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

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

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

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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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