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Zopfi, Jakob
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Zopfi, Jakob
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Voici les éléments 1 - 10 sur 17
- PublicationMétadonnées seulementVolatiles produced by soil-borne endophytic bacteria increase plant pathogen resistance and affect tritrophic interactions(2014)
; ; Volatile organic compounds (VOCs) released by soil microorganisms influence plant growth and pathogen resistance. Yet, very little is known about their influence on herbivores and higher trophic levels. We studied the origin and role of a major bacterial VOC, 2,3-butanediol (2,3-BD), on plant growth, pathogen and herbivore resistance, and the attraction of natural enemies in maize. One of the major contributors to 2,3-BD in the headspace of soil-grown maize seedlings was identified as Enterobacter aerogenes, an endophytic bacterium that colonizes the plants. The production of 2,3-BD by E.?aerogenes rendered maize plants more resistant against the Northern corn leaf blight fungus Setosphaeria turcica. On the contrary, E.?aerogenes-inoculated plants were less resistant against the caterpillar Spodoptera littoralis. The effect of 2,3-BD on the attraction of the parasitoid Cotesia marginiventris was more variable: 2,3-BD application to the headspace of the plants had no effect on the parasitoids, but application to the soil increased parasitoid attraction. Furthermore, inoculation of seeds with E.?aerogenes decreased plant attractiveness, whereas inoculation of soil with a total extract of soil microbes increased parasitoid attraction, suggesting that the effect of 2,3-BD on the parasitoid is indirect and depends on the composition of the microbial community. - PublicationMétadonnées seulementVolatiles produced by soil-borne endophytic bacteria increase plant pathogen resistance and affect tritrophic interactions(2013)
; ; Volatile organic compounds (VOCs) released by soil microorganisms influence plant growth and pathogen resistance. Yet, very little is known about their influence on herbivores and higher trophic levels. We studied the origin and role of a major bacterial VOC, 2,3-butanediol (2,3-BD), on plant growth, pathogen and herbivore resistance, and the attraction of natural enemies in maize. One of the major contributors to 2,3-BD in the headspace of soil-grown maize seedlings was identified as Enterobacter aerogenes, an endophytic bacterium that colonizes the plants. The production of 2,3-BD by E.?aerogenes rendered maize plants more resistant against the Northern corn leaf blight fungus Setosphaeria turcica. On the contrary, E.?aerogenes-inoculated plants were less resistant against the caterpillar Spodoptera littoralis. The effect of 2,3-BD on the attraction of the parasitoid Cotesia marginiventris was more variable: 2,3-BD application to the headspace of the plants had no effect on the parasitoids, but application to the soil increased parasitoid attraction. Furthermore, inoculation of seeds with E.?aerogenes decreased plant attractiveness, whereas inoculation of soil with a total extract of soil microbes increased parasitoid attraction, suggesting that the effect of 2,3-BD on the parasitoid is indirect and depends on the composition of the microbial community. - PublicationAccès libreIntrinsic biodegradation potential of aromatic hydrocarbons in an alluvial aquifer - Potentials and limits of signature metabolite analysis and two stable isotope-based techniques(2011)
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Firstly, a stable carbon isotope-based field method allowed quantifying biodegradation of monoaromatic compounds in situ and confirmed the degradation of naphthalene. No evidence could be deduced from stable isotope shifts for the intrinsic biodegradation of larger molecules such as methylnaphthalenes or acenaphthene. Secondly, using signature metabolite analysis, various intermediates of the anaerobic degradation of (poly-) aromatic and heterocyclic compounds were identified. The discovery of a novel metabolite of acenaphthene in groundwater samples permitted deeper insights into the anaerobic biodegradation of almost persistent environmental contaminants. A third method, microcosm incubations with 13C-labeled compounds under in situ-like conditions, complemented techniques one and two by providing quantitative information on contaminant biodegradation independent of molecule size and sorption properties. Thanks to stable isotope labels, the sensitivity of this method was much higher compared to classical microcosm studies. The 13C-microcosm approach allowed the determination of first-order rate constants for 13C-labeled benzene, naphthalene, or acenaphthene even in cases when degradation activities were only small. The plausibility of the third method was checked by comparing 13C-microcosm-derived rates to field-derived rates of the first approach. Further advantage of the use of 13C-labels in microcosms is that novel metabolites can be linked more easily to specific mother compounds even in complex systems. This was achieved using alluvial sediments where 13C-acenaphthyl methylsuccinate was identified as transformation product of the anaerobic degradation of acenaphthene. - PublicationAccès libreDiscovery of anammox bacteria in terrestrial ecosystems(2011)
; Avant cette étude, le processus anammox (oxydation anaérobie de l’ammonium) était uniquement étudié dans les usines de traitement des eaux usées et dans les milieux aquatiques, sédiments inclus. Cependant, rien n'était connu encore sur la distribution, la diversité, l'abondance et l'activité des bactéries anammox dans les écosystèmes terrestres. Dans cette étude, nous apportons l’évidence, par approche moléculaire, de la présence de bactéries anammox dans les sols de zones humides, les sédiments des marais, le profil de sol d’un Reductisol, des sols de rives de lacs, un sol sur Permafrost et un aquifère poreux. L'analyse phylogénétique des séquences du gène ARNr 16S a démontrée que les bactéries anammox présentes dans les écosystèmes terrestres sont affiliées à Candidatus ‘Brocadia’, ‘Kuenenia’, ‘Scalindua’, ‘Jettenia’ and ‘Anammoxoglobus’ ainsi qu’à deux groupes non identifiés. Ces candidats anammox étaient largement distribués dans les différents environnements terrestres indiquant une plus grande diversité que dans les colonnes d’eau des milieux marins. Les bactéries anammox n'étaient pas présentes dans tous les milieux et fractions de sol échantillonnés, l’analyse démontrant leur distribution hétérogène et leurs besoins écologiques spécifiques comme la présence d’interfaces oxique / anoxique à long terme et de composés azotés inorganiques. Nous avons quantifié les bactéries anammox dans ces différents environnements en développant une nouvelle approche qPCR spécifique anammox, et leur abondance variait de 104 à 106 copies / g de sol. Finalement, le Réductisol a été sélectionné pour réaliser une analyse détaillée de l’activité anammox le long du profil de sol par des expériences d'incubation à l’isotope 15N. Pour chaque date d'échantillonnage, une production de 29N2 était observée à toutes les profondeurs du Réductisol, démontrant la présence de bactéries anammox actives. La contribution d‘anammox à la production totale de N2 était inférieure à 14%. Cette étude fournit la première preuve que les bactéries anammox sont présentes, diverses et actives dans les écosystèmes terrestres., Until this study, the anammox (anaerobic ammonium oxidation) process has been only studied in waste water treatment plants and aquatic environments, including sediments. However, nothing is known so far about the distribution, diversity, abundance and activity of anammox bacteria in terrestrial ecosystems. In this study, we provided molecular evidence for the presence of anammox bacteria in wetlands, sediments of marshes, a Reductisol profile, lake shores, a permafrost soil and a porous aquifer. Phylogenetic analysis of the 16S rRNA gene sequences showed that anammox bacteria from terrestrial ecosystems are affiliated to Candidatus ‘Brocadia’, ‘Kuenenia’, ‘Scalindua’, ‘Jettenia’ and ‘Anammoxoglobus’, as well as two unidentified clusters. They were widely distributed in the different terrestrial environments indicating a higher diversity than in marine water column environments. Anammox bacteria were not present in every sampled environments and soil fractions demonstrating their heterogeneous distribution and their specific ecological requirements as the presence of long term oxic/anoxic interfaces and inorganic nitrogen compounds. We quantified Anammox bacteria using a new developed qPCR approach applied to the different soil environments and their abundance ranged from 104 to 106 copies/g of soil. Finally, the Reductisol has been selected for a detailed analysis of their activity along the soil profile by 15N-isotope incubation experiments. For each sampling date, production of 29N2 was observed at all depths in the soil profile demonstrating the presence of active anammox bacteria. The amount of N2 produced by anammox is less than 14% of the total N2 production. This study provides the first evidence that anammox bacteria are present, diverse and active in terrestrial ecosystems. - PublicationMétadonnées seulementPercolation and Particle Transport in the Unsaturated Zone of a Karst Aquifer(2009)
; ; Recharge and contamination of karst aquifers often occur via the unsaturated zone, but the functioning of this zone has not yet been fully understood. Therefore, irrigation and tracer experiments, along with monitoring of rainfall events, were used to examine water percolation and the transport of solutes, particles, and fecal bacteria between the land surface and a water outlet into a shallow cave. Monitored parameters included discharge, electrical conductivity, temperature, organic carbon, turbidity, particle-size distribution (PSD), fecal indicator bacteria, chloride, bromide, and uranine. Percolation following rainfall or irrigation can be subdivided into a lag phase (no response at the outlet), a piston-flow phase (release of epikarst storage water by pressure transfer), and a mixed-flow phase (increasing contribution of freshly infiltrated water), starting between 20 min and a few hours after the start of recharge event. Concerning particle and bacteria transport, results demonstrate that (1) a first turbidity signal occurs during increasing discharge due to remobilization of particles from fractures (pulse-through turbidity); (2) a second turbidity signal is caused by direct particle transfer from the soil (flow-through turbidity), often accompanied by high levels of fecal indicator bacteria, up to 17,000 Escherichia coli/100 mL; and (3) PSD allows differentiation between the two types of turbidity. A relative increase of fine particles (0.9 to 1.5 mu m) coincides with microbial contamination. These findings help quantify water storage and percolation in the epikarst and better understand contaminant transport and attenuation. The use of PSD as "early-warning parameter" for microbial contamination in karst water is confirmed. - PublicationAccès libreEvaluating the fate of chlorinated ethenes in streambed sediments by combining stable isotope, geochemical and microbial methods(2009)
; - PublicationAccès libreCarbon and chlorine isotope fractionation during aerobic oxidation and reductive dechlorination of vinyl chloride and cis-1,2-dichloroethene(2009)
; - PublicationAccès libreMicrobial communities in karst groundwater and their potential use for biomonitoring(2009)
; - PublicationAccès libreOrigin and spatial–temporal distribution of faecal bacteria in a bay of Lake Geneva, Switzerland(2009)
; - PublicationAccès librePercolation and Particle Transport in the Unsaturated Zone of a Karst Aquifer(2008)
; ; Recharge and contamination of karst aquifers often occur via the unsaturated zone, but the functioning of this zone has not yet been fully understood. Therefore, irrigation and tracer experiments, along with monitoring of rainfall events, were used to examine water percolation and the transport of solutes, particles, and fecal bacteria between the land surface and a water outlet into a shallow cave. Monitored parameters included discharge, electrical conductivity, temperature, organic carbon, turbidity, particle-size distribution (PSD), fecal indicator bacteria, chloride, bromide, and uranine. Percolation following rainfall or irrigation can be subdivided into a lag phase (no response at the outlet), a piston-flow phase (release of epikarst storage water by pressure transfer), and a mixed-flow phase (increasing contribution of freshly infiltrated water), starting between 20 min and a few hours after the start of recharge event. Concerning particle and bacteria transport, results demonstrate that (1) a first turbidity signal occurs during increasing discharge due to remobilization of particles from fractures (pulse-through turbidity); (2) a second turbidity signal is caused by direct particle transfer from the soil (flow-through turbidity), often accompanied by high levels of fecal indicator bacteria, up to 17,000 Escherichia coli/100 mL; and (3) PSD allows differentiation between the two types of turbidity. A relative increase of fine particles (0.9 to 1.5 μm) coincides with microbial contamination. These findings help quantify water storage and percolation in the epikarst and better understand contaminant transport and attenuation. The use of PSD as "early-warning parameter" for microbial contamination in karst water is confirmed.