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

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

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

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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>

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