218broad distribution <strong>in</strong> nature, occurr<strong>in</strong>g commonly <strong>in</strong> soil and <strong>in</strong> associationwith plants, fungi and animals, where mutualistic as well as parasitic<strong>in</strong>teractions can be found. The importance of Burkholderia species asopportunistic pathogens (e.g. <strong>in</strong> cystic fibrosis patients) is <strong>in</strong>creas<strong>in</strong>glyrecognized and the molecular mechanisms underly<strong>in</strong>g virulence have beenextensively studied. However, little is known so far about the abundance,the diversity and the biogeography of the genus Burkholderia <strong>in</strong> naturalenvironments such as soils. Reports from the literature <strong>in</strong>dicate thatBurkholderia species are often isolated from acidic environments, whichsuggests that pH could be an important factor <strong>in</strong> shap<strong>in</strong>g the biogeographyof Burkholderia. To assess this question, 46 soil DNA samples collectedacross North and South America were used (Fierer and Jackson, 2006). Aspecific real time PCR protocol target<strong>in</strong>g Burkholderia 16S rRNA genewas developed to analyse the relative abundance of Burkholderia sp. <strong>in</strong>these soil samples. Results suggest that pH has a significant effect onBurkholderia relative abundance <strong>in</strong> soils: the highest relative abundancewas observed <strong>in</strong> soils rang<strong>in</strong>g between pH 5 and pH 6 where up to 6.7 %of total bacterial 16S rRNA genes were represented by Burkholderiaspecies. Lower pH soils also showed high relative abundance ofBurkholderia (up to 2.8%). However, Burkholderia 16S rRNA copynumbers were not detected <strong>in</strong> alkal<strong>in</strong>e soils. We are currently <strong>in</strong>vestigat<strong>in</strong>gthe diversity of Burkholderia <strong>in</strong> a subset of 15 selected sites vary<strong>in</strong>g <strong>in</strong> pH,C:N ratio, location of sampl<strong>in</strong>g and relative abundance of Burkholderia.This will allow us to better understand which populations are particularlyaffected by pH and which other factors are shap<strong>in</strong>g the abundance, thediversity and the biogeography of soil Burkholderia species.1. N. Fierer and R.B. Jackson, The diversity and biogeography of soil bacterial communities,PNAS,103(2006), p. 626-631.SMP019Characterization of microbial dehalogenation us<strong>in</strong>g compoundspecific stable isotope analysisJ. Renpenn<strong>in</strong>g*, J. Kaesler, I. NijenhuisHelmholtz Centre for Environmental Research - UFZ, Department ofIsotope Biogeochemistry, Leipzig, GermanyChlor<strong>in</strong>ated ethenes are the most common soil and groundwatercontam<strong>in</strong>ants worldwide. Technical application of tetra- andtrichloroethenes (PCE, TCE) <strong>in</strong> the dry clean<strong>in</strong>g <strong>in</strong>dustry and metaldegreas<strong>in</strong>g resulted <strong>in</strong> big scale production and release <strong>in</strong> the environment.Chloroethenes are an issue of serious risk for human health and suspectedto be carc<strong>in</strong>ogenic. Dur<strong>in</strong>g the last decade several bacterial stra<strong>in</strong>s wereisolated from contam<strong>in</strong>ated soil and groundwater capable of reductivedehalogenation of chlor<strong>in</strong>ated ethenes. However, the actual reactionmechanism and the <strong>in</strong>volved genes responsible for specific dehalogenationare still a po<strong>in</strong>t of <strong>in</strong>terest.We aim to <strong>in</strong>vestigate and characterize the reductive dehalogenationreaction <strong>in</strong> several stra<strong>in</strong>s, us<strong>in</strong>g stable isotope techniques. Compoundspecific stable isotope analysis can be used to analyze the reactionmechanism and degradation pathway. Previously, we observed that thecarbon stable isotope fraction was highly variable when compar<strong>in</strong>gdifferent stra<strong>in</strong>s capable of the reductive dehalogenation of the chlor<strong>in</strong>atedethenes [1]. These differences may either be due to differences <strong>in</strong> enzymemechanism or to e.g. rate limit<strong>in</strong>g effects and substrate uptake processes asobserved for Sulfurospirillum multivorans and Desulfitobacteriumsp. stra<strong>in</strong>PCE-S [2]. Our prelim<strong>in</strong>ary experiment have shown that rate limitationdoes not appear to play a role <strong>in</strong> Dehalobacter restrictus and that highlysimilar enzymes, although present <strong>in</strong> different organisms i.e. D. restrictusand Desulfitobacterium sp. PCE-S, produced similar isotope effects,contrary to previous publications. Further studies should allow analysis ofthe causes for different isotope fractionation of the chlor<strong>in</strong>ated ethenes byother bacteria such as Geobacter or Desulfuromonas.Acknowledgement: This work is supported by the DFG (research unit FOR1530)1. Cichocka, D., et al.,Variability <strong>in</strong> microbial carbon isotope fractionation of tetra-and trichloroethene uponreductive dechlor<strong>in</strong>ation.Chemosphere, 2008.71(4): p. 639-648.2. Nijenhuis, I., et al.,Stable isotope fractionation of tetrachloroethene dur<strong>in</strong>g reductive dechlor<strong>in</strong>ation bySulfurospirillum multivorans and Desulfitobacterium sp. stra<strong>in</strong> PCE-S and abiotic reactions withcyanocobalam<strong>in</strong>.Applied and Environmental Microbiology, 2005.71(7): p. 3413.SMP020Abundance, distribution, and activity of Fe(II)-oxidiz<strong>in</strong>g andFe(III)-reduc<strong>in</strong>g microorganisms <strong>in</strong> hypersal<strong>in</strong>e sediments ofLake Kas<strong>in</strong>, Southern RussiaM. Emmerich*, A. Bhansali, T. Lösekann-Behrens, C. Schröder, A. Kappler,S. BehrensCenter for Applied Geosciences, Geosciences, Tüb<strong>in</strong>gen, GermanyThe extreme osmotic conditions prevail<strong>in</strong>g <strong>in</strong> hypersal<strong>in</strong>e environmentsresult <strong>in</strong> decreas<strong>in</strong>g metabolic diversity with <strong>in</strong>creas<strong>in</strong>g sal<strong>in</strong>ity. Variousmicrobial metabolisms have been shown to occur even at high sal<strong>in</strong>ity,<strong>in</strong>clud<strong>in</strong>g photosynthesis, sulfate and nitrate reduction. However,<strong>in</strong>formation about anaerobic microbial iron metabolism <strong>in</strong> hypersal<strong>in</strong>eenvironments is scarce. We studied the phylogenetic diversity, distribution,and metabolic activity of iron(II)-oxidiz<strong>in</strong>g and iron(III)-reduc<strong>in</strong>g bacteriaand archaea <strong>in</strong> iron-rich salt lake sediments (Lake Kas<strong>in</strong>, Southern Russia;sal<strong>in</strong>ity 348.6 g L -1 ) us<strong>in</strong>g a comb<strong>in</strong>ation of culture-dependent and-<strong>in</strong>dependent techniques. 16S rRNA gene clone libraries for Bacteria andArchaea revealed a microbial community composition typical forhypersal<strong>in</strong>e sediments. Most probable number experiments and enrichmentcultures confirmed the presence of microbial iron(II) oxidation andiron(III) reduction <strong>in</strong> the salt lake sediments. Microbial iron(III) reductionwas detected <strong>in</strong> the presence of 5 M NaCl, thereby extend<strong>in</strong>g the naturalhabitat boundaries for this important microbial respiratory process.Quantitative real-time PCR showed that 16S rRNA gene copy numbers oftotal Bacteria, total Archaea, and species dom<strong>in</strong>at<strong>in</strong>g the iron(III)-reduc<strong>in</strong>genrichment cultures (relatives of Halobaculum gomorrense, Desulfosporos<strong>in</strong>uslacus, and members of the Bacilli) were highest <strong>in</strong> an iron oxide-rich sedimentlayer. Comb<strong>in</strong>ed with the presented geochemical and m<strong>in</strong>eralogical data, ourf<strong>in</strong>d<strong>in</strong>gs suggest the presence of an active microbial iron cycle at saltconcentrations close to the solubility limit of NaCl.SMP021Microbial, geochemical, and m<strong>in</strong>eralogical contributions toarsenic removal from dr<strong>in</strong>k<strong>in</strong>g water <strong>in</strong> house hold sand filters<strong>in</strong> VietnamA. Bhansali*, K. Nitzsche*, A. Kappler, S. BehrensCenter for Applied Geosciences, Geosciences, Tüb<strong>in</strong>gen, GermanyWorldwide more than 100 million people <strong>in</strong>gest detrimental concentrationsof arsenic by consum<strong>in</strong>g groundwater contam<strong>in</strong>ated from natural geogenicsources. Many Asian countries, <strong>in</strong> particular Vietnam, Bangladesh, India,and Cambodia are known to be affected by high groundwater arsenicconcentrations as a result of chemically reduc<strong>in</strong>g aquifer conditions.Household sand filters are simple to operate and remove on average 80%of arsenic from groundwater conta<strong>in</strong><strong>in</strong>g 1 mg/L of ferrous iron or aniron/arsenic ratio of about 50. The <strong>in</strong>stallation and operation costs ofhousehold sand filters are low and the construction materials are locallyavailable. The filters can treat a reasonable amount of groundwater with<strong>in</strong>a short time and they can easily be <strong>in</strong>stalled by the affected communities.Oxidation of dissolved iron present <strong>in</strong> the groundwater leads to theformation of sparsely soluble iron(hydr)oxide particles <strong>in</strong> the sand filters,which b<strong>in</strong>d negatively charged arsenic species and reduce arsenicconcentrations <strong>in</strong> the water. Although household sand filters have beenproven to be an effective technical solution for mitigat<strong>in</strong>g arsenicexposure, not much is known about microbial iron, manganese, arsenicredox-processes occurr<strong>in</strong>g <strong>in</strong> the filters and their effect on filter efficiency.Therefore, one of the goals of this study was to isolate, identify, andquantify Fe, Mn, and As-oxidiz<strong>in</strong>g and -reduc<strong>in</strong>g microorganisms from aarsenic removal sand filter and to study their specific Fe, Mn, and Asredox activities. Water samples and filter solids were collected from alocal sand filter close to the city of Hanoi, Vietnam. The samples weregeochemically and m<strong>in</strong>eralogically characterized. Total iron, arsenic,manganese, and phosphate concentrations, pH, TOC, TIC measurements,as well as total cell counts were performed on samples from various depth ofthe sand filter. Most probable number counts confirmed the presence andactivity of various iron, manganese, arsenic redox-processes and theirdistribution with<strong>in</strong> the water filter. The goals of this research project are tobetter understand the microbial redox transformation processes that drivearsenic/manganese/iron m<strong>in</strong>eral <strong>in</strong>teractions <strong>in</strong> household sand filters and togive recommendations for improved filter use and filter material disposal.SMP022Impact of Biochar Amendment on Microbial Nitrogen-Cycl<strong>in</strong>g<strong>in</strong> Agricultural SoilS. Schüttler*, N. Hagemann*, J. Harter, H.-M. Krause, A. Kappler, S. BehrensCenter for Applied Geosciences, Geosciences, Tüb<strong>in</strong>gen, GermanyN 2O is a major greenhouse gas (GHG) contribut<strong>in</strong>g 8% to global GHGemissions with agricultural sources represent<strong>in</strong>g 84% of anthropogenicN 2O emissions. N 2O is a product of microbial denitrification and itsformation is correlated to fertilizer use. Soil biochar amendment has beenobserved to decrease soil N 2O emissions. Biochar is a stable, carbon richproduct that is manufactured by thermal decomposition of organic materialunder limited oxygen supply. Although the effect of biochar on nitrousoxide emissions from soil has been studied previously the mechanismsbeh<strong>in</strong>d the reduced N 2O emission from biochar amended soil are not yetunderstood. We <strong>in</strong>vestigated whether the decrease <strong>in</strong> N 2O emissionscaused by biochar amendment is due to changes <strong>in</strong> the functionalcomposition of the nitrogen-cycl<strong>in</strong>g microbial community. For this reasonagricultural soil was <strong>in</strong>cubated <strong>in</strong> microcosms with different amounts ofbiochar under oxic (60% WFPS - water filled pore space) and anoxic(100% WFPS) conditions over a period of 3 month. Copy numbers ofdifferent functional genes <strong>in</strong>volved <strong>in</strong> the microbial nitrogen cycle werequantified by real-time PCR. Gene abundance and expression werecorrelated to N 2O, CO 2, CH 4 emissions as well as soil NH + -4 , NO 2 and-NO 3 concentrations. Differences <strong>in</strong> microbial respiration rates <strong>in</strong> thepresence of various nitrogen compounds <strong>in</strong> the treatments with andwithout biochar were quantified <strong>in</strong> BIOLOG assays. Our experimentsBIOspektrum | Tagungsband <strong>2012</strong>
219showed reduced N 2O emissions <strong>in</strong> the biochar treatments up to 84%. Ingeneral N 2O emissions were 30 times higher under anoxic conditionscompared to the emissions from the oxic microcosms. Decreased N 2Oemissions were correlated to an <strong>in</strong>crease <strong>in</strong> the relative abundance of nitrousoxide reductase (nosZ) gene copy numbers dur<strong>in</strong>g the first two weeks afterbiochar addition. Our results further showed that reduced N 2O emissions frombiochar amended soils were directly l<strong>in</strong>ked to changes <strong>in</strong> the functionalcomposition, nitrogen compound utilization, and activity of the nitrogentransform<strong>in</strong>gmicrobial community. Overall, soil biochar amendment promotedcomplete denitrification via stimulation of growth and activity of nosZconta<strong>in</strong><strong>in</strong>g,nitrous oxide reduc<strong>in</strong>g denitrifiers. Our f<strong>in</strong>d<strong>in</strong>gs will facilitate thedevelopment of new mitigation strategies for anthropogenic GHGs.SMP023Microbial and metabolic analysis and optimization of CH 4production from wheat stillage at elevated temperaturesI. Röske* 1 , W. Sabra 2 , A. Sorger 1 , K. Sahm 1 , R. Daniel 3 , A.-P. Zeng 2 ,G. Antranikian 11 Hamburg University of Technology, Institute of Technical Microbiology,Hamburg, Germany2 Hamburg University of Technology, Institute for Bioprocess and BiosystemsEngeneer<strong>in</strong>g, Hamburg, Germany3 Georg-August-University, Department of Genomic and Applied Microbiology,Gött<strong>in</strong>gen, GermanyDevelopment of an efficient bioethanol production plant based on biomassrequires the <strong>in</strong>tegration of various biological and non-biological processes.After the bioconversion of wheat to ethanol and the distillation processhigh amounts of lignocellulose and dead yeast cells still rema<strong>in</strong> untreated(stillage). From a high-temperature biogas plant, us<strong>in</strong>g corn and chickenmanure as biogas substrates, a microbial community was enriched able toconvert wheat stillage to methane at 55°C.In order to <strong>in</strong>vestigate the microbial community <strong>in</strong> the model biogasreactor pyrosequence analysis of 16S rRNA gene-tags was conductedresult<strong>in</strong>g <strong>in</strong> 23,000 gene sequences. The studies <strong>in</strong>dicate the predom<strong>in</strong>anceof Archaea of the genera Methanosaeta and Methanothermobacter andBacteria of the families Thermotogaceae, Anaerol<strong>in</strong>eaceae,Synergistaceae and Thermodesulfobiaceae.The archaeon Methanothermobacter thermautotrophicus and the bacteriaLutispora thermophila, Thermoanaerobacter thermosaccharolyticum,Clostridium succ<strong>in</strong>ogenes and Thermohydrogenium kirishiense wereisolated by anaerobic serial dilution techniquesTo improve biogas production we <strong>in</strong>vestigated different stra<strong>in</strong>s for theirbioaugmentation potential. We could demonstrate that the addition of apure culture of Caldicellulosiruptor saccharolyticus to the exist<strong>in</strong>g biogascommunity resulted <strong>in</strong> a considerable biogas <strong>in</strong>tensification rate with aconstant CO 2/CH 4 ratio.To <strong>in</strong>vestigate dynamics and stability of the microbial community dur<strong>in</strong>gprocess modifications such as <strong>in</strong>crease <strong>in</strong> load<strong>in</strong>g rate and addition ofaccumulat<strong>in</strong>g <strong>in</strong>termediates, denatur<strong>in</strong>g gradient gel electrophoresis andfluorescence <strong>in</strong>-situ hybridization was employed. The results revealed thepresence of a robust consortium of methanogenic Archaea.The set of primers developed <strong>in</strong> this study provides a tool for monitor<strong>in</strong>gmethanogenic communities from a wide range of biogas processes.SMP024Methanogenic communities and their response to Holoceneand Late Pleistocene climate changes <strong>in</strong> permafrostenvironmentsD. Wagner* 1 , J. Griess 1 , K. Mangelsdorf 21 Alfred Wegener Institute for Polar and Mar<strong>in</strong>e Research, Research UnitPotsdam, Potsdam, Germany2 Helmholtz Zentrum Potsdam Deutsches Geoforschungszentrum, Section 4.3,Potsdam, GermanyThe currently observed climate change due to global warm<strong>in</strong>g is expectedto have a strong impact, notably on Arctic permafrost environments. Thethaw<strong>in</strong>g of permafrost is suggested to be associated with a massive releaseof greenhouse gases, <strong>in</strong> particular methane. Thus, Arctic permafrostregions play a fundamental role with<strong>in</strong> the global carbon cycle and thefuture development of Earth’s climate. To understand how the system willrespond to climate changes it is not only important to <strong>in</strong>vestigate thecurrent status of carbon turnover but also how the system reacted toclimate changes <strong>in</strong> the past.This presentation therefore takes a journey through time from the recentactive layer of permafrost to Holocene and Late Pleistocene permafrostdeposits <strong>in</strong> the Siberian Arctic, to reconstruct the microbial driven methanedynamics. Generally, <strong>in</strong>-situ methane contents of the deposits reflect theTOC profile with depth underl<strong>in</strong><strong>in</strong>g the correlation of the distribution oforganic matter and methanogenesis. Significant amounts of methane couldalso be found <strong>in</strong> Late Pleistocene deposits of an age of 30 and 41 ka,respectively. Lipid biomarkers and amplifiable DNA were successfullyrecovered throughout the whole permafrost sequences with an age of up to42 ka. Analysis of the abundance and distribution of archaeol, an <strong>in</strong>dicatorfor fossil methanogenic communities, revealed a temperature response toclimate changes dur<strong>in</strong>g the Late Pleistocene and Holocene. Past warm<strong>in</strong>gtrends seem to cause an enhanc<strong>in</strong>g of methanogenic communities, whilecool<strong>in</strong>g trends conversely caused them to decrease. Furthermore,<strong>in</strong>dications for recently liv<strong>in</strong>g archaeal communities <strong>in</strong> frozen groundcould be found, us<strong>in</strong>g phospholipid ether lipids (PLEL) and 16S rRNAf<strong>in</strong>gerpr<strong>in</strong>ts as specific markers. The obta<strong>in</strong>ed data on present and pastmethanogenic communities suggest a response to future warm<strong>in</strong>g events aswas reconstructed from previous warmer periods.SMP025FISH <strong>in</strong> soil: applications for the <strong>in</strong> situ <strong>in</strong>vestigation ofmicroorganismsH. Schmidt*, T. EickhorstUniversity of Bremen, Soil Science, Bremen, GermanyFluorescence <strong>in</strong> situ hybridization (FISH) represents a powerful methodfor the phylogenetic identification, enumeration, and visualization ofs<strong>in</strong>gle microbial cells <strong>in</strong> soil. The applicability of this tool for studies <strong>in</strong>soil microbiology is exemplarily shown on the basis of several FISHapproaches which are used <strong>in</strong> our lab.For rout<strong>in</strong>e applications of FISH <strong>in</strong> soil, the amplification of fluorescentsignals (CARD) is necessary for a clear discrim<strong>in</strong>ation of target signalsfrom the <strong>in</strong>tense background <strong>in</strong>duced by organic matter, high contents ofclay, and plant tissue. CARD-FISH <strong>in</strong> soil provides quantitative data ofs<strong>in</strong>gle microbial cells, and thus gives <strong>in</strong>sight <strong>in</strong>to the composition ofmicrobial consortia associated with different microenvironments (e.g. bulksoil and rhizosphere).With CARD-FISH applied to roots, the enumeration of s<strong>in</strong>gle cells as wellas the analysis of the spatial distribution of these microbes on therhizoplane gives additional <strong>in</strong>formation for comprehensive studies <strong>in</strong> thesoil-root <strong>in</strong>terface. Especially on roots, sequential hybridizations withfluorochromes of different spectral characteristics have shown to be usefulfor the analysis of microorganisms on doma<strong>in</strong> specific or hierarchic levels.The comb<strong>in</strong>ation of FISH and micropedology (res<strong>in</strong> embedd<strong>in</strong>g and th<strong>in</strong>section<strong>in</strong>g of soil samples) allows for the <strong>in</strong> situ detection of s<strong>in</strong>glemicroorganisms <strong>in</strong> the undisturbed soil matrix. The simultaneous use ofmultiple oligonucleotide probes thereby provides <strong>in</strong>formation on thespatial distribution of microorganisms belong<strong>in</strong>g to different taxonomicdivisions.In the recently developed gold-FISH protocol, conjugates labelled withfluorochromes and nanogold particles allow the comb<strong>in</strong>ative approach ofanalyz<strong>in</strong>g microorganisms by epifluorescence and scann<strong>in</strong>g electronmicroscopy. It is therefore possible to identify and localize s<strong>in</strong>gle microbialcells <strong>in</strong> situ on an ultrastructural level. Furthermore, the biochemical conditions<strong>in</strong> the microbial habitat of gold-FISH detected cells can be characterized byelement mapp<strong>in</strong>g generated with energy dispersive X-ray spectroscopy.SMP026Bacterial communities change along a glacier forefieldtransect - A comb<strong>in</strong>ed approach of molecular f<strong>in</strong>gerpr<strong>in</strong>ts (T-RFLP) and environmental analysesF. Bajerski*, D. WagnerAlfred Wegener <strong>in</strong>stitute for polar and mar<strong>in</strong>e research, PeriglacialResearch, Potsdam, GermanyGlacier forefields are known to be a pioneer site for primary successionand <strong>in</strong>habit extreme climatic and environmental conditions. Retreat<strong>in</strong>gglaciers expose new terrestrial terra<strong>in</strong> that becomes accessible for soilformation and microbial colonisation. Pioneer microorganisms supportweather<strong>in</strong>g processes and the colonisation of more complex microbialcommunities or plants. Because <strong>in</strong>creas<strong>in</strong>g temperatures due to climatechange enhance glacial degradation, it is important to understand howbacterial communities react to chang<strong>in</strong>g environmental conditions. Acomb<strong>in</strong>ed approach of geochemical and microbiological exam<strong>in</strong>ations willbe used to describe the habitat characteristics and the complex system ofmicrobial communities <strong>in</strong> two glacier forefields on Larsemann Hills, EastAntarctica. Term<strong>in</strong>al Restriction Length Polymorphism Analyses showthat bacterial community structures vary significantly between glacierforefields of different development status. Although relatively low,enzyme activities <strong>in</strong>crease with an advanced forefield development anddecrease with <strong>in</strong>creas<strong>in</strong>g depth. The extreme habitat conditions becomeapparent with<strong>in</strong> the geochemical and geochemical properties. The studysite is characterised by very low nutrient and water availability and acoarse gra<strong>in</strong> size. Statistics reveal a connection between environmental andbiological data and the position of the sample <strong>in</strong> the glacier forefield.Altogether our results show a high abundance and variability ofmicroorganisms <strong>in</strong> the hardly developed habitat glacier forefield.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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42 SHORT LECTURESMonday, March 19,
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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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- 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 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