214determ<strong>in</strong>ed as a function of the redox gradient. Moreover, the energy thatis available to iron-convert<strong>in</strong>g microorganisms has been quantified withrespect to local geochemical gradients. The comb<strong>in</strong>ation of geochemical,m<strong>in</strong>eralogical, energetical and microbiological data allowed a detailed<strong>in</strong>vestigation of the spatial structure of the iron cycl<strong>in</strong>g throughout naturalredox gradients. First microcosm studies have been performed to<strong>in</strong>vestigate the competition for ferrous iron as electron donor for ironoxidiz<strong>in</strong>gbacteria. The obta<strong>in</strong>ed data allow to construct a conceptualmodel describ<strong>in</strong>g the substrate and electron donor/acceptor flux betweenthe areas of pronounced metabolic activity (i.e. different iron convert<strong>in</strong>gprocesses) <strong>in</strong> the elemental iron cycl<strong>in</strong>g throughout natural redox gradientsand the <strong>in</strong>terspecies substrate competition.SMV016Autotrophic Fe(II) oxidiz<strong>in</strong>g bacteria <strong>in</strong> the littoral sedimentof Lake Große FuchskuhleD. Kanaparthi* 1 , M. Dumont 1 , B. Pommerenke 1 , P. Casper 1,21 Max Plank Institute for Terrestrial Microbiology, Department ofBiogeochemistry, Marburg, Germany2 Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Stechl<strong>in</strong>,GermanyLake Große Fuchskuhle is a dystrophic acidic bog lake located <strong>in</strong> northernGermany. The primary objective of this study was to <strong>in</strong>vestigate theprocesses and microorganisms responsible for anaerobic CO 2 fixation <strong>in</strong>the littoral sediment. A time-course DNA-SIP approach was used us<strong>in</strong>g13 CO 2. Little or no CH 4 production was observed dur<strong>in</strong>g 12-week<strong>in</strong>cubation, suggest<strong>in</strong>g that conditions were not suitable formethanogenesis. Analysis of labeled 16S rRNA genes <strong>in</strong>dicated that only afew species had <strong>in</strong>corporated the13 CO 2, <strong>in</strong>clud<strong>in</strong>g a group ofBetaproteobacteria related to Gallionella and Sideroxydans species and agroup with<strong>in</strong> the Act<strong>in</strong>obacteria related to Acidimicrobium ferrooxidans.Previous studies have reported a high abundance of similar act<strong>in</strong>obacterial16S rRNA sequences <strong>in</strong> this and other humic bog lakes, but the ecologicalfunction and physiology of these organisms is unknown. As most of the16S rRNA genes sequenced from the heavy fraction are related toGallionella, Sideroxydans and Acidimicrobium which are known ironoxidiz<strong>in</strong>g bacteria (FeOB), we <strong>in</strong>vestigated the possibility that the labeledorganisms <strong>in</strong> this study were chemoautotrophic FeOB. Fe 2+ concentrationswere measured <strong>in</strong> the sediment and found to be 1.8 mM and enumerationby MPN method have shown the presence of 1x10 4 autotrophic and 1x10 7heterotrophic FeOB <strong>in</strong> the sediment. Anaerobic enrichment <strong>in</strong>cubationswere performed and it was shown that the Act<strong>in</strong>obacteria could be highlyenriched <strong>in</strong> the presence of Fe 2+ , CO 2 and NO - 3 , suggest<strong>in</strong>g they areautotrophic FeOB and could be us<strong>in</strong>g NO - 3 as a term<strong>in</strong>al electron acceptor.This study suggests that anaerobic chemoautotrophic FeOB may bedom<strong>in</strong>ant autotrophic bacteria <strong>in</strong> this lake and to our knowledge our resultsare the first to <strong>in</strong>dicate the autotrophy and a probable Nitrate dependentferrous iron oxidiz<strong>in</strong>g nature of theseAct<strong>in</strong>obacteria.SMP001Microbial iron(II) oxidation <strong>in</strong> littoral freshwater lakesediments: Competition between phototrophic vs. nitratereduc<strong>in</strong>giron(II)-oxidizersE.D. Melton*, C. Schmidt, A. KapplerUniversität Tüb<strong>in</strong>gen, Geowissenschaften, Tüb<strong>in</strong>gen, GermanyThe temporal and spatial distribution of neutrophilic microbial ironoxidation is ma<strong>in</strong>ly determ<strong>in</strong>ed by local physico-chemical gradients ofoxygen, light, nitrate and ferrous iron. In the anoxic part of the top layer oflittoral freshwater lake sediments, nitrate-reduc<strong>in</strong>g and phototrophiciron(II)-oxidizers compete for the same electron donor; reduced iron.Though a conceptual framework for biogeochemical iron cycl<strong>in</strong>g has beenproposed 1 , it is not yet understood how these microbes co-exist <strong>in</strong> thesediment, what their spatial distribution is relative to one another and whatrole they play <strong>in</strong> the overall iron cycle. In this study we show that bothmetabolic types of anaerobic Fe(II)-oxidiz<strong>in</strong>g microorganisms are present<strong>in</strong> the same sediment layer directly beneath the oxic-anoxic sediment<strong>in</strong>terface. The photoferrotrophic MPNs counted 3.4·10 5 cells·g -1 and theautotrophic and mixotrophic nitrate-reduc<strong>in</strong>g Fe(II)-oxidizers totalled1.8·10 4 and 4.5·10 4 cells·g -1 dry weight sediment, respectively.Additionally, <strong>in</strong> order to dist<strong>in</strong>guish between the two microbial Fe(II)oxidation processes and to assess their <strong>in</strong>dividual contribution to thesedimentary iron cycle, littoral lake sediment was <strong>in</strong>cubated <strong>in</strong> microcosmswith various additives. We found that nitrate-reduc<strong>in</strong>g Fe(II)-oxidiz<strong>in</strong>gbacteria exhibited a higher maximum Fe(II) oxidation rate per cell <strong>in</strong> bothpure cultures and microcosms than achieved by photoferrotrophs.However, where photoferrotrophs <strong>in</strong>stantly started oxidiz<strong>in</strong>g Fe(II),nitrate-reduc<strong>in</strong>g Fe(II)-oxidizers showed a significant lag-phase <strong>in</strong>microcosms dur<strong>in</strong>g which time they probably use organics as electrondonor before they <strong>in</strong>itiated Fe(II) oxidation. This suggests that nitratereduc<strong>in</strong>gFe(II)-oxidizers will be outcompeted by photoferrotrophic Fe(II)-oxidizers dur<strong>in</strong>g optimal light conditions due to Fe(II) limitations, asphototrophs deplete Fe(II) before nitrate-reduc<strong>in</strong>g Fe(II)-oxidizers startFe(II) oxidation. Thus, the co-existence of the two anaerobic Fe(II)-oxidizers may be possible due to a niche space separation <strong>in</strong> time by theday night cycle, where nitrate-reduc<strong>in</strong>g Fe(II)-oxidizers oxidize Fe(II)dur<strong>in</strong>g the night and phototrophs play a dom<strong>in</strong>ant role <strong>in</strong> Fe(II) oxidationdur<strong>in</strong>g daylight hours. Furthermore, metabolic flexibility of Fe(II)-oxidiz<strong>in</strong>g microorganisms may play a paramount role <strong>in</strong> the conservationof the sedimentary Fe cycle.1. C. Schmidt, S. Behrens and A. Kappler, Environmental Chemistry7(2010), p399-405SMP002Intermediary Ecosystem Metabolism <strong>in</strong> Different CH 4 -emitt<strong>in</strong>g Peatland SoilsS. Hunger*, C. Bruß, M. Eppendorfer, A.S. Gößner, H.L. DrakeUniversity Bayreuth, Department of Ecological Microbiology, Bayreuth,GermanyNatural wetlands such as bogs and fens contribute up to approximately40% to the global emission of methane. Biopolymers <strong>in</strong> peatland soils areanaerobically degraded via <strong>in</strong>termediary events that term<strong>in</strong>ate <strong>in</strong> theemission of methane (i.e., collectively ‘<strong>in</strong>termediary ecosystemmetabolism’). Glucose, acetate, and H 2-CO 2 have been observed tostimulate <strong>in</strong>termediary events (i.e., fermentation, acetogenesis) andterm<strong>in</strong>al events (i.e., methanogenesis) <strong>in</strong> anoxic microcosms of soils fromthe regional fen Schlöppnerbrunnen. The stimulation of glucose-, acetate-,and H 2-CO 2-dependent processes were analyzed <strong>in</strong> different regionalpeatland soils and compared to the <strong>in</strong>termediary ecosystem metabolism ofthe fen Schlöppnerbrunnen. Peatland soils were diluted with m<strong>in</strong>eralmedium and <strong>in</strong>cubated <strong>in</strong> the dark under anoxic conditions. The microbialcommunity <strong>in</strong> soil microcosms were evaluated with mcrA/mrtA (encodefor the alpha-subunit of methyl-CoM reductases I and II) and bacterial 16SrRNA genes. Glucose-dependent fermentation was stimulated <strong>in</strong> all soilmicrocosms, but product profiles differed between sampl<strong>in</strong>g sides.Propionate, butyrate, and CO 2 accumulated as end products <strong>in</strong> all soilmicrocosms. Ethanol, H 2, and acetate accumulated as end products <strong>in</strong> soilmicrocosms from some peatland soils or were partially degraded <strong>in</strong> others.Formate was transiently detected <strong>in</strong> glucose-supplemented soilmicrocosms from some peatland soils. Hydrogenotrophic methanogenesiswas stimulated <strong>in</strong> all soil microcosms, whereas acetoclasticmethanogenesis and H 2-dependent acetogenesis were stimulated <strong>in</strong> most ofthe soil microcosms. Most abundant taxa under <strong>in</strong> situ conditions <strong>in</strong> one ofthe fen soils were Acidobacteria, Anaerol<strong>in</strong>eae, unclassified and noveltaxa, whereas Acidobacteria, Alphaproteobacteria, unclassified and novel taxawere most abundant <strong>in</strong> one of the peat bog soils under <strong>in</strong> situ conditions.Methanogens of the contrast<strong>in</strong>g soils were also resolved. The collective resultsre<strong>in</strong>force the likelihood that the <strong>in</strong>termediary ecosystem metabolism differsbetween different peatland soils and that Acidobacteria-related taxa as well ashitherto unknown taxa are <strong>in</strong>tegrated to the ‘<strong>in</strong>termediary ecosystemmetabolism’ and the emission of methane <strong>in</strong> the peatland soils.SMP003Mobilization of cadmium from Fe(III) (oxyhydr)oxides dur<strong>in</strong>gmicrobial Fe(III) reduction <strong>in</strong> cadmium-contam<strong>in</strong>ated soilE.M. Muehe* 1 , U. Kraemer 2 , A. Kappler 11 University of Tueb<strong>in</strong>gen, Geomicrobiology, Tueb<strong>in</strong>gen, Germany2 Ruhr-University Bochum, Plant Physiology, Bochum, GermanySoils worldwide have <strong>in</strong>creas<strong>in</strong>gly been contam<strong>in</strong>ated with <strong>in</strong>dustrialwaste metals, <strong>in</strong>clud<strong>in</strong>g cadmium, which may subsequently enter the foodcha<strong>in</strong> through agriculturally used plants. These contam<strong>in</strong>ant metals<strong>in</strong>fluence the natural ecosystem drastically and can have dramatic effectson human health. Hence, there is a need for the development andapplication of new techniques to efficiently remediate contam<strong>in</strong>ated soils.In the study presented here, we comb<strong>in</strong>ed phytoremediation andmicrobially enhanced natural attenuation to determ<strong>in</strong>e whether a moretime- and cost-efficient removal of cadmium from contam<strong>in</strong>ated sites isachieved. A cadmium-tolerant Fe(III)-reduc<strong>in</strong>g bacterium oftheGeobactergroup was enriched and isolated from a highly cadmiumcontam<strong>in</strong>atedsite <strong>in</strong> Germany. By design<strong>in</strong>g specific primers theisolatedGeobacterstra<strong>in</strong> was quantified <strong>in</strong> cadmium-contam<strong>in</strong>ated sites andlaboratory experiments. In batch experiments this cadmium-tolerantFe(III)-reducer was shown to mobilize cadmium from Fe(III) (hydr)oxidesthrough reductive dissolution. Subsequently, the phytoavailable cadmiumwas actively be taken up by the metallophyte cadmium hyperaccumulatorplantArabidopsis halleriand accumulated <strong>in</strong> the above ground tissue. Inplant-microbe-soil mesocosms, geochemical and microbial parameterswere determ<strong>in</strong>ed to trace the microbial release of cadmium from cadmiumbear<strong>in</strong>gFe(III) m<strong>in</strong>erals by the natural microbial community <strong>in</strong>comparison to sterile setups. Additionally, the cadmium uptake andaccumulation by the plantA.halleri<strong>in</strong> the presence and absence of thesebacteria was quantified. By harvest<strong>in</strong>g the plant regularly, an efficientremoval of cadmium from contam<strong>in</strong>ated sites may be achieved.BIOspektrum | Tagungsband <strong>2012</strong>
215SMP004Physiological constra<strong>in</strong>ts of microbial electron shuttl<strong>in</strong>g frombacteria via redox-active humic substances to poorly solubleFe(III) m<strong>in</strong>eralsN. Rohrbach* 1 , M. Obst 2 , A. Kappler 11 University of Tueb<strong>in</strong>gen, Geomicrobiology, Tueb<strong>in</strong>gen, Germany2 University of Tueb<strong>in</strong>gen, Env. Analytical Microscopy, Tueb<strong>in</strong>gen,GermanyMicrobial redox processes <strong>in</strong> soils and sediments impact biogeochemicalcycl<strong>in</strong>g of elements and nutrients and are controlled by the availability ofdifferent electron acceptors. Reduction of Fe(III) poses a challenge tomicrobes, s<strong>in</strong>ce Fe(III) is present at neutral pH <strong>in</strong> form of poorly solublem<strong>in</strong>erals. However, Fe(III)-reduc<strong>in</strong>g bacteria are known to overcome thissolubility problem and several mechanisms have been suggested forelectron transfer from the outer membrane to the surface of the ferric(oxyhydr)oxides: (i) direct electron transfer from outer membrane c-typecytochromes requir<strong>in</strong>g direct cell-m<strong>in</strong>eral contact, (ii) <strong>in</strong>direct reduction ofFe(III) via solubilization of the Fe(III) by organic chelators and uptake andreduction of the Fe(III) <strong>in</strong> the cell, or (iii) <strong>in</strong>direct reduction of the Fe(III)m<strong>in</strong>erals via electron shuttles such as dissolved or solid-phase humicsubstances (HS) (Konhauser et al., 2011). HS are ubiquitous <strong>in</strong> theenvironment and can be used by a variety of microbes as electron acceptoras well as electron mediator to transfer electrons from the cell to otherelectron acceptors. However, it is currently unknown whether bothm<strong>in</strong>eral-surface-associated and planktonic cells benefit from HS aselectron mediators and how microbes, m<strong>in</strong>erals and HS are spatiallyarranged as a function of cell density.We studied the extent of microbial reduction of the Fe(III) m<strong>in</strong>eralferrihydrite [Fe(OH) 3] by Shewanella oneidensis stra<strong>in</strong> MR-1 at differentconcentrations of cells <strong>in</strong> the presence and absence of HS. As expected,HS stimulated Fe(III) reduction <strong>in</strong> high-cell-number systems <strong>in</strong> whichexcess planktonic cells transfer electrons via dissolved HS to the Fe(III)m<strong>in</strong>eral surface that is otherwise <strong>in</strong>accessible to them. Unexpectedly, wefound that the presence of HS also stimulated Fe(III) reduction <strong>in</strong> low-cellnumbersystems where all cells present had direct access to the m<strong>in</strong>eralsurface. This suggests that even small spatial gaps between electronreleas<strong>in</strong>gcell-surface prote<strong>in</strong>s and the m<strong>in</strong>eral surface can be bridged viaredox-active HS. Confocal laser scann<strong>in</strong>g microscopy (CLSM) was used toimage cell-m<strong>in</strong>eral-HS-aggregates and to visualize how the microbial cellswere distributed <strong>in</strong> the setups. These results emphasize the relevance of HS<strong>in</strong> biogeochemical redox processes <strong>in</strong> soils and sediments.Konhauser, K.O., Kappler, A., Roden, E.E. (2011) Iron <strong>in</strong> microbial metabolism. Elements, 7, 89-93.SMP005Study<strong>in</strong>g colonization on stone surfaces by a model biofilm <strong>in</strong>a flow-through chamber approachF. Seiffert* 1 , A. Friedmann 2 , A. Heilmann 2 , A. Gorbush<strong>in</strong>a 11 Federal Institute for Materials Research and Test<strong>in</strong>g, 4.0: Model Biofilms<strong>in</strong> Materials Research, Berl<strong>in</strong>, Russian Federation2 Fraunhofer Institute for Mechanics of Materials IWM, Department ofBiological and Macromolecular Materials, Halle, GermanySoil formation on weather<strong>in</strong>g rock surfaces is <strong>in</strong>tr<strong>in</strong>sically connected withprimary microbial colonization at the atmosphere-lithosphere <strong>in</strong>terface.Rock-<strong>in</strong>habit<strong>in</strong>g life is ubiquitous on rock surfaces all around the world,but the laws of its establishment, and more important, quantification of itsgeological <strong>in</strong>put are possible only <strong>in</strong> well-controlled and simplifiedlaboratory models. In a previous study [1] a model rock biofilm consist<strong>in</strong>gof the heterotrophic black yeast Sarc<strong>in</strong>omyces petricola and thephototrophic and nitrogen-fix<strong>in</strong>g cyanobacterium Nostoc punctiforme wasestablished.In the present work the growth of this model biofilm on diverse materialswith different physical and chemical properties was <strong>in</strong>vestigated underwell controlled laboratory conditions. To clarify the role of environmentalfactors, the parameters temperature, light <strong>in</strong>tensity, CO 2 content andrelative humidity were varied <strong>in</strong> growth test series. For an acceleratedstone colonization and to <strong>in</strong>crease the biomass yield different flow-throughchamber systems with semi-cont<strong>in</strong>uous cultures have been applied,simulat<strong>in</strong>g weather<strong>in</strong>g conditions like flood<strong>in</strong>g, desiccation and nutrient<strong>in</strong>put. The biofilm development was studied by (i) light and electronmicroscopy and (ii) qualitatively and quantitatively with respect to cellforms and biomass. Mixed and s<strong>in</strong>gle cultures of the model biofilmprotagonists were compared to elucidate possible growth <strong>in</strong>fluenc<strong>in</strong>geffects by the respective symbiotic partner.Under the mentioned environmental conditions two types of flow-throughchambers have been applied (i) with a neutral growth support<strong>in</strong>gmembrane and (ii) <strong>in</strong>clud<strong>in</strong>g m<strong>in</strong>eral materials to explore possible rocksurface colonization. The first flow-through chamber type is directlyobservable under the light microscope and can be divided <strong>in</strong>to twocompartments via a semi-permeable membrane allow<strong>in</strong>g co-cultivation ofs<strong>in</strong>gle cultures and a regular control of their cell morphology. With thissystem it is possible to determ<strong>in</strong>e if a metabolite exchange between themodel biofilm partners is sufficient for the symbiosis or if there is a needfor a direct cell-cell-contact. Possible biologically <strong>in</strong>duced m<strong>in</strong>eral surfacealterations were followed on various rock substrates exposed <strong>in</strong> the secondflow-through chamber system.[1] A.A. Gorbush<strong>in</strong>a and W.J. Broughton (2009). Annu. Rev. Microbiol.63: 431-450.SMP006Composition of methanogenic archaea of the El’gygytgynCrater Lake NE-SiberiaJ. Görsch*, J. Griess, D. WagnerAWI, Potsdam, Potsdam, GermanyArctic lakes are an important source of methane, which has a 26 timesstronger greenhouse gas effect than CO 2. An <strong>in</strong>crease of abundance andsurface of North Siberian lakes has lead to a rise of methane emission upto 58% from 1974 to 2000 [1]. Nevertheless, the knowledge about methanedynamics <strong>in</strong> arctic lakes and methanogenic archaea <strong>in</strong> deeper sedimentdeposits is still limited.To deepen the understand<strong>in</strong>g of methane dynamics <strong>in</strong> arctic lakes, amolecular biological characterization of methanogenic archaea was carriedout <strong>in</strong> 10.000 to 400.000 years old sediment deposits of the El’gygytgynCrater Lake drilled <strong>in</strong> scope of the ICDP-project ‘Scientific Drill<strong>in</strong>g <strong>in</strong>El’gygytgyn Crater Lake’ [2]. Archaeal DNA was successfully amplifiedthroughout deposits of Middle and Late Pleistocene as well as Holocene.Furthermore, on the base of 16S rRNA, denatur<strong>in</strong>g gradient gelelectrophoresis and clone libraries of selected samples showed a diversityof methanogens affiliated with Methanosarc<strong>in</strong>ales, Methanocellales andMethanomicrobiales. The methanogenic diversity strongly variedthroughout the sediment depths with two areas of high diversity <strong>in</strong> 250.000and 320.000 years old sediments. Additionally, a positive correlationbetween the diversity and the amount of organic carbon was discovered.Application of propidium monoazide helped to dist<strong>in</strong>guish between viablecells and free DNA and showed that a great proportion of amplified DNAcame from <strong>in</strong>tact cells. The oldest liv<strong>in</strong>g archaea was isolated out of390.000 years old sediment deposits. Moreover, a higher methaneproduction rate was detected <strong>in</strong> areas of high diversity. Conclusively,methanogenic archaea are able to survive <strong>in</strong> a metabolic active stage overhundreds of thousand years under lake conditions. As the temperature ofdeeper lake sediments is ris<strong>in</strong>g <strong>in</strong> the context of climate change, it is to beexpected that their activity and consequently the methane emission will<strong>in</strong>crease. Summaris<strong>in</strong>g the results give valuable <strong>in</strong>sights <strong>in</strong> the methanedynamic <strong>in</strong> deeper sediment deposits and confirm the <strong>in</strong>fluence of oldcarbon source to positive feedback loop of climate change.[1] K.M. Walter et al., Nature 443 (2006), p. 71-75.[2] M. Melles et al., Scientific Drill<strong>in</strong>g 11 (2011), p. 29-40.SMP007Population analysis and Fluorescence <strong>in</strong> situ Hybridisation ofaerobic chloroethene degrad<strong>in</strong>g bacteriaT. Teutenberg* 1 , S. Kanukollu 1 , S. Mungenast 2 , A. Tiehm 2 , T. Schwartz 11 KIT Campus North, IFG, Microbiology of Natural and TechnicalInterfaces Department, Eggenste<strong>in</strong>-Leopoldshafen, Germany2 DVGW - Water Technology Center (TZW), Department of EnvironmentalBiotechnology, Karlsruhe, GermanyChloroethenes are a major source of groundwater and soil contam<strong>in</strong>ation.Several mixed cultures and pure bacterial stra<strong>in</strong>s, which grow underanaerobic conditions us<strong>in</strong>g chloroethenes as electron acceptor <strong>in</strong> additionto auxiliary substrates, have been published and exam<strong>in</strong>ed <strong>in</strong> regard toapplication as bioremediation agent. However, aerobic microorganismsthat use the target pollutant like v<strong>in</strong>yl chloride (VC) as growth substratewould be favourable for bioremediation processes.This study has the aim to identify microorganisms <strong>in</strong>volved <strong>in</strong> aerobicdegradation of chloroethenes to use them for bioremediation ofcontam<strong>in</strong>ated sites.Different species were identified via 16S-rRNA PCR-DGGE experimentsus<strong>in</strong>g eubacterial primers and subsequent sequence analysis us<strong>in</strong>g BLASTof the NCBI database. Based on these results species specific primers forPCR and specific gene probes for fluorescence <strong>in</strong>-situ hybridisation (FISH)were designed.Accord<strong>in</strong>g to the sequence analysis results, five different species, whichbelong to the ß-proteobacteria sub-family, were identified <strong>in</strong> metabolicchloroethene degrad<strong>in</strong>g batch cultures <strong>in</strong>oculated with ground watersamples of contam<strong>in</strong>ated sites. Focuss<strong>in</strong>g on these species, conventionalPCR approaches with specific primers were performed.FISH analysis can determ<strong>in</strong>e the presence of the specific bacteria <strong>in</strong>samples from the contam<strong>in</strong>ated site us<strong>in</strong>g the previously designed geneprobes. For that, a preced<strong>in</strong>g treatment regard<strong>in</strong>g the cell wall permeabilitywas established and the hybridization conditions were optimized for eachFISH probe. To verify the quality and specificity of the gene probesdifferent reference bacteria were used as positive and negative control.Quantitative PCR experiments target<strong>in</strong>g possible candidate genes forchloroethene biotransformation will be performed for molecularcharacterization of aerobic decontam<strong>in</strong>ation processes.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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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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32 CONFERENCE PROGRAMMECONFERENCE P
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42 SHORT LECTURESMonday, March 19,
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52ISV01Die verborgene Welt der Bakt
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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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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
- Page 152 and 153:
152OTP065The role of GvpM in gas ve
- Page 154 and 155:
154OTP074Comparison of Faecal Cultu
- Page 156 and 157:
156OTP084The Use of GFP-GvpE fusion
- Page 158 and 159:
158compared to 20 ºC. An increase
- Page 160 and 161:
160characterised this plasmid in de
- Page 162 and 163:
162Streptomyces sp. strain FLA show
- Page 164 and 165: 164The study results indicated that
- Page 166 and 167: 166have shown direct evidences, for
- Page 168 and 169: 168biosurfactant. The putative lipo
- Page 170 and 171: 170the absence of legally mandated
- Page 172 and 173: 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 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 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