220SMP027Contrast<strong>in</strong>g assimilators of 2,4-dichlorophenol derived carbonoccur <strong>in</strong> soil and drilosphereA. Ramm, M. Horn*University of Bayreuth, Ecological Microbiology, Bayreuth, GermanyChlorophenols are frequently detected <strong>in</strong> terrestrial and freshwaterecosystems, are carc<strong>in</strong>ogenic, mutagenic, and recalcitrant. Thus,chlorophenols are of major environmental concern. 2,4-dichlorophenol(2,4-DCP) has been extensively used as wood preservative, is an<strong>in</strong>termediate <strong>in</strong> the degradation of the herbicide 2,4-dichlorophenoxyaceticacid, and was chosen as model compound. Degradation occurs <strong>in</strong> soil,ma<strong>in</strong>ly due to aerobic microbial processes. Degradation ‘hot spots’ <strong>in</strong> soils<strong>in</strong>clude the drilosphere, i.e., earthworm gut content, cast, and burrows.Assimilators of [U 13 C]-2,4-DCP were identified <strong>in</strong> soil columns with andwithout soil-feed<strong>in</strong>g earthworms (Aporrectodea calig<strong>in</strong>osa). [ 12 C]-2,4-DCPtreatments served as controls for SIP. Disappearance of low, <strong>in</strong> siturelevant concentrations of 2,4-DCP (20 g g DW -1 ) was stimulated byearthworms. Barcoded amplicon pyrosequenc<strong>in</strong>g coupled to 16S rRNAstable isotope prob<strong>in</strong>g (SIP) yielded app. 337,000 sequences and identified39 family level taxa of 2,4-DCP-[ 13 C] assimilators relative to [ 12 C]-2,4-DCP controls. Alpha-, Beta-, Gamma - and Deltaproteobacteria,Firmicutes, Acidobacteria, Bacteroidetes, Chloroflexi, Act<strong>in</strong>obacteria andCyanobacteria were 2,4-DCP-[ 13 C] labelled. Sph<strong>in</strong>gomonadaceae,Comamonadaceae, Pseudomonadaceae and Flavobacteriaceae dom<strong>in</strong>atedassimilators of [U 13 C]-2,4-DCP. Many detected 16S rRNA genes wereonly distantly related to publicly available sequences. LabelledClostridiaceae were exclusively detected <strong>in</strong> the anoxic earthworm gut andcast, labelled Flavobacteriaceae occurred only <strong>in</strong> cast, labelledPseudomonadaceae dom<strong>in</strong>ated <strong>in</strong> burrow walls, while labelledSph<strong>in</strong>gomonadaceae were detected <strong>in</strong> earthworm-unaffected soil only.[U 13 C]-2,4-DCP 16S rRNA SIP of enrichment cultures set up with soil anddrilosphere material from soil coulmn experiments <strong>in</strong>dicated thatComamonadaceae and Sph<strong>in</strong>gomonadaceae reacted to cont<strong>in</strong>uous supply overa long time period of 2,4-DCP (50 days, puls<strong>in</strong>g of 5 x 60 g g DW -1 every 10days) <strong>in</strong> liquid media. The collective data <strong>in</strong>dicates that (a) earthwormsstimulate the degradation of 2,4-DCP <strong>in</strong> soil and drilosphere, (b) earthwormsselect for dist<strong>in</strong>ct microbial degraders of 2,4-DCP <strong>in</strong> the drilosphere, and (c)soils <strong>in</strong>fluenced by earthworms harbor highly diverse and hitherto unknown2,4-DCP-utiliz<strong>in</strong>g microorganisms. Thus, vermiremediation may prove to be anenvironmentally susta<strong>in</strong>able way to treat contam<strong>in</strong>ated soils.SMP028Behaviour of act<strong>in</strong>omycete communities <strong>in</strong> soils fertilized withbiotransformed Dry Olive ResidueJ. Siles Martos* 1 , P. Hernández Suárez 1 , V. Menéndez González 2 ,G. Bills 2 , I. García Romera 1 , I. Sampedro Quesada 11 Estación Experimental del Zaidín, Microbiología del Suelo y SistemasSimbióticos, Granada, Spa<strong>in</strong>2 Fundación Med<strong>in</strong>a, Microbiología, Armilla, Spa<strong>in</strong>The Spanish olive oil <strong>in</strong>dustry generates huge amounts of Dry OliveResidue (DOR). This waste is a major environmental problem. Despite itspotential fertilizer value, its <strong>in</strong>corporation <strong>in</strong>to soil results <strong>in</strong> a variety ofnegative effects related with its toxicity caused by several phenolicsubstances (Sampedro et al., 2004). These and others components havebeen l<strong>in</strong>ked with the phytotoxic and antimicrobial this residue’s effects(Paredes et al., 1986; L<strong>in</strong>ares et al., 2003; Sampedro et al., 2008). Treat<strong>in</strong>gthis waste with saprobic fungi could transform DOR <strong>in</strong>to organic fertilizer(Sampedro et al., 2005). Knowledge about the impact of biotransformedDOR on soil microbial ecology is scarce. This work aimed to characterizethe physico-chemical properties of DOR bioremediated with the saprobicfungus Coriolopsis rigida after 30 days of <strong>in</strong>cubation at 28ºC and tomeasure the effect of the application of this residue for 0, 30 and 60 dayson the act<strong>in</strong>omycete communities of sorghum rhizospheric soil. The totalpolyphenols <strong>in</strong> C. rigida-treated DOR decreased by 75% and the C/N wasreduced. The concentration of some microelements like alum<strong>in</strong>ium, iron,chrome and z<strong>in</strong>c was significantly differed. To further understand theeffects of residues on the act<strong>in</strong>omycete communities, 200 bacterial stra<strong>in</strong>swere isolated <strong>in</strong> gellan gum-solidified VL70 modified medium (Sait et al.,2002; Joseph et al., 2003; David et al., 2005) from a control soil, a soil<strong>in</strong>cubated with untreated DOR and soil <strong>in</strong>cubated with C. rigida-treatedDOR over time. The population of filamentous act<strong>in</strong>omycetes from eachtreatment were morphologically dist<strong>in</strong>guished. Soil populations ofact<strong>in</strong>omycetes were 90% lower <strong>in</strong> soil amended with untreated DORrespect to the control soil across all times. However, this decrease was lessevident <strong>in</strong> the soil treated with C. rigida-treated DOR. The 16S rRNA gene ofall the act<strong>in</strong>omycetes was analyzed with act<strong>in</strong>omycete-specific primer (Xiao etal., 2011) by PCR-DGGE. The data showed that C. rigida-treated DOR appliedto soil reduced the negative impact on act<strong>in</strong>omycete microbial communities.SMP029Characterization of the microbial community <strong>in</strong> a deep sal<strong>in</strong>eaquifer used for geothermal heat storage - Thermal effects onmicrobial composition and microbial <strong>in</strong>duced corrosive andprecipitative processes affect<strong>in</strong>g plant operationS. Lerm*, M. Alawi, R. Miethl<strong>in</strong>g-Graff, A. Seibt, M. Wolfgramm,H. WürdemannHelmholtz-Zentrum PotsdamDeutsches GeoForschungsZentrum GFZ,Mikrobielles Geoeng<strong>in</strong>eer<strong>in</strong>g, Potsdam, GermanyThe microbial diversity of a sal<strong>in</strong>e aquifer (m<strong>in</strong>eralisation 131 g/L) usedfor geothermal heat storage <strong>in</strong> the North German Bas<strong>in</strong> was characterizedover a period of two years. Results of SSCP- and DGGE- f<strong>in</strong>gerpr<strong>in</strong>t<strong>in</strong>gand scann<strong>in</strong>g electron microscopic (SEM) analyses <strong>in</strong>dicated dist<strong>in</strong>ctdifferences <strong>in</strong> the microbial community composition <strong>in</strong> the cold and thewarm well, with temperatures rang<strong>in</strong>g between 45-54°C and 65-80°C,respectively. High temperature <strong>in</strong> the warm well probably enhancedorganic matter availability and set off a cascade of organic mattertransformation favour<strong>in</strong>g diverse heterotrophic bacteria <strong>in</strong> the warm welland fermentative bacteria after temperature reduction due to heatextraction <strong>in</strong> the topside facility. In contrast, a high diversity of sulphatereduc<strong>in</strong>g bacteria (SRB), affiliated to members of the generaDesulfotomaculum, Desulfohalobium and Candidatus Desulforudisaudaxviator, was detected <strong>in</strong> the cold well. They were accounted for thecorrosion damage to the submersible pump <strong>in</strong> the cold well and ironsulphide precipitations <strong>in</strong> the near well bore area and topside facility filtersof the cold well. This study reflects the thermal effects on microbialcomposition <strong>in</strong> a geothermally used aquifer, whereas the microbial <strong>in</strong>ducedprocesses adversely affect plant operation; and this applies particularly tothe cold well.SMP030Influence of manure and Sulfadiaz<strong>in</strong>e on microbial diversitypattern and the distribution of resistance genes aga<strong>in</strong>stantimicrobials <strong>in</strong> an artificial rhizosphereM. ZieglerHelmholtz Zentrum München, Environmental Genetics, Neuherberg,GermanySulfadiaz<strong>in</strong>e (SDZ) is a veter<strong>in</strong>ary antibiotic which is widely used <strong>in</strong>animal livestock. Farm<strong>in</strong>g animals excrete residues of SDZ and resistantmicrobiota which are <strong>in</strong>troduced <strong>in</strong>to the environment by manureapplication to arable land. This process is argued to lead to the spread<strong>in</strong>gof antibiotic resistance genes <strong>in</strong> the environment and f<strong>in</strong>ally causes<strong>in</strong>creas<strong>in</strong>g untreatable bacterial <strong>in</strong>fections <strong>in</strong> humans. The plant rootsurface - also called rhizoplane - is a hotspot of microorganisms due toplant root exudation. Bacterial cells attached to the plant root formcommunity-like structures enclosed by an extrapolymeric matrix.Therefore, microorganisms are protected from abiotic and biotic stressesand due to the high proximity of the cells the chance for horizontal genetransfer <strong>in</strong>creases. This leads to our hypothesis, that the rhizoplane couldbe an ideal environment for spread<strong>in</strong>g antibiotic resistance genes.To address this question, we used an artificial root model (ARM) whichconsisted of a glass slide covered with an artificial root exudate mix<strong>in</strong>cubated <strong>in</strong> soil. For pre-<strong>in</strong>cubation, both piggery manure and SDZ wereadded to the soil, and after one and two weeks <strong>in</strong>cubation of the ARMrespectively, we harvested the attached microorganisms. To detect the<strong>in</strong>fluence of manure and SDZ application to the bacterial communities onthe ARM, we performed T-RFLP based on 16S rRNA genes andquantified the SDZ-resistance genes sul1 and sul2 by quantitative PCR.The results show an <strong>in</strong>crease of SDZ resistance <strong>in</strong> bacterial communitiesattached to the ARM, but no shift <strong>in</strong> community structure whenpre<strong>in</strong>cubated with manure and SDZ.SMP031Metabolic networks <strong>in</strong> soil microbial communities <strong>in</strong>vestigatedby prote<strong>in</strong>-stable isotope prob<strong>in</strong>g (prote<strong>in</strong>-SIP)R. Kermer* 1 , T. Wubet 2 , F. Buscot 2,3 , M. von Bergen 1,4 , J. Seifert 11 Helmholtz Centre for Environmental Research, Proteomics, Leipzig, Germany2 Helmholtz Centre for Environmental Research, Soil Ecology, Halle/Saale,Germany3 University of Leipzig, Institute of Biology, Chair of Soil Ecology, Leipzig,Germany4 Helmholtz Centre for Environmental Research, Metabolomics, Leipzig,GermanyThe degradation of plant-derived materials like leaf litter, consist<strong>in</strong>g ofcellulose, lign<strong>in</strong>, hemicellulose, pect<strong>in</strong> and prote<strong>in</strong>s, is an <strong>in</strong>terest<strong>in</strong>gsubject to study complex m<strong>in</strong>eralization cycles <strong>in</strong> nature [1]. Consortia ofbacteria and especially fungi greatly contribute to this key ecosystemprocess by express<strong>in</strong>g a suite of various extracellular enzymes. In fact,these microorganisms decompose almost 90% of the plant biomassBIOspektrum | Tagungsband <strong>2012</strong>
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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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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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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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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166have shown direct evidences, for
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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 214 and 215: 214determined as a function of the
- Page 216 and 217: 216Funding by BMWi (AiF project no.
- Page 218 and 219: 218broad distribution in nature, oc
- 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