993 resultados para Bacteria, Anaerobic


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The effects of metal bioleaching on nutrient solubilization, especially nitrogen and phosphorous, from anaerobically-digested sewage sludge were investigated in this work. The assessment of the sanitary quality of the anaerobic sludge after bioleaching was also carried out by enumerating indicator (total coliforms, fecal coliforms, and fecal streptococci) and total heterotrophic bacteria. The experiments of bioleaching were performed using indigenous sulphur-oxidizing bacteria (Thiobacillus spp.) as inoculum and samples of anaerobically-digested sludge. Nitrogen and phosphorous solubilization from sewage sludge was assessed by measuring, respectively, the concentration of Total Kjeldahl Nitrogen, ammonia, nitrate/nitrite, and soluble and total phosphorous before and after the bioleaching assays. At the end of the experiment, after 4 days of incubation (final pH of 1.4), the following metal solubilization yields were obtained: zinc, 91%; nickel, 87%; copper, 79%; lead, 52%; and chromium, 42%. As a result of sludge acidification, the viable counts of selected indicator bacteria were decreased to below the detection limit (4 × 103 cfu 100 ml-1), followed by an increase in the mineral fraction of nitrogen (from 6 to 10%) and in the soluble fraction of phosphorous (from 15 to 30%). Although some loss of sludge nutrients can occur during solid-liquid separation following bioleaching, its beneficial effects as metal removal and reduction of pathogenic bacteria are sufficient to consider the potential of this treatment before sludge disposal onto agricultural fields.

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Organic carbon, lead and cadmium contents of 20 sediments were determined and compared with the colony counts of anaerobic heterotrophic, anaerobic nitrogen fixing, chitinoclastic and cellulolytic bacteria. Organic carbon content, which is dependent on the sediment type, was positively correlated with lead and cadmium as well as with colony counts of all 4 physiological groups of bacteria. Even the sediments with the highest concentrations of 251.7 ppm Pb and 3.1 ppm Cd showed no reduction in their colony counts. From 2 different sediment sampIes with lead contents of 140 ppm and 21 ppm lead tolerance of the aerobic heterotrophic bacteria was investigated. However, no significant difference in lead tolerance of the 2 heterotrophic populations was found. Water from 6 stations was analysed for dissolved and particulate organic carbon, lead and cadmium. Dissolved lead concentrations were in the range of 0.2-0.5 µg/l and the particulate lead contents were between 0.05 and 4.3 µg/l. The concentrations of total lead for the stations off-shore were only one order of magnitude from the concentrations of the near-shore stations. The same phenomenon was observed for dissolved cadmium (0.02 - 0.25 µg/l) and particulate cadmium (0.003 - 0.15 µg/I) concentrations. Correlations between dissolved (1.6 - 10.8 mg/I) and particulate organic carbon (0.25 - 1.53 mg/I) with dissolved and particulate lead or cadmium were not found.

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Includes bibliographies and index.

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Here we reported the fatty-acids and their δ 13C values in seep carbonates collected from Green Canyon lease block 185 (GC 185; Sample GC-F) at upper continental slope (water depth: ∼540 m), and Alaminos Canyon lease block 645 (GC 645; Sample AC-E) at lower continental slope (water depth: ∼2200 m) of the Gulf of Mexico. More than thirty kinds of fatty acids were detected in both samples. These fatty acids are maximized at C16. There is a clear even-over-odd carbon number predominance in carbon number range. The fatty acids are mainly composed of n-fatty acids, iso-/anteiso-fatty acids and terminally branched odd-numbered fatty acids (iso/anteiso). The low δ 13C values (−39.99‰ to.32.36‰) of n-C12:0, n-C13:0, i-C14:0and n-C14:0 suggest that they may relate to the chemosynthetic communities at seep sites. The unsaturated fatty acids n-C18:2 and C18:1Δ9 have the same δ 13C values, they may originate from theBeggiatoa/Thioploca. Unlike other fatty acids, the terminally branched fatty acids (iso/anteiso) show lowerδ 13C values (as low as −63.95‰) suggesting a possible relationship to sulfate reducing bacteria, which is common during anaerobic oxidation of methane at seep sites.

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L’atmosphère terrestre est très riche en azote (N2). Mais cet azote diatomique est sous une forme très stable, inutilisable par la majorité des êtres vivants malgré qu’il soit indispensable pour la synthèse de matériels organiques. Seuls les procaryotes diazotrophiques sont capables de vivre avec le N2 comme source d’azote. La fixation d’azote est un processus qui permet de produire des substances aminées à partir de l’azote gazeux présent dans l’atmosphère (78%). Cependant, ce processus est très complexe et nécessite la biosynthèse d’une vingtaine de protéines et la consommation de beaucoup d’énergie (16 molécules d’ATP par mole de N2 fixé). C’est la raison pour laquelle ce phénomène est rigoureusement régulé. Les bactéries photosynthétiques pourpres non-sulfureuses sont connues pour leur capacité de faire la fixation de l’azote. Les études faites à la lumière, dans le mode de croissance préféré de ces bactéries (photosynthèse anaérobie), ont montré que la nitrogénase (enzyme responsable de la fixation du diazote) est sujet d’une régulation à trois niveaux: une régulation transcriptionnelle de NifA (protéine activatrice de la transcription des gènes nif), une régulation post-traductionnelle de l’activité de NifA envers l’activation de la transcription des autres gènes nif, et la régulation post-traductionnelle de l’activité de la nitrogénase quand les cellules sont soumises à un choc d’ammoniaque. Le système de régulation déjà décrit fait intervenir essentiellement une protéine membranaire, AmtB, et les deux protéines PII, GlnB et GlnK. Il est connu depuis long temps que la nitrogénase est aussi régulée quand une culture photosynthétique est exposée à la noirceur, mais jusqu’aujourd’hui, on ignore encore la nature des systèmes intervenants dans cette régulation. Ainsi, parmi les questions qui peuvent se poser: quelles sont les protéines qui interviennent dans l’inactivation de la nitrogénase lorsqu’une culture anaérobie est placée à la noirceur? Une analyse de plusieurs souches mutantes, amtB- , glnK- , glnB- et amtY- poussées dans différentes conditions de limitation en azote, serait une façon pour répondre à ces interrogations. Alors, avec le suivi de l’activité de la nitrogénase et le Western Blot, on a montré que le choc de noirceur provoquerait un "Switch-off" de l’activité de la nitrogénase dû à une ADP-ribosylation de la protéine Fe. On a réussit aussi à montrer que ii tout le système déjà impliqué dans la réponse à un choc d’ammoniaque, est également nécessaire pour une réponse à un manque de lumière ou d’énergie (les protéines AmtB, GlnK, GlnB, DraG, DraT et AmtY). Or, Rhodobacter capsulatus est capable de fixer l’azote et de croitre aussi bien dans la micro-aérobie à la noirceur que dans des conditions de photosynthèse anaérobies, mais jusqu'à maintenant sa régulation dans l’obscurité est peu étudiée. L’étude de la fixation d’azote à la noirceur nous a permis de montrer que le complexe membranaire Rnf n’est pas nécessaire à la croissance de R. capsulatus dans de telles conditions. Dans le but de développer une façon d’étudier la régulation de la croissance dans ce mode, on a tout d’abord essayé d’identifier les conditions opératoires (O2, [NH4 + ]) permettant à R. capsulatus de fixer l’azote en microaérobie. L’optimisation de cette croissance a montré que la concentration optimale d’oxygène nécessaire est de 10% mélangé avec de l’azote.

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Fundação de Amparo à Pesquisa do Estado de São Paulo (FAPESP)

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Atrophic gastritis patients have intestinal bacterial overgrowth which could produce menaquinones. The aim of this study was to evaluate the interaction between a diet low in phylloquinone and minidoses of warfarin in subjects with and without bacterial overgrowth. Subjects with atrophic gastritis (indicated by serum pepsinogen ratio) and healthy volunteers were studied while fed a restrictive phylloquinone diet and while receiving a minidose of warfarin. Coagulation times, serum osteocalcin, serum undercarboxylated osteocalcin, plasma phylloquinone, plasma K-epoxide, plasma undercarboxylated prothrombin (PIVKA)-II and urinary gamma-carboxyglutamic acid (Gla) were measured. At baseline, there were no differences between groups for any variable measured. Comparisons between baseline and post intervention in both groups, showed significant increases in circulating levels of K-epoxide, PIVKA II and undercarboxylated osteocalcin. However, no differences were observed when comparisons were made between groups. Our data do not support the hypothesis that bacterial synthesis of menaquinones in patients with bacterial overgrowth due to atrophic gastritis confers considerable resistance to the effect of warfarin.