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

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

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221produced <strong>in</strong> terrestrial ecosystems [2]. The goal of the present project is toprovide a closer <strong>in</strong>sight towards the structure and function of thesecommunities by identify<strong>in</strong>g metabolically active species, <strong>in</strong>teractions andmetabolic networks. For the detection of metabolic key players prote<strong>in</strong>-SIPis applied, a method based on the metabolic <strong>in</strong>corporation of isotopicallylabeled substrates, e.g. with 13 C, 15 N or 36 S, <strong>in</strong>to the proteome ofmicroorganisms [3].Prote<strong>in</strong>-SIP experiments were performed <strong>in</strong> which soil from a tobaccofield <strong>in</strong> Germany was <strong>in</strong>cubated with leaf litter from either 15 N-labeledtobacco or 13 C-labeled corn plants as substrate over 14 days. The microbialgrowth with<strong>in</strong> the approaches was monitored by measur<strong>in</strong>g the biologicaloxygen demand. Immediate oxygen consumption was measured <strong>in</strong> the leaflitter-soil <strong>in</strong>cubations and sampl<strong>in</strong>g took place three times <strong>in</strong> the first threedays and three times with<strong>in</strong> the rema<strong>in</strong><strong>in</strong>g 11 days. The samples wereconducted to two prote<strong>in</strong> extraction steps: one for the extracellular andanother one for the <strong>in</strong>tracellular proteome. Prote<strong>in</strong>s were separated by 1-dimensional SDS gel electrophoresis and peptides were analyzed by UPLCOrbitrap MS/MS measurements. For prote<strong>in</strong> identification themetagenome sequence of the soil from the tobacco field was conducted.454 pyrosequenc<strong>in</strong>g resulted <strong>in</strong> about 390 Mb distributed over about871,000 reads with an average length of 450 bp. MG-RAST analysisshowed that a large proportion of the functional genes belong to bacterialprote<strong>in</strong>s (~97%) and to eukaryotic prote<strong>in</strong>s (~2%). In addition to theassessment of the phylogeny of organism <strong>in</strong> the soil the metagenome willfacilitate the identification rate of the metaproteome approach andtherefore will <strong>in</strong>crease the number of prote<strong>in</strong>s for which the 13 C and 15 N<strong>in</strong>corporation patterns can be determ<strong>in</strong>ed.1. Yadav V, Malanson G (2007) Progress <strong>in</strong> soil organic matter research: litter decomposition, modell<strong>in</strong>g,monitor<strong>in</strong>g and sequestration. Progress <strong>in</strong> Physical Geography 31: 131-1542. Zhang Q, Zak JC (1998) Potential Physiological Activities of Fungi and Bacteria <strong>in</strong> Relation to PlantLitter Decomposition along a Gap Size Gradient <strong>in</strong> a Natural Subtropical Forest. Microb Ecol 35: 172-1793. Jehmlich N, Schmidt F, Taubert M, Seifert J, Bastida F, von Bergen M, Richnow HH, Vogt C (2010)Prote<strong>in</strong>-based stable isotope prob<strong>in</strong>g. Nat Protoc 5: 1957-1966SMP032Horizontal gene transfer <strong>in</strong> wastewater irrigated soils <strong>in</strong> theMézquital Valley, MexicoM. Broszat* 1,2 , T. Sak<strong>in</strong>c 1 , Y. López Vidal 3 , J. Huebner 1 , E. Grohmann 11 University Medical Centre Freiburg, Department of Infectious Diseases,Freiburg, Germany2 University Freiburg, Institute of Microbiology, Freiburg, Germany3 Universidad Nacional Autónoma de México, Departamento de Microbiologíay Parasitología, Mexico City, MexicoThe Mézquital Valley (60 km north of Mexico City) is the world´s largestwastewater (WW) irrigation area. There, untreated WW from Mexico Cityis reused for crop irrigation. This practise might pose risks for fieldworkers and consumers of agricultural products, because of the presence ofpharmaceuticals, pathogens and antibiotic resistance genes <strong>in</strong> the WW. Weperformed soil column experiments with two different types of soil (soilirrigated with WW for 100 years and ra<strong>in</strong>-fed soil) to <strong>in</strong>vestigate thespread of resistance genes by horizontal gene transfer (HGT) <strong>in</strong> WWirrigated soils. To visualize plasmid transfer an Enterococcus faecalisdonor harbour<strong>in</strong>g a mobilizable broad host range plasmid labeled with theGreen Fluorescent Prote<strong>in</strong> (GFP) [1] and a second non-mobilizableplasmid labelled with the Red Fluorescent Prote<strong>in</strong> (RFP) [2] were added tora<strong>in</strong>-fed and 100 years-irrigated soil, each <strong>in</strong> soil columns of 20 cm heightand 15 cm diameter. The mobilizable plasmid conta<strong>in</strong>s a replication orig<strong>in</strong>for Gram-positive and Gram-negative bacteria, the gfp gene under controlof the <strong>in</strong>ducible nis<strong>in</strong> promoter and the pIP501 orig<strong>in</strong> of transfer. Soilcolumns were irrigated once a week, <strong>in</strong> total three times. At each irrigation10 9 donors were applied to the columns with one pore volume of artificialra<strong>in</strong>water (for ra<strong>in</strong>-fed soil) or WW (for WW-irrigated soil). Dur<strong>in</strong>girrigation leachate water was collected. Furthermore pore water wassampled at 4 heights with suction cups. Soil samples from the top weretaken daily. After 4 weeks soil samples were taken from different heights(every 2.5 cm). Bacteria <strong>in</strong> soil and water which have acquired themobilizable resistance plasmid via plasmid transfer are detectable throughtheir green fluorescence while their donors are identified by their greenand red fluorescence. Transfer rates for both types of soil and <strong>in</strong> water willbe presented. The soil column experiment will help assess the risk posedby HGT of resistance determ<strong>in</strong>ants <strong>in</strong> WW-irrigated soil.[1] Arends, K., Schiwon, K., Sak<strong>in</strong>c, T., Huebner, J., and Grohmann, E. A GFP-labelled monitor<strong>in</strong>g tool toquantify conjugative plasmid transfer between G+ and G- bacteria. Appl. Environ. Microbiol. (accepted)[2] Paprotka, K., Giese, B., Fraunholz, M. J. 2010. Codon-improved fluorescent prote<strong>in</strong>s <strong>in</strong> <strong>in</strong>vestigation ofStaphylococcus aureus host pathogen <strong>in</strong>teractions. J. Microbiol. Methods. 83: 82-86.SMP033Understand<strong>in</strong>g factors which shape the community ofnitrifiers: structural and functional analysesA. Meyer* 1 , M. Schloter 2 , A. Focks 31 Technische Universität München, soil ecology, Neuherberg, Germany2 HelmholtzZentrum München, Enviromental Genomics, Neuherberg, Germany3 Wagen<strong>in</strong>gen University, Aquatic Ecology and Water Quality Management,Wagen<strong>in</strong>gen, NetherlandsUnderstand<strong>in</strong>g factors which drive the ecology of microbial communities<strong>in</strong>volved <strong>in</strong> nitrogen turnover is of central importance for susta<strong>in</strong>able landuse. As a model system grassland sites treated with different land use<strong>in</strong>tensities were studied: (I) <strong>in</strong>tensely used meadows, (II) <strong>in</strong>tensely usedmown pastures and (III) extensively used pastures. Samples were taken <strong>in</strong>spr<strong>in</strong>g and <strong>in</strong> the summer to <strong>in</strong>vestigate the seasonal as well as the land use<strong>in</strong>tensity effect. In the last years it was found that <strong>in</strong> many soils ammoniaoxidiz<strong>in</strong>garchaea (AOA) are more abundant than ammonia-oxidiz<strong>in</strong>gbacteria. However, till now the contribution of AOA to total ammoniaturnover rates are not clear. In order to address this question we estimateda theoretical potential nitrification rate (PNR) based on the actualmeasured abundances of archaeal and bacterial ammonia monooxygenasegenes (amoAAOA andamoAAOB) and hypothetical maximum oxidationrate constants. This approach offers the possibility to estimate not only thetheoretical PNR values but also the respective contributions of AOA andAOB. A comparison between the theoretical and the measured PNR valuesshows that they fit quiet well together. In order to assess the correlationbetween the observed temporal changes <strong>in</strong> nitrification activities, but alsothe found variability between the s<strong>in</strong>gle grassland plots, a diversity analysisbased onamoAAOA genes was performed. The results showed that the s<strong>in</strong>gletreatments are statistically well separated but surpris<strong>in</strong>gly no clear differencesbetween the two time po<strong>in</strong>ts could be found. Summariz<strong>in</strong>g, our results strike outthat AOAs deliver a high ammonium turnover potential to the soils. Changes <strong>in</strong>nitrification potentials are seem<strong>in</strong>gly not due to AOA diversity, but driven bythe activity state of the AOAs, which probably has changed between spr<strong>in</strong>g andsummer. Based on the above results, we assume that diversity of theamoAAOAgene is shaped by long-term changes <strong>in</strong> environmental parameters, whereas theactivity is probably driven by seasonal changes of environmental conditions.SMP034Metagenomic and metatranscriptomic analysis of German soilsamplesH. Nacke* 1 , C. Fischer 1 , A. Thürmer 2 , R. Daniel 1,21 Institute of Microbiology and Genetics, Department of Genomic andApplied Microbiology, Gött<strong>in</strong>gen, Germany2 Institute of Microbiology and Genetics, Gött<strong>in</strong>gen Genomics Laboratory,Gött<strong>in</strong>gen, GermanyPhylogenetic, transcriptomic, and functional analyses of microbialcommunities present <strong>in</strong> soil samples from the German BiodiversityExploratories Schorfheide-Chor<strong>in</strong>, Ha<strong>in</strong>ich-Dün, and Schwäbische Albwere performed (see www.biodiversity-exploratories.de). Theexperimental procedure <strong>in</strong>cluded the isolation of whole genomic DNAfrom the A horizon and B horizon of selected forest and grassland sites.The prokaryotic diversity present <strong>in</strong> the different samples was assessed bypyrosequenc<strong>in</strong>g of amplicons us<strong>in</strong>g hypervariable regions of 16S rRNAgenes as target. Differences <strong>in</strong> prokaryotic community compositionsbetween A- and B-horizons as well as between forest and grasslandsamples were detected. Additionally, we extracted total RNA from soilsamples, enriched mRNA, and used it for the synthesis of cDNA.Pyrosequenc<strong>in</strong>g of the generated cDNA and subsequent sequence analysisallowed to assess soil microbial gene expression profiles.Metagenomic small-<strong>in</strong>sert and large-<strong>in</strong>sert libraries were constructed us<strong>in</strong>ggenomic DNA extracted from the different soil samples. Comparativescreen<strong>in</strong>g of the libraries for key microbial functions, such as cellulolytic,hemicellulolytic, and lipolytic activities was carried out. Several clonesexpress<strong>in</strong>g cellulase-, hemicellulase-, and lipase/esterase- activity wereobta<strong>in</strong>ed dur<strong>in</strong>g function-driven screen<strong>in</strong>g of the libraries. Genes encod<strong>in</strong>g(hemi)cellulolytic or lipolytic activity were recovered from thecorrespond<strong>in</strong>g clones and sequenced. So far, analyzed (hemi)cellulolyticenzymes were assigned to glycosidhydrolase families 9 and 11. Thirty-fiveof the 37 analyzed lipases/esterases grouped <strong>in</strong>to superfamilies I, IV, V,VI, and VIII of lipolytic enzymes. The rema<strong>in</strong><strong>in</strong>g two represent putativelynovel families. Biochemical characterization of (hemi)cellulolytic andlipolytic enzymes was carried out.SMP035Characterization of Paenibaciilus polymyxa RCP6 isolatedfrom root nodules of Blue peaA. AeronKurukshetra University, Department of Microbiology, Kurukshetra, IndiaQuestion: Clitoria purpurea L. (blue pea) is a slender climber legumeknown for its beautiful bluish-crimson coloured flowers. This is foundBIOspektrum | Tagungsband <strong>2012</strong>

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