237 research outputs found

    Développement d'outils microbiologiques et chimiques permettant d'identifier l'origine des pollutions fécales dans les eaux de baignades

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    La pollution organique issue des effluents d'Ă©levage et des stations d'Ă©puration urbaines conduit Ă  un problĂšme essentiel de santĂ© publique liĂ© Ă  la contamination des eaux de surface oĂč s'exercent des activitĂ©s sensibles telles que la baignade. S'il est possible de dĂ©terminer les pollutions localisĂ©es liĂ©es Ă  un dysfonctionnement des systĂšmes de traitement, il est beaucoup plus difficile d'identifier les pollutions organiques diffuses qui participent pourtant majoritairement Ă  la dĂ©gradation de la qualitĂ© des eaux de surface. La problĂ©matique des pollutions diffuses est d'autant plus importante que la nouvelle rĂ©glementation europĂ©enne concernant les eaux de baignade (Directive 2006/7/CE) demande de constituer des profils de baignade qui nĂ©cessitent une identification et une hiĂ©rarchisation des sources de pollutions fĂ©cales. Le dĂ©nombrement de Escherichia coli et des entĂ©rocoques intestinaux stipulĂ© par les textes rĂ©glementaires europĂ©ens, reprĂ©sente actuellement le seul outil analytique permettant la mise en Ă©vidence d'une contamination fĂ©cale du milieu aquatique, sans toutefois diffĂ©rencier l'origine humaine ou animale de cette contamination. Il est donc nĂ©cessaire de dĂ©velopper de nouvelles mĂ©thodes de dĂ©tection de la pollution fĂ©cale qui puissent non seulement mettre en Ă©vidence une contamination mais aussi en indiquer l'origine. C'est d'ailleurs dans cet objectif que s'est dĂ©veloppĂ© depuis quelques annĂ©es, le concept de "Microbial Source Tracking" ("Traceurs de Sources Microbiennes") qui consiste Ă  identifier Ă  l'aide de marqueurs microbiologiques ou chimiques les sources de pollutions fĂ©cales. Dans ce contexte, six laboratoires de recherche se sont associĂ©s pour dĂ©velopper des techniques de traçage des contaminations fĂ©cales afin de proposer un outil opĂ©rationnel utilisable pour diffĂ©rencier les sources de pollution, de leur point d'Ă©mission jusqu'au milieu rĂ©cepteur final que constituent les eaux de surface. Les marqueurs qui ont fait l'objet de cette Ă©tude sont des molĂ©cules chimiques naturelles (stĂ©roĂŻdes, cafĂ©ine), des molĂ©cules de synthĂšse retrouvĂ©es dans les effluents de stations d'Ă©puration ou des rapports de fluorescence de la matiĂšre organique ainsi que des micro-organismes (bactĂ©riophages, bactĂ©ries). A la suite des dĂ©veloppements mĂ©thodologiques, plusieurs marqueurs ont Ă©tĂ© sĂ©lectionnĂ©s : - bactĂ©ries appartenant aux groupes bactĂ©riens dominants du tractus intestinal humain (Bifidobacterium adolescentis) et porcin (Lactobacillus amylovorus) ; - Bacteroidales spĂ©cifiques des humains, porcins et bovins (HF183, Pig-2-Bac, Rum-2-Bac); - gĂ©nogroupes humains des bactĂ©riophages F ARN spĂ©cifiques; - rapports de stĂ©roĂŻdes : coprostanol/(24ethylcoprostanol+coprostanol) (R1) et sitostanol/coprostanol (R2); - cafĂ©ine, benzophĂ©none et tri(2-chloroethyl)phosphate (TCEP)

    Robust entropy expansiveness implies generic domination

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    Let f:M→Mf: M \to M be a CrC^r-diffeomorphism, r≄1r\geq 1, defined on a compact boundaryless dd-dimensional manifold MM, d≄2d\geq 2, and let H(p)H(p) be the homoclinic class associated to the hyperbolic periodic point pp. We prove that if there exists a C1C^1 neighborhood U\mathcal{U} of ff such that for every g∈Ug\in {\mathcal U} the continuation H(pg)H(p_g) of H(p)H(p) is entropy-expansive then there is a DfDf-invariant dominated splitting for H(p)H(p) of the form E⊕F1⊕...⊕Fc⊕GE\oplus F_1\oplus... \oplus F_c\oplus G where EE is contracting, GG is expanding and all FjF_j are one dimensional and not hyperbolic.Comment: 24 page

    Decay of correlations for maps with uniformly contracting fibers and logarithm law for singular hyperbolic attractors

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    We consider two dimensional maps preserving a foliation which is uniformly contracting and a one dimensional associated quotient map having exponential convergence to equilibrium (iterates of Lebesgue measure converge exponentially fast to physical measure). We prove that these maps have exponential decay of correlations over a large class of observables. We use this result to deduce exponential decay of correlations for the Poincare maps of a large class of singular hyperbolic flows. From this we deduce logarithm laws for these flows.Comment: 39 pages; 03 figures; proof of Theorem 1 corrected; many typos corrected; improvements on the statements and comments suggested by a referee. Keywords: singular flows, singular-hyperbolic attractor, exponential decay of correlations, exact dimensionality, logarithm la

    Mechanisms of escape phenomenon of spinal cord and brainstem in human rabies

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    BACKGROUND: Rabies virus preferentially involves brainstem, thalamus and spinal cord in human furious and paralytic rabies beginning in the early stage of illness. Nevertheless, rabies patient remains alert until the pre-terminal phase. Weakness of extremities develops only when furious rabies patient becomes comatose; whereas peripheral nerve dysfunction is responsible for weakness in paralytic rabies. METHODS: Evidence of apoptosis and mitochondrial outer membrane permeabilization in brain and spinal cord of 10 rabies patients was examined and these findings were correlated with the presence of rabies virus antigen. RESULTS: Although apoptosis was evident in most of the regions, cytochrome c leakage was relatively absent in spinal cord of nearly all patients despite the abundant presence of rabies virus antigen. Such finding was also noted in brainstem of 5 patients. CONCLUSION: Cell death in human rabies may be delayed in spinal cord and the reticular activating system, such as brainstem, thus explaining absence of weakness due to spinal cord dysfunction and preservation of consciousness

    Specific detection of Salmonella enterica and Escherichia coli strains by using ELISA with bacteriophages as recognition agents

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    The use of bacteriophages, instead of antibodies, in the ELISA-based detection of bacterial strains was tested. This procedure appeared to be efficient, and specific strains of Salmonella enterica and Escherichia coli could be detected. The sensitivity of the assay was about 105 bacterial cells/well (106/ml), which is comparable with or outperforms other ELISA tests detecting intact bacterial cells without an enrichment step. The specificity of the assay depends on the kind of bacteriophage used. We conclude that the use of bacteriophages in the detection and identification of bacteria by an ELISA-based method can be an alternative to the use of specific antibodies. The advantages of the use of bacteriophages are their environmental abundance (and, thus, a possibility to isolate various phages with different specificities) and the availability of methods for obtaining large amounts of phage lysates, which are simple, rapid, cheap, and easy

    Relative Decay of Fecal Indicator Bacteria and Human-Associated Markers: A Microcosm Study Simulating Wastewater Input into Seawater and Freshwater

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    Fecal contaminations of inland and coastal waters induce risks to human health and economic losses. To improve water management, specific markers have been developed to differentiate between sources of contamination. This study investigates the relative decay of fecal indicator bacteria (FIB, Escherichia coli and enterococci) and six human-associated markers (two bacterial markers: Bacteroidales HF183 (HF183) and Bifidobacterium adolescentis (BifAd); one viral marker: genogroup II F-specific RNA bacteriophages (FRNAPH II); three chemical markers: caffeine and two fecal stanol ratios) in freshwater and seawater microcosms seeded with human wastewater. These experiments were performed in darkness, at 20 °C and under aerobic conditions. The modeling of the decay curves allows us (i) to compare FIB and markers and (ii) to classify markers according to their persistence in seawater (FRNAPH II < HF183, stanol ratios < BifAd, caffeine) and in freshwater (HF183, stanol ratios < FRNAPH II < BifAd < caffeine). Although those results depend on the experimental conditions, this study represents a necessary step to develop and validate an interdisciplinary toolbox for the investigation of the sources of fecal contaminations

    Infinitesimal Lyapunov functions for singular flows

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    We present an extension of the notion of infinitesimal Lyapunov function to singular flows, and from this technique we deduce a characterization of partial/sectional hyperbolic sets. In absence of singularities, we can also characterize uniform hyperbolicity. These conditions can be expressed using the space derivative DX of the vector field X together with a field of infinitesimal Lyapunov functions only, and are reduced to checking that a certain symmetric operator is positive definite at the tangent space of every point of the trapping region.Comment: 37 pages, 1 figure; corrected the statement of Lemma 2.2 and item (2) of Theorem 2.7; removed item (5) of Theorem 2.7 and its wrong proof since the statement of this item was false; corrected items (1) and (2) of Theorem 2.23 and their proofs. Included Example 6 on smooth reduction of families of quadratic forms. The published version in Math Z journal needs an errat

    OECD validation study to assess intra- and inter-laboratory reproducibility of the zebrafish embryo toxicity test for acute aquatic toxicity testing

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    The OECD validation study of the zebrafish embryo acute toxicity test (ZFET) for acute aquatic toxicity testing evaluated the ZFET reproducibility by testing 20 chemicals at 5 different concentrations in 3 independent runs in at least 3 laboratories. Stock solutions and test concentrations were analytically confirmed for 11 chemicals. Newly fertilised zebrafish eggs (20/concentration and control) were exposed for 96 h to chemicals. Four apical endpoints were recorded daily as indicators of acute lethality: coagulation of the embryo, lack of somite formation, non-detachment of the tail bud from the yolk sac and lack of heartbeat. Results (LC50 values for 48/96 h exposure) show that the ZFET is a robust method with a good intra- and inter-laboratory reproducibility (CV 30%) for some very toxic or volatile chemicals, and chemicals tested close to their limit of solubility. The ZFET is now available as OECD Test Guideline 236. Considering the high predictive capacity of the ZFET demonstrated by Belanger et al. (2013) in their retrospective analysis of acute fish toxicity and fish embryo acute toxicity data, the ZFET is ready to be considered for acute fish toxicity for regulatory purposes

    Validation of the OECD reproduction test guideline with the New Zealand mudsnail Potamopyrgus antipodarum using trenbolone and prochloraz

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    The Organisation for Economic Cooperation and Development (OECD) provides several standard test methods for the environmental hazard assessment of chemicals, mainly based on primary producers, arthropods, and fish. In April 2016, two new test guidelines with two mollusc species representing different reproductive strategies were approved by OECD member countries. One test guideline describes a 28-day reproduction test with the parthenogenetic New Zealand mudsnail Potamopyrgus antipodarum. The main endpoint of the test is reproduction, reflected by the embryo number in the brood pouch per female. The development of a new OECD test guideline involves several phases including inter-laboratory validation studies to demonstrate the robustness of the proposed test design and the reproducibility of the test results. Therefore, a ring test of the reproduction test with P. antipodarum was conducted including eight laboratories with the test substances trenbolone and prochloraz and results are presented here. Most laboratories could meet test validity criteria, thus demonstrating the robustness of the proposed test protocol. Trenbolone did not have an effect on the reproduction of the snails at the tested concentration range (nominal: 10-1000 ng/L). For prochloraz, laboratories produced similar EC10 and NOEC values, showing the inter-laboratory reproducibility of results. The average EC10 and NOEC values for reproduction (with coefficient of variation) were 26.2 ”g/L (61.7%) and 29.7 ”g/L (32.9%), respectively. This ring test shows that the mudsnail reproduction test is a well-suited tool for use in the chronic aquatic hazard and risk assessment of chemicals
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