74as health problem due to the allergenic potential of these exceptional stablecompounds.Although their abundance <strong>in</strong> nature, little is known about thebiodegradation of this substance class and only for few stra<strong>in</strong>s hydrolysisof DKPs is reported. In this study we present different approaches toidentify potential DKP degrad<strong>in</strong>g stra<strong>in</strong>s and enzymes, test<strong>in</strong>g eight DKPssynthesized from prote<strong>in</strong>ogenic am<strong>in</strong>o acids and three from nonprote<strong>in</strong>ogenicam<strong>in</strong>o acids (e.g. sarcos<strong>in</strong>e) as substrates:- Despite peptidase activity aga<strong>in</strong>st some DKPs has been reported sometime ago [3] tested activities could not be confirmed <strong>in</strong> our lab. Furtherexperiments with additional peptidases <strong>in</strong>dicate peptidase stability for allused DKPs.- Recently certa<strong>in</strong> cyclic amidases (hydanto<strong>in</strong>ases) have been shown toalso cleave dihydropyrimid<strong>in</strong>e derivatives which are structurally related toDKPs [4]. We could demonstrate degradation of different DKPs by threestra<strong>in</strong>s exhibit<strong>in</strong>g such cyclic amidase activity. Whether the responsibleenzymes are the same is subject of further <strong>in</strong>vestigations.- Paenibacillus chibensis (DSM 329) and Streptomyces flavovirens (DSM40062) have been described to hydrolyze the aspartame derivativecyclo(L-Asp-L-Phe) [5]. In our studies this activity appeared to besubstrate <strong>in</strong>ducible <strong>in</strong> S. flavovirens but not <strong>in</strong> P. chibensis. Moreover wedetected the degradation of an additional substrate cyclo(L-Asp-L-Asp) byP. chibensis while no other of the tested DKPs was hydrolyzed by one ofthese stra<strong>in</strong>s.- Two bacterial stra<strong>in</strong>s isolated dur<strong>in</strong>g this study were shown toenantioselectively cleave racemic cyclo(DL-Ala-DL-Ala). We coulddemonstrate that the cyclo(D-Ala-D-Ala) isomer was not attacked by bothstra<strong>in</strong>s which were identified as Microbacterium sp. and Paenibacillus sp.by 16S rDNA sequence analysis.1. M.B. Mart<strong>in</strong>s, I. Carvalho, Tetrahedron63(2007), p. 9923.2. A. Lamm, I. Gozlan, A. Rotste<strong>in</strong>, D. Avisar, J Env Sci Health Part A44(2009), p. 1512.3. T. Ishiyama, J Biochem17(1933), p. 287.4. U. Engel, C. Syldatk, J. Rudat, Appl Microbiol Biotechnol, published onl<strong>in</strong>e Nov 27th, 2011.5. EP 0 220 028 - B1 (1990) AJINOMOTO CO.EMP2-FGEthylbenzene - Isotope fractionation measurements as a tool tocharacterize aerobic and anaerobic biodegradationC. Dorer* 1 , A.J.M. Stams 2 , H.H. Richnow 1 , C. Vogt 11 Helmholtz Centre for Environmental Research - UFZ, Department ofIsotope Biogeochemistry, Leipzig, Germany2 Wagen<strong>in</strong>gen University, Laboratory of Microbiology, Wagen<strong>in</strong>gen,NetherlandsBTEX compounds (benzene, toluene, ethylbenzene and xylenes) arecommon pollutants <strong>in</strong> our environment released from spill<strong>in</strong>gs of gasol<strong>in</strong>e.As hydrocarbons are chemically <strong>in</strong>ert compounds they need to be activatedto start degradation processes. For long time only molecular oxygen ashighly reactive cosubstrate was known to <strong>in</strong>itiate biological decompositionof these compounds. In the last years biochemically completely differentmechanisms for <strong>in</strong>itial attack under anoxic conditions were elucidated.Two of them are relevant for ethylbenzene degradation: fumarate additionand oxygen-<strong>in</strong>dependent hydroxylation. The better we know whichbiodegradation process prevails the better it is possible to make reliablepredictions for remediation measures.Here we present isotope fractionation measurements of carbon andhydrogen as a tool to characterize the biodegradation processes ofethylbenzene and a cheap means for monitor<strong>in</strong>g the transformation atcontam<strong>in</strong>ated sites. Different reaction mechanisms are reflected bydifferent isotope effects (the result of different reaction rates of moleculesconta<strong>in</strong><strong>in</strong>g the light or the heavy isotope). By this way the <strong>in</strong>itial step ofvarious degradation pathways can be differed by determ<strong>in</strong><strong>in</strong>g the s<strong>in</strong>gleand comb<strong>in</strong>ed fractionation behaviour of carbon and hydrogen.Investigated ethylbenzene dehydrogenase catalysed reactions by nitratereduc<strong>in</strong>gtest organisms (Aromatoleum aromaticum, Georgfuchsiatoluolica and Azoarcus sp.) show a pronounced hydrogen fractionationcontrast<strong>in</strong>g to aerobic transformation via hydroxylation of the side-cha<strong>in</strong> orthe r<strong>in</strong>g (<strong>in</strong>vestigated for Pseudomonas putida and an enrichment culturedom<strong>in</strong>ated by an Acidovorax-related species, respecively. Furthermoremask<strong>in</strong>g effects can be excluded by look<strong>in</strong>g at two elements at the sametime.Altogether the newly ga<strong>in</strong>ed isotopic enrichment factors from various labcultures will be useful for application at field sites and will complete thepicture of isotope effects for BTEX compounds.EMP3-FGChloroethenes <strong>in</strong> a historical context: From recalcitrance tocomplete m<strong>in</strong>eralizationS. Mungenast*, I. Kranzioch, I. Kranzioch, K.R. Schmidt, A. TiehmDVGW-Water Technology Center (TZW), Department of EnvironmentalBiotechnology, Karlsruhe, GermanyChloroethenes were identified as common contam<strong>in</strong>ants <strong>in</strong> groundwater asearly as the 1970s (1). Their extensive use as degreas<strong>in</strong>g or dry clean<strong>in</strong>gsolvents and synthetic feed stocks until today has led to groundwatercontam<strong>in</strong>ation world wide. They are <strong>in</strong>cluded <strong>in</strong> the USEPA’s list ofprimary regulated dr<strong>in</strong>k<strong>in</strong>g water contam<strong>in</strong>ants (2), because of their toxicand carc<strong>in</strong>ogenic effects on human health.Common consensus until 1980 was that chlor<strong>in</strong>ated ethenes(Tetrachloroethene (=Perchloroethene, PCE); Trichloroethene (TCE); thethree dichloroethenes isomers (cDCE, tDCE, 1,1DCE) and v<strong>in</strong>yl chloride(VC)) were recalcitrant to biodegradation. This op<strong>in</strong>ion was supported bythe fact that these compounds were thought to be only of anthropogenicorig<strong>in</strong>. In addition to that only little importance was assigned to biologicalprocesses <strong>in</strong> groundwater before the 1980s (1).After several studies on the fate of PCE and TCE <strong>in</strong> anaerobicgroundwater and the accumulation of cDCE or VC as possibletransformation products, it was clear at the end of the 1980s that microbialreductive dechlor<strong>in</strong>ation can take place <strong>in</strong> anaerobic, chloroethenecontam<strong>in</strong>ated aquifers. From that time on researchers all over the worldaddressed biological degradation of chloroethenes under different redoxconditionsand with a wide range of auxiliary substrates. Today thecommon op<strong>in</strong>ion is that chloroethenes with higher chlor<strong>in</strong>e content (PCE,TCE) can be degraded more easily under anaerobic conditions serv<strong>in</strong>g aselectron acceptors and chloroethenes with lower chlor<strong>in</strong>e content (DCE,VC) can be degraded more easily under aerobic conditions serv<strong>in</strong>g aselectron donors (3).Here we want to report recent f<strong>in</strong>d<strong>in</strong>gs on reductive dechlor<strong>in</strong>ation, onaerobic metabolism (cometabolic and productive) of lower chlor<strong>in</strong>atedethenes and on first results <strong>in</strong>dicat<strong>in</strong>g that aerobic productivebiodegradation of TCE is possible.(1) P. M. Bradley, Bioremediation Journal72003, p. 81.(2) Code of Federal Regulations Title 40, Pt.141.50 (2002 ed).(3) A. Tiehm and K. R. Schmidt, Current Op<strong>in</strong>ion <strong>in</strong> Biotechnology22(2011), p. 415.(4) The authors k<strong>in</strong>dly acknowledge f<strong>in</strong>ancial support by BMWi (AiF project no. 16224 N).EMP4-FGSoil microbial communities <strong>in</strong>volved <strong>in</strong> carbon cycl<strong>in</strong>g dur<strong>in</strong>gleaf litter degradation of annual and perennial plantsS. Wallisch* 1,2 , W. Heller 3 , S. Stich 3 , F. Fleischmann 4 , M. Schloter 2,51 Helmholtz Zentrum München, environmental genomics, Oberschleissheim,Germany2 Technische Universitaet Muenchen, Chair of Soil Ecology, Neuherberg,Germany3 HelmholtzZentrum Muenchen – German Research Center for EnvironmentalHealth, Institute of Biochemical Plant Pathology, Research Group of PlantAbiotic Stress, Neuherberg, Germany4 Technische Universität München, Phytopathology of Woody Plants,Freis<strong>in</strong>g, Germany5 HelmholtzZentrum Muenchen, Research Unit Environmental Genomics,Neuherberg, GermanyMicrobial degradation of plant litter materials provides the primaryresources for organic matter formation <strong>in</strong> soil. The aim of this study was toenlighten the role of bacterial colonisation on leaf litter fragments and to<strong>in</strong>vestigate shifts <strong>in</strong> microbial diversity dur<strong>in</strong>g leaf litter degradation <strong>in</strong> thecontext of carbon cycl<strong>in</strong>g.Therefore, we compared two different litter types: (I)Zea maysas annualand (II)Fagus sylvaticaas perennial model plant. Leafs were sewed <strong>in</strong>tonylon bags and <strong>in</strong>cubated for up to eight (Z. mays) and thirty (F. sylvatica)weeks, respectively, <strong>in</strong> the soil. The state of degradation was determ<strong>in</strong>edby the loss of dry weight. For molecular analyses 16S rRNA genes weredetected by two different f<strong>in</strong>gerpr<strong>in</strong>t<strong>in</strong>g techniques, term<strong>in</strong>al restrictionfragment length polymorphism (T-RFLP) and enterobacterial repetitive<strong>in</strong>tergenic consensus sequences (ERIC). To get a deeper <strong>in</strong>sight whichbacterial communities are <strong>in</strong>volved <strong>in</strong> litter degradation next generationsequenc<strong>in</strong>g us<strong>in</strong>g a 454 platform was performed. Additionally, the amountof sugars, am<strong>in</strong>o sugars and phenols was analysed.First results of the experiment with litter of the annual plant showed aconsistent pattern of microbial community shifts. T-RFLP, ERIC andsequenc<strong>in</strong>g results reflected concordantly changes of the bacterialcommunity over time. Summariz<strong>in</strong>g, microbial diversity <strong>in</strong>creased dur<strong>in</strong>gleaf litter degradation and bacterial stra<strong>in</strong>s related to carbon cycl<strong>in</strong>g suchasAct<strong>in</strong>omycetesandMyxococcalescould be identified. Further analyseswill reveal how microbial diversity develops on perennial leaf litter.Different results are expected as the litter ofF. sylvaticaconta<strong>in</strong>s higheramounts of persistent substances as lign<strong>in</strong> and celluloses compared toZeamays.EMP5-FGBenzotriazole derivatives: biodegradation patterns with threedifferent activated sludge biocenosesB. Herzog* 1 , H. Lemmer 2 , H. Horn 1 and E. Müller 11 Institute of Water Quality Control, TU München, Garch<strong>in</strong>g, Germany2 Bavarian Environment Agency, Munich, GermanyThe compounds benzotriazole (BT), 5-methylbenzotriazole (5-TTri) and 4-methylbenzotriazole (4-TTri) are polar micropollutants widely used asBIOspektrum | Tagungsband <strong>2012</strong>
75corrosion <strong>in</strong>hibitors <strong>in</strong> dishwash<strong>in</strong>g detergents and <strong>in</strong> deic<strong>in</strong>g or anti-ic<strong>in</strong>gfluids on airplanes. Due to their widespread usage <strong>in</strong> many applications,their high polarity and therefore good water solubility on one hand andtheir poor biodegradability on the other, these compounds are found <strong>in</strong>nearly all aquatic compartments <strong>in</strong>clud<strong>in</strong>g ground water. For that reasonthere is urgent need to shed more light on the biological relevance ofbenzotriazole derivatives. The aim of the present work is to ga<strong>in</strong> <strong>in</strong>sight<strong>in</strong>to selected BT derivatives biodegradation patterns by bench scale testswith three different activated sludge biocoenoses derived from threewastewater treatment systems: WWTP 1 with membrane technology,WWTP 2 equipped with a two-step activated sludge treatment and WWTP3 with an <strong>in</strong>termittent nitrification/denitrification regime. After <strong>in</strong>oculationwith 5 g L -1 MLSS and 10 mg L -1 of BT or else a 10 mg L -1 mixture of 4-TTri and 5-TTri ( 40/60%) the reactors, rang<strong>in</strong>g from 100 to 500 ml <strong>in</strong>volume, were operated under different nutrient and biomass conditions toevaluate the best setup for aerobically degrad<strong>in</strong>g benzotriazole compounds.Biodegradation was shown best for 5-TTri followed by BT and worst for4-TTri <strong>in</strong> all reactors regardless which sludge was applied. Concern<strong>in</strong>g thedegradation rate over time the sludge from WWTP 1 proved best, followedby WWTP 2 and 3. Also the concentration of nutrients and energy sourcessuch as C- and N-substrates proved to be important. Thus by dos<strong>in</strong>g thebenzotriazoles as co-substrates together with an easily utilizable C- and N-source degradation turned out faster compared to reactors fedbenzotriazoles as sole C- and/or N-source. In addition to the laboratoryexperiments environmental water samples were collected to check the<strong>in</strong>fluence of WWT retention times on biodegradation. Moreover,benzotriazole concentrations <strong>in</strong> the receiv<strong>in</strong>g rivers were determ<strong>in</strong>ed.These studies showed <strong>in</strong> all tested waters benzotriazoles to be found atconcentrations rang<strong>in</strong>g from 0.50 to 31.0 g L -1 . WWTPs turned out toconstitute one major po<strong>in</strong>t source for benzotriazoles <strong>in</strong>to the aquaticenvironment. Ongo<strong>in</strong>g research is focus<strong>in</strong>g on benzotriazole degrad<strong>in</strong>gorganisms' or communities' characterization at aerobic and anaerobicconditions and locat<strong>in</strong>g of possible <strong>in</strong>termediates or end-products.FBV1-FGNo abstract submitted!FBV2-FGThe carbon depletion response of Aspergillus niger dur<strong>in</strong>gsubmerged cultivation.B.M. Nitsche* 1 , T.R. Jrgensen 1,2 , V. Meyer 2,3 , A.F.J. Ram 1,21 Leiden University, Institute of Biotechnology, Leiden, Netherlands2 Kluyver Centre for Genomics of Industrial Fermentation, Delft, Netherlands3 Berl<strong>in</strong> University of Technology, Institute of Biotechnology, Berl<strong>in</strong>, GermanyBackground: Filamentous fungi experience carbon limitation <strong>in</strong> both theirnatural habitats and biotechnological operations. Compared to nutrient-richgrowth conditions, carbon limitation triggers dramatic changes affect<strong>in</strong>gvirtually all cellular processes. Liberation of carbon from extra- and<strong>in</strong>tracellular sources fuel<strong>in</strong>g fungal self-propagation can be considered astheir key response. Comprehensive description of the processes <strong>in</strong>volvedand their <strong>in</strong>teractions are important to ga<strong>in</strong> further understand<strong>in</strong>g on asystems-level. Increas<strong>in</strong>g knowledge will be relevant for <strong>in</strong>dustrial,medical and fundamental research to improve yields of bioprocesses anddevelop new antifungal strategies.Results: This study describes the physiological, morphological andgenome-wide transcriptional changes caused by severe carbon limitationdur<strong>in</strong>g prolonged submerged batch cultivation of the filamentous fungusAspergillus niger. The application of bioreactors allowed for highlyreproducible cultivation conditions and monitor<strong>in</strong>g of physiologicalparameters. We describe the dispersed hyphal morphology at dist<strong>in</strong>ctcultivation phases and applied automated image analysis to illustrate thedynamics of cryptically re-grow<strong>in</strong>g hyphae. Us<strong>in</strong>g the AffymetrixGeneChip platform, we established genome-wide transcriptional profilesfor day 1, 3 and 6 of carbon limitation. Compared to exponential growthconditions, roughly 50% (7292) of all genes were differentially expresseddur<strong>in</strong>g at least one of the starvation time po<strong>in</strong>ts. To identify majortranscriptional trends, we performed enrichment analysis of GeneOntology, Pfam doma<strong>in</strong> and Kyoto Encyclopedia of Genes and Genomespathway annotations. Among the predom<strong>in</strong>antly <strong>in</strong>duced processes areautophagy and asexual reproduction. Furthermore, we discuss thetranscriptional profiles of enzyme classes, which have been reported toplay important roles <strong>in</strong> ag<strong>in</strong>g cultures of filamentous fungi, such aschit<strong>in</strong>ases, glucanases and proteases.Conclusions: Us<strong>in</strong>g an <strong>in</strong>terdiscipl<strong>in</strong>ary approach, which comb<strong>in</strong>es highlyreproducible cultivation conditions with bio<strong>in</strong>formatics <strong>in</strong>clud<strong>in</strong>gautomated image analysis, genome-wide transcriptional profil<strong>in</strong>g andenrichment analysis, this study provides the first comprehensive analysisof the carbon depletion response <strong>in</strong> filamentous fungi. The generated datawill be fundamental to further improve our understand<strong>in</strong>g of <strong>in</strong>terrelatedprocesses triggered by carbon limitation such as autolysis, proteolysis, celldeath, and reproduction.FBV3-FGBlood is a very special fluid - the transcriptome of Aspergillusfumigatus <strong>in</strong> response to human bloodP. Olbermann* 1 , S. Tarazona 2 , H. Irmer 3 , C. Jöchl 4 , D. Turras 5 , A. Di Pietro 5 ,H. Haas 4 , G.H. Braus 3 , A. Conesa 2 , S. Krappmann 11 Universität Würzburg, Zentrum für Infektionsforschung, Würzburg, Germany2 Centro de Investigacion Príncipe Felipe, Bio<strong>in</strong>formatics and GenomicsDepartment, Valencia, Spa<strong>in</strong>3 University of Gött<strong>in</strong>gen, Institute for Microbiology and Genetics, Gött<strong>in</strong>gen,Germany4 Innsbruck Medical University, Division of Molecular Biology, Innsbruck,Australia5 University of Cordoba, Department of Genetics, Cordoba, Spa<strong>in</strong>Aspergillus fumigatus is the major cause of Invasive Aspergillosis (IA), alife threaten<strong>in</strong>g disease with a mortality rate of 90 to 95 % that affectsprimarily immunocompromised <strong>in</strong>dividuals. A pivotal step l<strong>in</strong>ked toseverity of this disease is the entry of the fungus <strong>in</strong>to a blood vessel and itsdissem<strong>in</strong>ation <strong>in</strong>to the blood circuit. Upon enter<strong>in</strong>g the blood stream A.fumigatus has to adapt to its new environment and to cope with multiplefactors. Although transcriptomes of several host <strong>in</strong>fect<strong>in</strong>g fungi have beenpublished recently, knowledge about the adaptation of the A. fumigatustranscriptome to blood environment <strong>in</strong>side the human host is scarce andlimits understand<strong>in</strong>g of pathogenesis and A. fumigatus dissem<strong>in</strong>ation.To ga<strong>in</strong> <strong>in</strong>sight <strong>in</strong>to this part of <strong>in</strong>fection and transcriptional networks<strong>in</strong>volved <strong>in</strong> this process, we developed an <strong>in</strong> vitro model us<strong>in</strong>g humanblood mimick<strong>in</strong>g haematogenous dissem<strong>in</strong>ation <strong>in</strong>clud<strong>in</strong>g a time courseanalysis to elucidate the differences of fungal response at several timepo<strong>in</strong>ts towards blood. This model was used to capture the gene expressionthat can be found dur<strong>in</strong>g adaptational processes of the fungus. Sampleswere analysed by whole genome expression profil<strong>in</strong>g us<strong>in</strong>g microarraysfollowed by gene enrichment analysis and further bio<strong>in</strong>formatic analysis.Herewith we could identify multiple genes <strong>in</strong>volved <strong>in</strong> adaptation of A.fumigatus to blood such as genes <strong>in</strong>volved <strong>in</strong> signal<strong>in</strong>g, growth regulationand metabolism. As a first application of our <strong>in</strong> vitro model we alsomeasured the transcriptional response of A. fumigatus to human bloodwhen exposed to the antifungal posaconazole. This gave us the possibilityto identify the responses of the fungus when cop<strong>in</strong>g with the drug <strong>in</strong> theenvironment <strong>in</strong> which it acts <strong>in</strong> human treatment. Additionally those datawere confirmed us<strong>in</strong>g real-time qPCR to support the role of certa<strong>in</strong> genesfor the survival of A. fumigatus <strong>in</strong> blood.This analysis will provide important <strong>in</strong>sights regard<strong>in</strong>g the genes <strong>in</strong>volved<strong>in</strong> stages of IA and thus may lead the way to new targets for fight<strong>in</strong>g thisopportunistic pathogen. The model allows us to test the role of A.fumigatus and factors affect<strong>in</strong>g the pathogen <strong>in</strong> this unique environment.FBV4-FGProteomic profil<strong>in</strong>g of the short-term response of Aspergillusfumigatus to hypoxic growth conditionsK. Kroll* 1,2 , M. Vödisch 1,2 , M. Roth 3 , A.A. Brakhage 1,2 , O. Kniemeyer 1,21 Hans-Knöll-Institute, Department of Molecular and AppliedMicrobiology, Jena, Germany2 Friedrich-Schiller-University Jena, Jena, Germany3 Hans-Knöll-Institute, Department of Bio Pilot Plant, Leibniz Institute forNatural Product Research and Infection Biology, Jena, GermanyAspergillus fumigatus is an opportunistic airborne pathogen caus<strong>in</strong>gsystemic <strong>in</strong>fections <strong>in</strong> immunocompromised patients. This filamentousfungus is an obligate aerobe and requires molecular oxygen for growth.However, dur<strong>in</strong>g the <strong>in</strong>fection process A. fumigatus has to adapt quickly tovery low oxygen concentrations when it grows <strong>in</strong> <strong>in</strong>flammatory, necrotictissue. Recently, it was shown that hypoxia is <strong>in</strong>volved <strong>in</strong> virulence of A.fumigatus [1]. In our lab, the metabolic long-term response of this fungushas recently been analyzed by us<strong>in</strong>g an oxygen-controlled chemostat [2].However, little is known about the short-term adaptive mechanisms of A.fumigatus to low oxygen concentrations. Therefore, we aimed to<strong>in</strong>vestigate the immediate response of A. fumigatus after oxygen depletionon the prote<strong>in</strong> level.A. fumigatus was cultivated as a batch culture <strong>in</strong> a 3 L bioreactor. Afterpre-cultivation at 21 % (vol/vol) molecular oxygen concentration, theoxygen supply was shifted to 0.2 % (vol/vol) and several samples weretaken dur<strong>in</strong>g a 24 hour period of hypoxia. Cytosolic prote<strong>in</strong> levels wereanalyzed by 2D - gel electrophoresis and differentially regulated prote<strong>in</strong>swere identified by MALDI-TOF/TOF-analysis.Significant changes <strong>in</strong> the am<strong>in</strong>o acid, carbohydrate and energymetabolism were observed with<strong>in</strong> 24 hours of hypoxia. Glycolyticenzymes and prote<strong>in</strong>s <strong>in</strong>volved <strong>in</strong> am<strong>in</strong>o acid metabolism were upregulated.Furthermore, there was an <strong>in</strong>creased production of prote<strong>in</strong>s<strong>in</strong>volved <strong>in</strong> respiration, electron transport and the general stress response.By contrast, prote<strong>in</strong>s of the pentose phosphate pathway (PPP) and the TCAcycle were down regulated dur<strong>in</strong>g the short-term response, as well.Under hypoxic conditions, we determ<strong>in</strong>ed a strong up-regulation of thealcohol dehydrogenase AlcA which is <strong>in</strong>volved <strong>in</strong> the utilization of ethanolBIOspektrum | Tagungsband <strong>2012</strong>
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SPONSORS & EXHIBITORS9Sponsoren und
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- Page 72 and 73: 72CEP032Yeast mitochondria as a mod
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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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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
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170the absence of legally mandated
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172where lowest concentrations were
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174PSV008Physiological effects of d
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176of pH i in vivo using the pH sen
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178PSP010Crystal structure of the e
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180PSP018Screening for genes of Sta
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182In order to overproduce all enzy
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184substrate specific expression of
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186potential active site region. We
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188PSP054Elucidation of the tetrach
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190family, but only one of these, t
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192network stabilizes the reactive
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194conditions tested. Its 2D struct
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196down of RSs2430 influences the e
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198demonstrating its suitability as
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200RSP025The pH-responsive transcri
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202attracted the attention of molec
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204A (CoA)-thioester intermediates.
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206Ser46~P complex. Additionally, B
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208threat to the health of reefs wo
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210their ectosymbionts to varying s
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212SMV008Methanol Consumption by Me
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214determined as a function of the
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216Funding by BMWi (AiF project no.
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218broad distribution in nature, oc
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220SMP027Contrasting assimilators o
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222growing all over the North, Cent
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224SMP044RNase J and RNase E in Sin
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226labelled hydrocarbons or potenti
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228SSV009Mathematical modelling of
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230SSP006Initial proteome analysis
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232nine putative PHB depolymerases
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234[1991]. We were able to demonstr
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236of these proteins are putative m
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238YEV2-FGMechanistic insight into
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240 AUTORENAbdel-Mageed, W.Achstett
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242 AUTORENFarajkhah, H.HMP002Faral
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244 AUTORENJung, Kr.Jung, P.Junge,
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246 AUTORENNajafi, F.MEP007Naji, S.
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249van Dijk, G.van Engelen, E.van H
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251Eckhard Boles von der Universit
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253Anna-Katharina Wagner: Regulatio
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255Vera Bockemühl: Produktioneiner
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257Meike Ammon: Analyse der subzell
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springer-spektrum.deDas große neue