>in</strong>g m<strong>in</strong>erals ofnatural isotopic composition to identify the m<strong>in</strong>eral products formed fromthe dissolved Fe(II) dur<strong>in</strong>g Fe(II) oxidation. Analysis of Mössbauer spectraof microbial products showed that <strong>in</strong> the absence of nucleation sitem<strong>in</strong>erals, stra<strong>in</strong> BoFeN1 produces goethite (-FeOOH). The presence ofmagnetite (Fe 3O 4) <strong>in</strong>duced the formation of magnetite besides goethitewhile the presence of hematite (-Fe 2O 3) nucleation sites did not <strong>in</strong>ducehematite formation but only goethite was formed. This study showed thatm<strong>in</strong>eral formation not only depends on geochemical conditions but canalso be controlled by the presence of m<strong>in</strong>eral nucleation sites that <strong>in</strong>itiateprecipitation of certa<strong>in</strong> m<strong>in</strong>eral phases.1 A. Kappler, B. Sch<strong>in</strong>k, D. K. Newman, Geobiology, 3 (2005) 235-245.2 O. Van Cleemput & L. Baert, Soil Biol. Biochem., 15 (1983) 137-140.SMP010Molecular characterization of nitrogen-fix<strong>in</strong>g bacteria andtheir colonization pattern <strong>in</strong> mangrove rootsG. Alfaro-Esp<strong>in</strong>oza*, M. UllrichJacobs University Bremen gGmbH, Molecular Microbiology, Research II,Bremen, GermanyNitrogen-fix<strong>in</strong>g bacteria play a major role <strong>in</strong> re-m<strong>in</strong>eralization processes <strong>in</strong>mangrove ecosystems. Anaerobic processes like denitrification take place<strong>in</strong> the anoxic layers of mangrove sediments. Consequently, most of thenitrogen is lost and thus no longer available for metabolic processes <strong>in</strong>plants. Previous studies had shown that nitrogen-fix<strong>in</strong>g bacteria <strong>in</strong>teractwith mangrove roots mak<strong>in</strong>g nitrogen available for plants. Although,nitrogen fixation is a very important process <strong>in</strong> mangrove ecosystems, verylittle is known about bacterial colonization strategies and physiologicalimpacts on mangrove roots. Additionally, virtually noth<strong>in</strong>g is known aboutbacterial genes particularly required and expressed dur<strong>in</strong>g the <strong>in</strong>teractionof bacteria with mangrove plants. The establishment of a nitrogen-fix<strong>in</strong>gbacterium-mangrove <strong>in</strong>teraction model system is necessary to study themolecular mechanisms of this <strong>in</strong>teraction. The aim of the current<strong>in</strong>vestigation was to first isolate and characterize nitrogen-fix<strong>in</strong>g bacteriaassociated with root material of Avicennia sp. and Rhizophora mangle.Subsequently, the colonization patterns of selected bacterial stra<strong>in</strong>s onmangrove roots had to be <strong>in</strong>vestigated. Nitrogen-free medium was used forthe isolation of 9 bacterial stra<strong>in</strong>s assigned to two different phylogeneticclasses. Isolates were characterized <strong>in</strong> terms of their ability to fixatmospheric nitrogen, their phylogenetic affiliation us<strong>in</strong>g 16S rRNA genesequenc<strong>in</strong>g, their genetic accessibility, and their ability to survive andcolonize mangrove roots when <strong>in</strong>oculated with different other sedimentborne<strong>in</strong>digenous bacterial stra<strong>in</strong>s (fitness test). The mangrove rootcolonization patterns of two isolates, Halomonas sp. and Vibrio sp., werefollowed by confocal laser scann<strong>in</strong>g microscopy. Here<strong>in</strong>, it was demonstratedthat some of the diazotrophs were genetically accessible and were coloniz<strong>in</strong>gmangrove plants. These isolates are promis<strong>in</strong>g candidates to establish a cell-tocellbacteria-mangrove model system to cont<strong>in</strong>ue our <strong>in</strong>vestigation of themolecular mechanisms determ<strong>in</strong><strong>in</strong>g bacteria-mangrove <strong>in</strong>teractions.SMP011Effect of Oxygen Availability on Microbial Chit<strong>in</strong> Degraders<strong>in</strong> an Agricultural SoilA. Wieczorek*, S. Hetz, H.L. Drake, S. KolbUniversity of Bayreuth, Ecological Microbiology, Bayreuth, GermanyChit<strong>in</strong> is a biopolymer consist<strong>in</strong>g of alternat<strong>in</strong>g -1,4-l<strong>in</strong>ked N-acetylglucosam<strong>in</strong>e residues, and is the second most abundant organiccompound of terrestrial biomass. In an unsaturated soil, oxygendistribution is highly heterogeneous, and dynamic on the micro- tomillimeter scale. Therefore, different redox processes, such asfermentation or oxygen respiration, can simultaneously be active on thedegradation of chit<strong>in</strong>. In a wheat-planted soil from KlostergutScheyern,oxygen availability impacted differentially on the activation ofredox processes and activity of bacterial taxa dur<strong>in</strong>g cellulose degradation.The objective of the current study was to evaluate the effect of oxygenavailability on microbial processes and taxa dur<strong>in</strong>g degradation of chit<strong>in</strong>and its hydrolysis products N-acetylglucosam<strong>in</strong>e and glucosam<strong>in</strong>e.Supplemental chit<strong>in</strong>, N-acetylglucosam<strong>in</strong>e, and glucosam<strong>in</strong>e werecompletely m<strong>in</strong>eralized to carbon dioxide under oxic conditions.Concentrations of ammonium and nitrate <strong>in</strong>creased <strong>in</strong> the chit<strong>in</strong>supplementedtreatment, which suggested a release of ammonium byammonification, and subsequent oxidation of ammonium to nitrate bynitrifiers. Chit<strong>in</strong>, N-acetylglucosam<strong>in</strong>e, and glucosam<strong>in</strong>e wereanaerobically metabolized to carbon dioxide, molecular hydrogen,methane, acetate, propionate, and butyrate. Nitrate was completelyconsumed dur<strong>in</strong>g the experiment, and the soil microcosms went black,which <strong>in</strong>dicated precipitation of ferrous iron. Thus, respiration of nitrateand ferric iron by soil microbes was active. The f<strong>in</strong>d<strong>in</strong>gs suggest thatoxygen availability differentially activated redox guilds (aerobes,fermenters, nitrate and ferric iron reducers) dur<strong>in</strong>g the degradation ofchit<strong>in</strong>. The identity of the activated chit<strong>in</strong>olytic taxa is currently under<strong>in</strong>vestigation by analysis of 16S rRNA and chit<strong>in</strong>ase genes.SMP012Ammonification and nitrification rates depend on soil andland use type of subtropical savannah soilsK. Huber*, P. Wüst, B. Fösel, J. OvermannLeibniz Institute DSMZ-German Collection of Microorganisms and CellCultures, Department of Microbial Ecology and Diversity Research,Braunschweig, GermanyDrylands (i.e., arid, semiarid, and subhumid areas) cover approximately40% of earth´s terrestrial surface and the percentage <strong>in</strong>creases due toclimate change. However, over one billion people depend on agriculture <strong>in</strong>these disadvantaged regions. Besides water supply, nutrients likeammonium and nitrate limit plant production <strong>in</strong> these areas. In the presentstudy, ammonification and nitrification - N-liberat<strong>in</strong>g processes that arema<strong>in</strong>ly driven by microorganisms - were quantified by the Pool DilutionTechnique (PDT). In this approach, 15 N-ammonium and 15 N-nitrate areadded to the soil to <strong>in</strong>crease the 15/14 N ratio and changes of the 15/14 N ratiodur<strong>in</strong>g an <strong>in</strong>cubation experiment allow the calculation of grossammonification and nitrification rates. Sampl<strong>in</strong>g sites were located <strong>in</strong>North-Eastern Namibia south of the Okavango river. The soil samplesdiffered with respect to soil type (sand, i.e., Kalahari sands, and loamysand, i.e., old flood pla<strong>in</strong> soils) and land use type (fallow, drought andirrigation agriculture, bushland, and riparian woodland). First results of thePDT <strong>in</strong>dicate that microorganisms responsible for ammonification andnitrification seem to be ma<strong>in</strong>ly <strong>in</strong>fluenced by soil type rather than land usetype. Ammonification rates were highest <strong>in</strong> woodlands on loamy sands andlowest <strong>in</strong> fallow and drought agricultures. In contrast, nearly noammonification and nitrification was detected <strong>in</strong> the Kalahari sands. Theseresults are <strong>in</strong> agreement with CO 2 production rates which were highest <strong>in</strong>woodland soils from old flood pla<strong>in</strong>s, <strong>in</strong>dicat<strong>in</strong>g highest microbialactivities <strong>in</strong> these undisturbed soils.SMP013Culturability of novel Acidobacteria <strong>in</strong> German grass- andwoodland soilsV. Baumgartner*, P. Wüst, B. Fösel, J. OvermannLeibniz Institute DSMZ - German Collection of Microorganisms and CellCultures, Braunschweig, Department of Microbial Ecology and DiversityResearch, Braunschweig, GermanyAcidobacteria on average account for 20% of all soil bacteria and arephysiologically active <strong>in</strong> situ. Culture-<strong>in</strong>dependent studies <strong>in</strong>dicate thatAcidobacteria are nearly as diverse as the Proteobacteria and currentlycomprise 26 dist<strong>in</strong>ct phylogenetic subdivisions (sd). However, until nowonly a few stra<strong>in</strong>s from sd 1, 3, and 8, have been validly described.Genome analysis revealed the ability of Acidobacteria to use complexBIOspektrum | Tagungsband <strong>2012</strong>
217substrates as carbon sources. With<strong>in</strong> the German BiodiversityExploratories project we focus on functional <strong>in</strong>terrelations betweenAcidobacteria and land use. Six extensively managed sites from theExploratories Schwäbische Alb, Ha<strong>in</strong>ich-Dün, and Schorfheide-Chor<strong>in</strong>,one grassland and one woodland soil per exploratory, were selected for ahigh throughput cultivation approach. Microtiter plates were <strong>in</strong>oculatedwith 10 and 50 cells per well, respectively, us<strong>in</strong>g five media at<strong>in</strong> situpH.The media tested conta<strong>in</strong>ed (i) highly diluted carbon sources (HD1:10), (ii)low amounts of sugars, fatty acids, and am<strong>in</strong>o acids (C-Mix), (iii) solublehumic acids (e.g., sodium salicylate, furfural, phthalic acid), (iv) <strong>in</strong>solublehumic acids (e.g., quercet<strong>in</strong>, coumestrol, solan<strong>in</strong>e), and (v) a mix ofpolymeric substrates (e.g., chit<strong>in</strong>, pect<strong>in</strong>, cellulose). Culturability of totalaerobes ranged from below 0.2% (Schorfheide-Chor<strong>in</strong>, grassland, solublehumic acids) to 9.2% (Schwäbische Alb, woodland, HD1:10).Acidobacteria-positve wells were identified via a specific PCR approach.The percentages of cultured Acidobacteria among all cultured Bacteriaranged from 0% (Schorfheide-Chor<strong>in</strong>, woodland, polymeric substrates) to19.5% (Schwäbische Alb, woodland, polymeric substrates). TheAcidobacteria recovered were affiliated with sd 1, 3, 4, and 6. Inpolymers-supplemented media, only representatives of sd 1 were detected.In contrast, most members of sd 6 Acidobacteria were cultivated <strong>in</strong> C-mixmedium. For both, total aerobes and Acidobacteria, cultivation successwas highest with media conta<strong>in</strong><strong>in</strong>g easily available carbon sources,<strong>in</strong>dicat<strong>in</strong>g that low amounts of these substrates favor growth of soilbacteria, <strong>in</strong> particular Acidobacteria.Characterization of novelAcidobacteria as relevant members of the soil microbial community willimprove our knowledge about biogeochemical cycl<strong>in</strong>g <strong>in</strong> soils.SMP014Carbon Isotope Fractionation of Italian Rice Field Soil underH 2 /CO 2 and different temperature regimes.M. Blaser*, R. ConradMax-Planck-Institute for terrestrial microbiology, biogeochemistry,Marburg, GermanyIn anoxic environments organic matter is fermented to short cha<strong>in</strong> fattyacids, alcohols as well as CO 2 and H 2. The two gaseous products can befurther converted to either methane by methanogenic archaea or to acetateby acetogenic bacteria. Methanogenesis is energetically more favourablethan acetogenesis. Nevertheless acetogens can outcompete methanogens atlow temperatures. To <strong>in</strong>vestigate the contribution of both processes we<strong>in</strong>cubated anoxic rice slurry under H 2/CO 2 at 15°, 30° and 50° C andfollowed the isotopic signatures of the carbon compounds (CO 2, CH 4,acetate) by mass spectrometry. For better differentiation of the twoprocesses a second <strong>in</strong>cubation was performed with bromoethanesulfonatean <strong>in</strong>hibitor of methanogenesis.SMP015Methanogens at the top of the worldK. Aschenbach* 1 , R. Angel 1 , K. Rehakova 2 , K. Janatkova 2 , R. Conrad 11 Max-Planck-Institute for terrestrial microbiology, biogeochemistry, Marburg,Germany2 Institute of Botany As CR, Trebon, Czech RepublicDeserts (semiarid, arid and hyperarid regions) cover around one third ofthe Earth´s surface. Desert soils are typically covered by a unique layertermed biological soil crust (BSC), a few millimetres thick and denselycolonized by microorganisms. Dur<strong>in</strong>g dry periods the BSC is mostly<strong>in</strong>active, but follow<strong>in</strong>g wett<strong>in</strong>g the microbial activity <strong>in</strong>creases and oxygenbecomes limit<strong>in</strong>g. It was previously shown that BSC from hot deserts canthen produce methane (1). We wanted to <strong>in</strong>vestigate whether thisphenomenon can also be observed <strong>in</strong> high-altitude cold deserts <strong>in</strong> theHimalayas (Ladakh, India). For this purpose, soil samples from threedifferent vegetation zones: semiarid, steppe, and subglacial, as well asfrom front and lateral mora<strong>in</strong>es of a reced<strong>in</strong>g glacier were collected andtested for the production of methane.We <strong>in</strong>cubated 5 g soil with 5 ml water at 25 °C under anoxic conditionsand followed up gas production (CH 4, CO 2 and H 2) and the isotopicsignature of the carbon <strong>in</strong> the CH 4 and CO 2. Almost each sample from thevegetation zones produced methane, and also some from the mora<strong>in</strong>etransects. Methane production was faster <strong>in</strong> the BSC compared to thedeeper soil layers, demonstrat<strong>in</strong>g that most methanogens are likely to beconcentrated at the top layer. The isotopic analysis showed that methaneprobably developed from both acetate and CO 2 with no significantdifference between the layers. Our results demonstrate the existence of anactive methanogenic community even at such extreme oxic environment.1. Angel R, Matthies D, Conrad R (2011) Activation of Methanogenesis <strong>in</strong> Arid Biological SoilCrusts Despite the Presence of Oxygen. PLoS ONE 6(5): e20453SMP016Community analyses of fermentative hydrogen producers <strong>in</strong>environmental samplesO. Schmidt*, M.A. Horn, H.L. DrakeUniversity of Bayreuth, Department of Ecological Microbiology, Bayreuth,United StatesFermenters produce Hydrogen (H 2) to excrete excess reductant.Fermentative H 2 production is catalyzed by either [FeFe]-hydrogenases(e.g., dur<strong>in</strong>g butyrate fermentation of Clostridium butyricum) or Group 4[NiFe]-hydrogenases (e.g., dur<strong>in</strong>g mixed acid fermentation of Escherichiacoli). Similarity correlations between <strong>in</strong> silico translated am<strong>in</strong>o acidsequences from publicly available hydrogenase genes and correspond<strong>in</strong>g16S rRNA genes showed that closely related hydrogenases (i.e., 80%am<strong>in</strong>o acid sequence similarity) belonged to host organisms with<strong>in</strong> thesame family. However, due to gene duplication and subsequentdiversification, distantly related hydrogenases did not necessarily belong tohosts of different families. Degenerate primers target<strong>in</strong>g [FeFe]- andGroup 4 [NiFe]-hydrogenase genes were developed to identify potentiallyactive hydrogen producers <strong>in</strong> environmental samples. [FeFe]-hydrogenasegene sequences obta<strong>in</strong>ed from a methane emitt<strong>in</strong>g fen were affiliated to theClostridia, Alpha- and Deltaproteobacteria, Chloroflexi, Bacteroidetes,Verrucomicrobia and Negativicutes. Group 4 [NiFe]-hydrogenase genesequences obta<strong>in</strong>ed from H 2-emmit<strong>in</strong>g earthworm gut content wereaffiliated to the Gammaproteobacteria, Clostridia and Verrucomicrobia.These results demonstrated that the new hydrogenase primers are usefulfor the detection of a wide range of [FeFe]- and Group 4 [NiFe]-hydrogenases <strong>in</strong> environmental samples and that 80% am<strong>in</strong>o acid sequencesimilarity is a reasonable cut-off to group hydrogenases from fermentativehydrogen producers on the family level.SMP017Electrochemical Quantification of Microbial Humic SubstanceReductionA. Piepenbrock* 1 , M. Sander 2 , A. Kappler 11 University of Tueb<strong>in</strong>gen, Geomicrobiology, Tüb<strong>in</strong>gen, Germany2 ETH Zurich, Institute of Biogeochemistry and Pollutant Dynamics,Zurich, SwitzerlandHumic substances (HS) are ubiquitous <strong>in</strong> soils, sediments and waters andhave been shown to shuttle electrons between microorganisms and poorlysoluble electron acceptors such as Fe(III) m<strong>in</strong>erals. S<strong>in</strong>ce HS can bereduced by a variety of microorganisms <strong>in</strong>clud<strong>in</strong>g Fe(III)-reduc<strong>in</strong>g,sulfate-reduc<strong>in</strong>g and dechlor<strong>in</strong>at<strong>in</strong>g bacteria, but also chemically forexample by sulfide, electron transfer via HS has the potential to contributesignificantly to the electron fluxes <strong>in</strong> the environment. While microbial HSreduction has been studied for a variety of different HS andmicroorganisms, these results were semi-quantitative due to <strong>in</strong>directquantification of HS redox states.We quantitatively followed the microbial reduction of HS of differentorig<strong>in</strong> (soil, peat, and aquatic) by the dissimilatory Fe(III)-reduc<strong>in</strong>gbacterium Shewanella oneidensis MR-1 us<strong>in</strong>g mediated electrochemicalreduction and oxidation. Microbial HS reduction resulted <strong>in</strong> a decrease <strong>in</strong>the number of electrons that could be transferred to the HSelectrochemically (electron accept<strong>in</strong>g capacity, EAC) and <strong>in</strong> a concomitant<strong>in</strong>crease <strong>in</strong> the number of electrons donated from the same HS to thework<strong>in</strong>g electrode (electron donat<strong>in</strong>g capacity, EDC). Thus, microbial HSreduction could be shown and the amount of electrons transferred from themicrobes to the HS could be quantified over time. Aeration of the cultureswith air resulted <strong>in</strong> an <strong>in</strong>crease <strong>in</strong> the EAC and a decrease <strong>in</strong> the EDC,<strong>in</strong>dicat<strong>in</strong>g the re-oxidation of the previously reduced moieties <strong>in</strong> the HS.Subsequently, the HS were re-reduced by the bacteria as could be seen <strong>in</strong> adecrease <strong>in</strong> the EAC and <strong>in</strong>crease <strong>in</strong> the EDC. These f<strong>in</strong>d<strong>in</strong>gs demonstratethe reversibility of the microbial HS reduction. Throughout the entireexperiment, the sum of EAC and EDC rema<strong>in</strong>ed constant, demonstrat<strong>in</strong>g thatmicrobial reduction did not alter the total number of redox active moieties <strong>in</strong> theHS. Overall, our results provide important new quantitative <strong>in</strong>sights <strong>in</strong>to theextent of microbial HS reduction and give new <strong>in</strong>dications about thesignificance of this process <strong>in</strong> environmental systems: HS redox reactions cancontribute significantly to the (trans)formation of iron m<strong>in</strong>erals and the(im)mobilization and reductive degradation of organic and <strong>in</strong>organic pollutantsand to the redox buffer capacity of systems such as peats.SMP018Biogeography of soil Burkholderia populationsN. Stopnisek* 1 , N. Fierer 2 , L. Eberl 1 , L. Weisskopf 11 University of Zurich, Institute of Plant Biology, Department ofMicrobiology, Zurich, Switzerland2 University of Colorado, Department of Ecology and EvolutionaryBiology, Boulder, CO, USA, United StatesThe genus Burkholderia is an important component of soil microbialcommunities and comprises over 60 species. Burkholderia species have aBIOspektrum | 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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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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40 SPECIAL GROUPSACTIVITIES OF THE
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42 SHORT LECTURESMonday, March 19,
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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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- 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 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 224 and 225: 224SMP044RNase J and RNase E in Sin
- 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