20.07.2015 Views

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

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

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

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

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>

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!