28 resultados para water-in-oil emulsion

em Université de Lausanne, Switzerland


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OBJECTIVE: The anticancer action exerted by polyunsaturated fatty acid peroxidation may not be reproduced by commercially available lipid emulsions rich in vitamin E. Therefore, we evaluated the effects of fish oil (FO) emulsion containing α-tocopherol 0.19 g/L on human colorectal adenocarcinoma cells and tumors. METHODS: HT-29 cell growth, survival, apoptosis, and lipid peroxidation were analyzed after a 24-h incubation with FO 18 to 80 mg/L. Soybean oil (SO) emulsion was used as an isocaloric and isolipidic control. In vivo, nude mice bearing HT-29 tumors were sacrificed 7 d after an 11-d treatment with intravenous injections of FO or SO 0.2 g ∙ kg(-1) ∙ d(-1) FO or SO to evaluate tumor growth, necrosis, and lipid peroxidation. RESULTS: The FO inhibited cell viability and clonogenicity in a dose-dependent manner, whereas SO showed no significant effect compared with untreated controls. Lipid peroxidation and cell apoptosis after treatment with FO 45 mg/L were increased 2.0-fold (P < 0.01) and 1.6-fold (P = 0.04), respectively. In vivo, FO treatment did not significantly affect tumor growth. However, immunohistochemical analyses of tumor tissue sections showed a decrease of 0.6-fold (P < 0.01) in the cell proliferation marker Ki-67 and an increase of 2.3-fold (P = 0.03) in the necrotic area, whereas malondialdehyde and total peroxides were increased by 1.9-fold (P = 0.09) and 7.0-fold (P < 0.01), respectively, in tumors of FO-treated compared with untreated mice. CONCLUSION: These results suggest that FO but not SO has an antitumor effect that can be correlated with lipid peroxidation, despite its vitamin E content.

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PURPOSE: To evaluate the potential delay of the retinal degeneration in rd1/rd1 mice using recombinant human glial cell line-derived neurotrophic factor (rhGDNF) encapsulated in poly(D,L-lactide-co-glycolide) (PLGA) microspheres. METHODS: rhGDNF-loaded PLGA microspheres were prepared using a water in oil in water (w/o/w) emulsion solvent extraction-evaporation process. In vitro, the rhGDNF release profile was assessed using radiolabeled factor. In vivo, rhGDNF microspheres, blank microspheres, or microspheres loaded with inactivated rhGDNF were injected into the vitreous of rd1/rd1 mice at postnatal day 11 (PN11). The extent of retinal degeneration was examined at PN28 using rhodopsin immunohistochemistry on whole flat-mount retinas, outer nuclear layer (ONL) cell counting on histology sections, and electroretinogram tracings. Immunohistochemical reactions for glial fibrillary acidic protein (GFAP), F4/80, and rhodopsin were performed on cryosections. RESULTS: Significant delay of rod photoreceptors degeneration was observed in mice receiving the rhGDNF-loaded microspheres compared to either untreated mice or to mice receiving blank or inactivated rhGDNF microspheres. The degeneration delay in the eyes receiving the rhGDNF microspheres was illustrated by the increased rhodopsin positive signals, the preservation of significantly higher number of cell nuclei within the ONL, and significant b-wave increase. A reduction of the subretinal glial proliferation was also observed in these treated eyes. No significant intraocular inflammatory reaction was observed after the intravitreous injection of the various microspheres. CONCLUSIONS: A single intravitreous injection of rhGDNF-loaded microspheres slows the retinal degeneration processes in rd1/rd1 mice. The use of injectable, biodegradable polymeric systems in the vitreous enables the efficient delivery of therapeutic proteins for the treatment of retinal diseases.

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Land plants have developed a cuticle preventing uncontrolled water loss. Here we report that an ATP-binding cassette (ABC) subfamily G (ABCG) full transporter is required for leaf water conservation in both wild barley and rice. A spontaneous mutation, eibi1.b, in wild barley has a low capacity to retain leaf water, a phenotype associated with reduced cutin deposition and a thin cuticle. Map-based cloning revealed that Eibi1 encodes an HvABCG31 full transporter. The gene was highly expressed in the elongation zone of a growing leaf (the site of cutin synthesis), and its gene product also was localized in developing, but not in mature tissue. A de novo wild barley mutant named "eibi1.c," along with two transposon insertion lines of rice mutated in the ortholog of HvABCG31 also were unable to restrict water loss from detached leaves. HvABCG31 is hypothesized to function as a transporter involved in cutin formation. Homologs of HvABCG31 were found in green algae, moss, and lycopods, indicating that this full transporter is highly conserved in the evolution of land plants.

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Background: Transcatheter arterial chemoembolization (TACE) has been shown to offer a survival benefit for patients with intermediate-stage hepatocellular carcinoma (HCC). A widely accepted TACE regimen includes the administration of a doxorubicin-in-oil emulsion followed by gelatine sponge particles. Recently, a drug-eluting bead (DEB) has been developed to enhance drug delivery to the tumor and reduce its systemic availability. Purpose of this randomized trial was to compare conventional TACE with DEB-TACE for the treatment of intermediate-stage HCC in patients with cirrhosis. Methods: Two hundred and twelve patients (185 males and 27 females; mean age, 67 years) with Child-Pugh A or B liver cirrhosis and large and/or multinodular, unresectable HCC were randomized to receive DEB-TACE (DC Bead; Biocompatibles, UK) uploaded with doxorubicin or conventional TACE with doxorubicin, lipiodol, and gelatin sponge particles. Randomization was stratified according to Child Pugh status (A or B), performance status (ECOG 0 or 1), bilobar disease (yes or no) and prior curative treatment (yes or no). Tumor response at 6 months was the primary study endpoint. An independent, blinded review of magnetic resonance imaging studies was conducted to assess tumor response according to amended RECIST criteria. Results: DEB-TACE with doxorubicin showed a higher rate of complete response, objective response and disease control compared with conventional TACE (27% vs 22%; 52% vs 44%; and 63% vs 52%, respectively; p>0.05). Patients with Child Pugh B, ECOG 1, bilobar disease and recurrence following curative treatment showed a significant increase in objective response (p=0.038) compared to the control. There was a marked reduction in serious liver toxicity in patients treated with DEB-TACE. The rate of doxorubicin related side effects was significantly lower (p=0.0001) in the DEB-TACE group compared with the conventional TACE group. Conclusions: DEB-TACE with doxorubicin is safe and effective in the treatment of intermediate-stage HCC and may offer benefit to patients with more advanced disease.

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Depth profiles were sampled at different locations throughout Lake Geneva on a monthly and seasonal basis over the course of 2 years and analysed for their stable hydrogen and oxygen isotope compositions. The isotopic compositions indicate an isotopic stratification in the metalimnion during summer and fall. This is related to mixing of Rhône River water, which in summer is dominated by snow and glacier melt waters, and lake water, with the latter having a homogenous isotopic composition. The observed interflow layer is 7-15 m thick and can be traced by the distinct stable isotope composition of the water for about 55 km throughout the lake as well as into shallow bay regions. Depth of the interflow layer close to the Rhône River mouth is similar to those previously described based on echo-soundings and turbidity profiles of sediment dispersion. In contrast to previous descriptions of the interflow within Lake Geneva, the stable isotope compositions allow for direct, natural tracing of the Rhône River water even in cases where the turbidity and conductivity measurements do not indicate such an interflow. In addition, the method allows for a quantification of the Rhône River and lake water in the interflow with the fraction of Rhône River water within the interflow estimated to be up to 37% in summer. The isotopic composition further indicates different vertical mixing processes within the two lake basins of Lake Geneva, related to the density gradients and local stability within the water column. The method may be applicable to other lakes in catchments with large differences in the topography as water that originates from high altitudes or glaciers has a distinct oxygen and hydrogen isotope composition compared to other sources of water originating at lower altitudes and/or from direct precipitation over the lake. Stable isotope measurements thus improve the understanding of the circulation of water within the lake, which is fundamental for an evaluation of the water residence times, dissolved pollutant and nutrient transport as well as oxygenation.

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Novel formulations of cationic nanoemulsions based on three different lipids were developed to strengthen the attraction of the polyanionic oligonucleotide (ODN) macromolecules to the cationic moieties on the oil nanodroplets. These formulations were developed to prolong the release of the ODN from the nanoemulsion under appropriate physiological dilutions as encountered in the eye following topical application. Increasing the concentration of the new cationic lipid exhibiting two cationic amine groups (AOA) in the emulsion from 0.05% to 0.4% did not alter markedly the particle size or zeta potential value of the blank cationic nanoemulsion. The extent of ODN association did not vary significantly when the initial concentration of ODN remained constant at 10 microM irrespective of the cationic lipid nature. However, the zeta potential value dropped consistently with the low concentrations of 0.05% and 0.1% of AOA in the emulsions suggesting that an electrostatic attraction occurred between the cationic lipids and the polyanionic ODN molecules at the o/w interface. Only the nanoemulsion prepared with N-[1-(2,3-dioleoyloxy)propyl]-N,N,N-trimethylammonium salts (DOTAP) remained physically stable over time. DOTAP cationic lipid nanoemulsion was the most efficient formulation capable of retaining the ODN despite the high dilution of 1:100 with simulated tear solution (STS). Less than 10% of the ODN was exchanged in contrast to 40-50% with the other cationic nanoemulsions. The in-vitro release kinetic behavior of ODN exchange with physiological anions present in the STS appears to be complex and difficult to characterize using mathematical fitting model equations. Further pharmacokinetic studies are needed to verify our kinetic assumptions and confirm the in-vitro ODN release profile from DOTAP cationic nanoemulsions.

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During the first hours after release of petroleum at sea, crude oil hydrocarbons partition rapidly into air and water. However, limited information is available about very early evaporation and dissolution processes. We report on the composition of the oil slick during the first day after a permitted, unrestrained 4.3 m(3) oil release conducted on the North Sea. Rapid mass transfers of volatile and soluble hydrocarbons were observed, with >50% of ≤C17 hydrocarbons disappearing within 25 h from this oil slick of <10 km(2) area and <10 μm thickness. For oil sheen, >50% losses of ≤C16 hydrocarbons were observed after 1 h. We developed a mass transfer model to describe the evolution of oil slick chemical composition and water column hydrocarbon concentrations. The model was parametrized based on environmental conditions and hydrocarbon partitioning properties estimated from comprehensive two-dimensional gas chromatography (GC×GC) retention data. The model correctly predicted the observed fractionation of petroleum hydrocarbons in the oil slick resulting from evaporation and dissolution. This is the first report on the broad-spectrum compositional changes in oil during the first day of a spill at the sea surface. Expected outcomes under other environmental conditions are discussed, as well as comparisons to other models.

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Allegre et al. recently presented new experimental data regarding the dependence of the streaming potential coupling coefficient with the saturation of the water phase. Such experiments are important to model the self-potential response associated with the flow of water in the vadose zone and the electroseismic/seismoelectric conversions in unsaturated porous media. However, the approach used to interpret the data is questionable and the conclusions reached by Allegre et al. likely incorrect

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Transcatheter arterial chemoembolization (TACE) offers a survival benefit to patients with intermediate hepatocellular carcinoma (HCC). A widely accepted TACE regimen includes administration of doxorubicin-oil emulsion followed by gelatine sponge-conventional TACE. Recently, a drug-eluting bead (DC Bead) has been developed to enhance tumor drug delivery and reduce systemic availability. This randomized trial compares conventional TACE (cTACE) with TACE with DC Bead for the treatment of cirrhotic patients with HCC. Two hundred twelve patients with Child-Pugh A/B cirrhosis and large and/or multinodular, unresectable, N0, M0 HCCs were randomized to receive TACE with DC Bead loaded with doxorubicin or cTACE with doxorubicin. Randomization was stratified according to Child-Pugh status (A/B), performance status (ECOG 0/1), bilobar disease (yes/no), and prior curative treatment (yes/no). The primary endpoint was tumor response (EASL) at 6 months following independent, blinded review of MRI studies. The drug-eluting bead group showed higher rates of complete response, objective response, and disease control compared with the cTACE group (27% vs. 22%, 52% vs. 44%, and 63% vs. 52%, respectively). The hypothesis of superiority was not met (one-sided P = 0.11). However, patients with Child-Pugh B, ECOG 1, bilobar disease, and recurrent disease showed a significant increase in objective response (P = 0.038) compared to cTACE. DC Bead was associated with improved tolerability, with a significant reduction in serious liver toxicity (P < 0.001) and a significantly lower rate of doxorubicin-related side effects (P = 0.0001). TACE with DC Bead and doxorubicin is safe and effective in the treatment of HCC and offers a benefit to patients with more advanced disease.

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Switzerland appears to be a privileged place to investigate the urban political ecology of tap water because of the specificities of its political culture and organization and the relative abundance of drinking water in the country. In this paper, we refer to a Foucauldian theorization of power that is increasingly employed in the social sciences, including in human geography and political ecology. We also implement a Foucauldian methodology. In particular, we propose an archaeo-genealogical analysis of discourse to apprehend the links between urban water and the forms of governmentality in Switzerland between 1850 and 1950. Results show that two forms of governmentality, namely biopower and neoliberal governmentality, were present in the water sector in the selected period. Nonetheless, they deviate from the models proposed by Foucault, as their periodization and the classification of the technologies of power related to them prove to be much more blurred than Foucault's work, mainly based on France, might have suggested.

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OBJECTIVE: To evaluate the relationship between changes in body bioelectrical impedance (BI) at 0.5, 50 and kHz and the changes in body weight, as an index of total body water changes, in acutely ill surgical patients during the rapid infusion of isotonic saline solution. DESIGN: Prospective clinical study. SETTING: Multidisciplinary surgical ICU in a university hospital. PATIENTS: Twelve male patients treated for acute surgical illness (multiple trauma n = 5, major surgery n = 7). Selection criteria: stable cardiovascular parameters, normal cardiac function, signs of hypovolemia (CVP < or = 5 mmHg, urine output < 1 ml/kg x h). INTERVENTIONS: After baseline measurements, a 60 min fluid challenge test was performed with normal saline solution, 0.25 ml/kg/min [corrected]. MEASUREMENTS AND RESULTS: Body weight (platform digital scale), total body impedance (four-surface electrode technique; measurements at 0.5, 50 and 100 kHz) and urine output. Fluid retention induced a progressive decrease in BI at 0.5, 50 and 100 kHz, but the changes were significant for BI 0.5 and BI 100 only, from 40 min after the beginning of the fluid therapy onwards. There was a significant negative correlation between changes in water retention and BI 0.5, with individual correlation coefficients ranging from -0.72 to 0.95 (p < 0.01-0.0001). The slopes of the regression lines indicated that for each kg of water change, there was a mean decrease in BI of 18 ohm, but a substantial inter-individual variability was noted. CONCLUSION: BI measured at low frequency can represent a valuable index of acute changes in body water in a group of surgical patients but not in a given individual.

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At seismic frequencies, wave-induced fluid flow is a major cause of P-wave attenuation in partially saturated porous rocks. Attenuation is of great importance for the oil industry in the interpretation of seismic field data. Here, the effects on P-wave attenuation resulting from changes in oil saturation are studied for media with coexisting water, oil, and gas. For that, creep experiments are numerically simulated by solving Biot's equations for consolidation of poroelastic media with the finite-element method. The experiments yield time-dependent stress?strain relations that are used to calculate the complex P-wave modulus from which frequency-dependent P-wave attenuation is determined. The models are layered media with periodically alternating triplets of layers. Models consisting of triplets of layers having randomly varying layer thicknesses are also considered. The layers in each triplet are fully saturated with water, oil, and gas. The layer saturated with water has lower porosity and permeability than the layers saturated with oil and gas. These models represent hydrocarbon reservoirs in which water is the wetting fluid preferentially saturating regions of lower porosity. The results from the numerical experiments showed that increasing oil saturation, connected to a decrease in gas saturation, resulted in a significant increase of attenuation at low frequencies (lower than 2 Hz). Furthermore, replacing the oil with water resulted in a distinguishable behavior of the frequency-dependent attenuation. These results imply that, according to the physical mechanism of wave-induced fluid flow, frequency-dependent attenuation in media saturated with water, oil, and gas is a potential indicator of oil saturation.

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Acid mine drainage (AMD) from the Zn-Pb(-Ag-Bi-Cu) deposit of Cerro de Pasco (Central Peru) and waste water from a Cu-extraction plant has been discharged since 1981 into Lake Yanamate, a natural lake with carbonate bedrock. The lake has developed a highly acidic pH of similar to 1. Mean lake water chemistry was characterized by 16,775 mg/L acidity as CaCO(3), 4330 mg/L Fe and 29,250 mg/L SO(4). Mean trace element concentrations were 86.8 mg/L Cu, 493 mg/L Zn, 2.9 mg/L Pb and 48 mg/L As, which did not differ greatly from the discharged AMD. Most elements showed increasing concentrations from the surface to the lake bottom at a maximal depth of 41 m (e.g. from 3581 to 5433 mg/L Fe and 25,609 to 35,959 mg/L SO(4)). The variations in the H and 0 isotope compositions and the element concentrations within the upper 10 m of the water column suggest mixing with recently discharged AMD, shallow groundwater and precipitation waters. Below 15 m a stagnant zone had developed. Gypsum (saturation index, SI similar to 0.25) and anglesite (SI similar to 0.1) were in equilibrium with lake water. Jarosite was oversaturated (SI similar to 1.7) in the upper part of the water column, resulting in downward settling and re-dissolution in the lower part of the water column (SI similar to -0.7). Accordingly, jarosite was only found in sediments from less than 7 m water depth. At the lake bottom, a layer of gel-like material (similar to 90 wt.% water) of pH similar to 1 with a total organic C content of up to 4.40 wet wt.% originated from the kerosene discharge of the Cu-extraction plant and had contaminant element concentrations similar to the lake water. Below the organic layer followed a layer of gypsum with pH 1.5, which overlaid the dissolving carbonate sediments of pH 5.3-7. In these two layers the contaminant elements were enriched compared to lake water in the sequence As < Pb approximate to Cu < Cd < Zn = Mn with increasing depth. This sequence of enrichment was explained by the following processes: (i) adsorption of As on Fe-hydroxides coating plant roots at low pH (up to 3326 mg/kg As), (ii) adsorption at increasing pH near the gypsum/calcite boundary (up to 1812 mg/kg Pb, 2531 mg/kg Cu. and 36 mg/kg Cd), and (iii) precipitation of carbonates (up to 5177 mg/kg Zn and 810 mg/kg Mn: all data corrected to a wet base). The infiltration rate was approximately equal to the discharge rate, thus gypsum and hydroxide precipitation had not resulted in complete clogging of the lake bedrocks. (C) 2010 Elsevier Ltd. All rights reserved.

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Natural environments are constantly challenged by the release of hydrophobic organic contaminants, which represent a threat for both the ecosystem and human health. Despite a substantial degradation by naturally occurring micro-organisms, a non negligible fraction of these pollutants tend to persist in soil and sediments due to their reduced accessibility to microbial degraders. This lack of 'bioavailability' is acknowledged as a key parameter for the natural and stimulated clean-up (bioremediation) of contaminated sites. We developed a bacterial bioreporter that responds to the presence of polyaromatic hydrocarbons (PAHs) by the production of the green fluorescent protein (GFP), based on the PAH-degrading bacterium Burkholderia sartisoli. We showed in this study that the bacterial biosensor B. sartisoli strain RP037 was faithfully reporting the degradation of naphthalene and phenanthrene (two PAHs of low molecular weight) via the production of GFP. What is more, the magnitude of GFP induction was influenced by change in the PAH flux triggered by a variety of physico-chemical parameters, such as the contact surface between the pollutant and the aqueous suspension. Further experiments permitted to test the influence of dissolved organic matter, which is an important component of natural habitats and can interact with organic pollutants. In addition, we tested the influence of two types of biosurfactants (tensio-active agents produced by living organisms) on phenanthrene's degradation by RP037. Interestingly, the surfactant's effects on the biodegradation rate appeared to depend on the type of biosurfactant and probably on the type of bacterial strain. Finally, we tagged B. sartisoli strain RP037 with a constitutively expressed mCherry fluorescent protein. The presence of mCherry allowed us to visualize the bacteria in complex samples even when GFP production was not induced. The new strain RP037-mChe embedded in a gel patch was used to detect PAH fluxes from a point source, such as a non-aqueous liquid or particles of contaminated soil. In parallel, we also developed and tested a so-called multiwell bacterial biosensor platform, which permitted the simultaneous use of four different reporter strains for the detection of major crude oil components (e.g., saturated hydrocarbons, mono- and polyaromatics) in aqueous samples. We specifically constructed the strain B. sartisoli RP007 (pPROBE-phn-luxAB) for the detection of naphthalene and phenanthrene. It was equipped with a reporter plasmid similar to the one in strain RP037, except that the gfp gene was replaced by the genes luxAB, which encoded the bacterial luciferase. The strain was implemented in the biosensor platform and detected an equivalent naphthalene concentration in oil spilled-sea water. We also cloned the gene for the transcriptional activator AlkS and the operator/promoter region of the operon alkSB1GHJ from the alkane-degrader bacterium Alcanivorax borkumensis strain SK2 in order to construct a new bacterial biosensor with higher sensitivity towards long-chain alkanes. However, the resulting strain showed no increased light emission in presence of tetradecane (C14), while it still efficiently reported low concentrations of octane (C8). RÉSUMÉ : Les écosystèmes naturels sont constamment exposés à nombre de contaminants organiques hydrophobes (COHs) d'origine industrielle, agricole ou même naturelle. Les COHs menacent à la fois l'environnement, le bien-être des espèces animales et végétales et la santé humaine, mais ils peuvent être dégradés par des micro-organismes tels que les bactéries et les champignons, qui peuvent être capables des les transformer en produits inoffensifs comme le gaz carbonique et l'eau. La biodégradation des COHs est cependant fréquemment limitée par leur pauvre disponibilité envers les organismes qui les dégradent. Ainsi, bien que la biodégradation opère partiellement, les COHs persistent dans l'environnement à de faibles concentrations qui potentiellement peuvent encore causer des effets toxiques chroniques. Puisque la plupart des COHs peuvent être métabolisés par l'activité microbienne, leur persistance a généralement pour origine des contraintes physico-chimiques plutôt que biologiques. Par exemple, leur solubilité dans l'eau très limitée réduit leur prise par des consommateurs potentiels. De plus, l'adsorption à la matière organique et la séquestration dans les micropores du sol participent à réduire leur disponibilité envers les microbes. Les processus de biodisponibilité, c'est-à-dire les processus qui gouvernent la dissolution et la prise de polluants par les organismes vivants, sont généralement perçus comme des paramètres clés pour la dépollution (bioremédiation) naturelle et stimulée des sites contaminés. Les hydrocarbures aromatiques polycycliques (HAPs) sont un modèle de COH produits par les activités aussi bien humaines que naturelles, et listés comme des contaminants chroniques de l'air, des sols et des sédiments. Ils peuvent être dégradés par un vaste nombre d'espèces bactériennes mais leur taux de biodégradation est souvent limité par les contraintes mentionnées ci-dessus. Afin de comprendre les processus de biodisponibilité pour les cellules bactériennes, nous avons décidé d'utiliser les bactéries elles-mêmes pour détecter et rapporter les flux de COH. Ceci a été réalisé par l'application d'une stratégie de conception visant à produire des bactéries `biocapteurs-rapporteurs', qui littéralement s'allument lorsqu'elles détectent un composé cible pour lequel elles ont été conçues. En premier lieu, nous nous sommes concentrés sur Burkholderia sartisoli (souche RP007), une bactérie isolée du sol et consommatrice de HAP .Cette souche a servi de base à la construction d'un circuit génétique permettant la formation de la protéine autofluorescente GFP dès que les cellules détectent le naphtalène ou le phénanthrène, deux HAP de faible masse moléculaire. En effet, nous avons pu montrer que la bactérie obtenue, la souche RP037 de B. sartisoli, produit une fluorescence GFP grandissante lors d'une exposition en culture liquide à du phénanthrène sous forme cristalline (0.5 mg par ml de milieu de culture). Nous avons découvert que pour une induction optimale il était nécessaire de fournir aux cellules une source additionnelle de carbone sous la forme d'acétate, ou sinon seul un nombre limité de cellules deviennent induites. Malgré cela, le phénanthrène a induit une réponse très hétérogène au sein de la population de cellules, avec quelques cellules pauvrement induites tandis que d'autres l'étaient très fortement. La raison de cette hétérogénéité extrême, même dans des cultures liquides mélangées, reste pour le moment incertaine. Plus important, nous avons pu montrer que l'amplitude de l'induction de GFP dépendait de paramètres physiques affectant le flux de phénanthrène aux cellules, tels que : la surface de contact entre le phénanthrène solide et la phase aqueuse ; l'ajout de surfactant ; le scellement de phénanthrène à l'intérieur de billes de polymères (Model Polymer Release System) ; la dissolution du phénanthrène dans un fluide gras immiscible à l'eau. Nous en avons conclu que la souche RP037 détecte convenablement des flux de phénantrène et nous avons proposé une relation entre le transfert de masse de phénanthrène et la production de GFP. Nous avons par la suite utilisé la souche afin d'examiner l'effet de plusieurs paramètres chimiques connus dans la littérature pour influencer la biodisponibilité des HAP. Premièrement, les acides humiques. Quelques rapports font état que la disponibilité des HAP pourrait être augmentée par la présence de matière organique dissoute. Nous avons mesuré l'induction de GFP comme fonction de l'exposition des cellules RP037 au phénanthrène ou au naphtalène en présence ou absence d'acides humiques dans la culture. Nous avons testé des concentrations d'acides humiques de 0.1 et 10 mg/L, tandis que le phénanthrène était ajouté via l'heptamethylnonane (HMN), un liquide non aqueux, ce qui au préalable avait produit le plus haut flux constant de phénanthrène aux cellules. De plus, nous avons utilisé des tests en phase gazeuse avec des concentrations d'acides humiques de 0.1, 10 et 1000 mg/L mais avec du naphtalène. Contrairement à ce que décrit la littérature, nos résultats ont indiqué que dans ces conditions l'expression de GFP en fonction de l'exposition au phénanthrène dans des cultures en croissance de la souche RP037 n'était pas modifiée par la présence d'acides humiques. D'un autre côté, le test en phase gazeuse avec du naphtalène a montré que 1000 mg/L d'acides humiques abaissent légèrement mais significativement la production de GFP dans les cellules de RP037. Nous avons conclu qu'il n'y a pas d'effet général des acides humiques sur la disponibilité des HAP pour les bactéries. Par la suite, nous nous sommes demandé si des biosurfactants modifieraient la disponibilité du phénanthrène pour les bactéries. Les surfactants sont souvent décrits dans la littérature comme des moyens d'accroître la biodisponibilité des COHs. Les surfactants sont des agents tensio-actifs qui augmentent la solubilité apparente de COH en les dissolvant à l'intérieur de micelles. Nous avons ainsi testé si des biosurfactants (des surfactants produits par des organismes vivants) peuvent être utilisé pour augmenter la biodisponibilité du phénanthrène pour la souche B. sartisoli RP037. Premièrement, nous avons tenté d'obtenir des biosurfactants produits par une autre bactérie vivant en co-culture avec les biocapteurs bactériens. Deuxièmement, nous avons utilisé des biosurfactants purifiés. La co-cultivation en présence de la bactérie productrice de lipopeptide Pseudomonas putida souche PCL1445 a augmenté l'expression de GFP induite par le phénanthrène chez B. sartisoli en comparaison des cultures simples, mais cet effet n'était pas significativement différent lorsque la souche RP037 était co-cultivée avec un mutant de P. putida ne produisant pas de lipopeptides. L'ajout de lipopeptides partiellement purifiés dans la culture de RP037 a résulté en une réduction de la tension de surface, mais n'a pas provoqué de changement dans l'expression de GFP. D'un autre côté, l'ajout d'une solution commerciale de rhamnolipides (un autre type de biosurfactants produits par Pseudomonas spp.) a facilité la dégradation du phénanthrène par la souche RP037 et induit une expression de GFP élevée dans une plus grande proportion de cellules. Nous avons ainsi conclu que les effets des biosurfactants sont mesurables à l'aide de la souche biocapteur, mais que ceux-ci sont dépendants du type de surfactant utilisé conjointement avec le phénanthrène. La question suivante que nous avons abordée était si les tests utilisant des biocapteurs peuvent être améliorés de manière à ce que les flux de HAP provenant de matériel contaminé soient détectés. Les tests en milieu liquide avec des échantillons de sol ne fournissant pas de mesures, et sachant que les concentrations de HAP dans l'eau sont en général extrêmement basses, nous avons conçu des tests de diffusion dans lesquels nous pouvons étudier l'induction par les HAPs en fonction de la distance aux cellules. Le biocapteur bactérien B. sartisoli souche RP037 a été marqué avec une seconde protéine fluorescente (mCherry), qui est constitutivement exprimée dans les cellules et leur confère une fluorescence rouge/rose. La souche résultante RP037-mChe témoigne d'une fluorescence rouge constitutive mais n'induit la fluorescence verte qu'en présence de naphtalène ou de phénanthrène. La présence d'un marqueur fluorescent constitutif nous permet de visualiser les biocapteurs bactériens plus facilement parmi des particules de sol. Un test de diffusion a été conçu en préparant un gel fait d'une suspension de cellules mélangées à 0.5 % d'agarose. Des bandes de gel de dimensions 0.5 x 2 cm x 1 mm ont été montées dans des chambres d'incubation et exposées à des sources de HAP (soit dissouts dans du HMN ou en tant que matériel solide, puis appliqués à une extrémité de la bande). En utilisant ce montage expérimental, le naphtalène ou le phénanthrène (dissouts dans du HMN à une concentration de 2.5 µg/µl) ont induit un gradient d'intensité de fluorescence GFP après 24 heures d'incubation, tandis que la fluorescence mCherry demeurait comparable. Un sol contaminé par des HAPs (provenant d'un ancien site de production de gaz) a induit la production de GFP à un niveau comparable à celui du naphtalène. Des biocapteurs bactériens individuels ont également détecté un flux de phénanthrène dans un gel contenant des particules de sol amendées avec 1 et 10 mg/g de phénanthrène. Ceci a montré que le test de diffusion peut être utilisé pour mesurer des flux de HAP provenant de matériel contaminé. D'un autre côté, la sensibilité est encore très basse pour plusieurs sols contaminés, et l'autofluorescence de certains échantillons rend difficile l'identification de la réponse de la GFP chez les cellules. Pour terminer, un des points majeurs de ce travail a été la production et la validation d'une plateforme multi-puits de biocapteurs bactériens, qui a permis l'emploi simultané de plusieurs souches différentes de biocapteurs pour la détection des constituants principaux du pétrole. Pour cela nous avons choisi les alcanes linéaires, les composés mono-aromatiques, les biphényls et les composés poly-aromatiques. De plus, nous avons utilisé un capteur pour la génotoxicité afin de détecter la `toxicité globale' dans des échantillons aqueux. Plusieurs efforts d'ingénierie ont été investis de manière à compléter ce set. En premier lieu, chaque souche a été équipée avec soit gfp, soit luxAB en tant que signal rapporteur. Deuxièmement, puisqu'aucune souche de biocapteur n'était disponible pour les HAP ou pour les alcanes à longues chaînes, nous avons spécifiquement construit deux nouveaux biocapteurs. L'un d'eux est également basé sur B. sartisoli RP007, que nous avons équipé avec le plasmide pPROBE-phn-luxAB pour la détection du naphtalène et du phénanthrène mais avec production de luciférase bactérienne. Un autre est un nouveau biocapteur bactérien pour les alcanes. Bien que nous possédions une souche Escherichia coli DHS α (pGEc74, pJAMA7) détectant les alcanes courts de manière satisfaisante, la présence des alcanes à longues chaînes n'était pas rapportée efficacement. Nous avons cloné le gène de l'activateur transcriptionnel A1kS ainsi que la région opérateur/promoteur de l'opéron alkSB1GHJ chez la bactérie dégradant les alcanes Alcanivorax borkumensis souche SK2, afin de construire un nouveau biocapteur bactérien bénéficiant d'une sensibilité accrue envers les alcanes à longues chaînes. Cependant, la souche résultante E. coli DHSα (pAlk3} n'a pas montré d'émission de lumière augmentée en présence de tétradécane (C14), tandis qu'elle rapportait toujours efficacement de basses concentrations d'octane (C8). De manière surprenante, l'utilisation de A. borkumensis en tant que souche hôte pour le nouveau plasmide rapporteur basé sur la GFP a totalement supprimé la sensibilité pour l'octane, tandis que la détection de tétradécane n'était pas accrue. Cet aspect devra être résolu dans de futurs travaux. Pour calibrer la plateforme de biocapteurs, nous avons simulé une fuite de pétrole en mer dans une bouteille en verre ouverte de 5L contenant 2L d'eau de mer contaminée avec 20 ml (1%) de pétrole brut. La phase aqueuse a été échantillonée à intervalles réguliers après la fuite durant une période allant jusqu'à une semaine tandis que les principaux contaminants pétroliers étaient mesurés via les biocapteurs. L'émission de bioluminescence a été mesurée de manière à déterminer la réponse des biocapteurs et une calibration intégrée faite avec des inducteurs types a servi à calculer des concentrations d'équivalents inducteurs dans l'échantillon. E. coli a été utilisée en tant que souche hôte pour la plupart des spécificités des biocapteurs, à l'exception de la détection du naphtalène et du phénanthrène pour lesquels nous avons utilisé B. sartisoli. Cette souche, cependant, peut être employée plus ou moins selon la même procédure. Il est intéressant de noter que le pétrole répandu a produit une apparition séquentielle de composés dissouts dans la phase aqueuse, ceux-ci .étant détectables par les biocapteurs. Ce profil contenait d'abord les alcanes à courtes chaînes et les BTEX (c'est-à dire benzène, toluène, éthylbenzène et xylènes), apparaissant entre des minutes et des heures après que le pétrole a été versé. Leurs concentrations aqueuses ont par la suite fortement décru dans l'eau échantillonnée après 24 heures, à cause de la volatilisation ou de la biodégradation. Après quelques jours d'incubation, ces composés sont devenus indétectables. Les HAPs, en revanche, sont apparus plus tard que les alcanes et les BTEX, et leur concentration a augmenté de pair avec un temps d'incubation prolongé. Aucun signal significatif n'a été mis en évidence avec le biocapteur pour le biphényl ou pour la génotoxicité. Ceci démontre l'utilité de ces biocapteurs, spécifiquement pour la détection des composés pétroliers, comprenant les alcanes à courtes chaînes, les BTEX et les HAPs légers.