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Dans l'étang de Berre, les apports excessifs en eau douce entraînent souvent des variations brusques de la salinité et des apports en azote parfois abondants. Les processus de régénération sédimentaire et d'élimination d'azote constituent des phénomènes majeurs pouvant expliquer le développement phytoplanctoniques et contrôler l'eutrophisation. L'étude de ces processus a été réalisée dans 2 stations ayant subi des historiques de variations de salinité différents. RDNA et anammox étaient négligeables. La dénitrification (couplée à la nitrification) serait le principal processus de sortie de N2 de l'étang. La forte production primaire pélagique utilisant l'ammonium a pu être expliquée par les processus de régénération, contrairement au nitrate dont la demande pélagique serait soutenue par des apports externes. Comme la salinité est susceptible d'influencer les processus d'azote, des microcosmes ont été utilisés afin d'évaluer la sensibilité de ces processus (résistance, résilience, shift) face aux variations à court terme de la salinité. Les 2 stations ont présenté des réponses différentes (dénitrification et nitrate réduction plus résilientes que la nitrification), suggérant que les stress halins à long terme influencent les réponses à court terme. Une hypothèse serait que la diversité et la structure des communautés joueraient un rôle crucial dans le maintien des taux d'activité. Dans cette étude, seule la communauté nitrifiante (AO) a été étudiée. Les AO et leurs transcrits étaient spécifiques aux sites et leurs abondances changeaient faiblement entre les microcosmes (résistance plus forte dans le site fréquemment soumis à des fluctuations de salinité). / The Berre lagoon receives excess freshwater leading to strong changes in the ecosystem salinity and in the nutrient inputs. Regeneration processes and the N2 removal of nitrogen are of a particular interest as they can explain the planktonic development and control the eutrophication state. These processes were studied in 2 stations with different patterns of long term stresses. DNRA and anammox were negligible. Denitrification (particularly the one coupled to nitrification) would be the main N2 removal in the lagoon. The high primary production based on N-NH4+ can be explained by the regeneration processes, while the primary production based on N-NO3- might be sustained by external inputs. As salinity susceptible to influence directly or indirectly the nitrogen processes, a microcosm approach was used in order to assess their sensitivity (resistance, resilience, shifts) to short term salinity fluctuations. Overall, towards the same kind of perturbations, the two stations responded differently (denitrification and nitrate reduction exhibited showed higher resilience than nitrification.), suggesting that long-term saline stresses would influence short-term responses. We suggest that the diversity and the structure of the communities would be crucial in their functional redundancy and thereby in the maintenance of the rates. In this study, we focused on the total structure of the nitrifying community (AO). AO and their transcripts were site-specific and their abundances changed slightly between microcosms (higher resistance in the site subject to frequent salinity fluctuations compared to the other site which is not affected by changes in the in situ salinity).

<div>Biosolids-based fertilizers are sold to the public to provide beneficial nutrients and organic matter for plant production. They are commonly applied to community gardens, municipal lands, reclamation projects, and golf courses. These fertilizers, however, may also contain a variety of trace organic contaminants, which can be persistent in the environment. Our work sought to quantify the persistence of biosolids contaminants in community garden soils. The commercial biosolids-based fertilizer, OCEANGRO®, was amended to two community garden soils to determine the first-order half-lives of four model contaminants: carbamazepine, miconazole, triclocarban, and triclosan. The criteria for their selection included biosolids occurrence, ecotoxicity, antimicrobial function, and knowledge gaps. Aerobic biosolids-amended soil microcosms were incubated at 22 ± 1 °C and approximately 80% field capacity. Sacrificial sampling occurred seven times over 180 days through multi-step solvent extractions. Detection and quantification were done on a high-performance liquid chromatograph tandem triple-quadrupole mass spectrometer. Results indicated that biosolids contaminants persist in soils with some having modeled half-lives in the hundreds of days. Additional analyses of solvent-spiked contaminant degradation and porewater desorption were performed to provide greater insight into possible limitations on resident biosolids contaminant degradation and to form a better comparative basis to previous literature. Solvent-spiked contaminants degraded more quickly than those resident within biosolids, which indicate that data using the former may underestimate persistence in real-world environments. The porewater analysis allowed for the desorption coefficient to be calculated for all four model resident contaminants. Disparities in the trends of these desorption coefficients and solvent-spiked degradation rates showed that desorption from the biosolids matrix may have been a limiting factor to resident degradation for only some of our four model contaminants. Nonetheless, the demonstrated persistence of these contaminants necessitates long-term thinking in relation to biosolids application. More work is needed on the potential hazards associated with biosolids use in public lands regarding ecotoxicity and antimicrobial resistance.</div>

Thesis (Ph. D.)--Miami University, Dept. of Botany, 2008. / Title from second page of PDF document. Includes bibliographical references (p. 86-88).

Le 7 août 2009, un pipeline transportant du pétrole brut s'est rompu, provoquant le déversement de 5100 m3 de brut sur 5 hectares de la Réserve Naturelle des Coussouls de Crau. Le pétrole a atteint l'aquifère et a formé un LNAPL qui alimente un panache de polluants dissous, dont le benzène, composé cible car toxique. Cette étude vise à montrer que la biodégradation du pétrole (biostimulation ou atténuation naturelle), en particulier des composés dissous, est une mesure efficace de gestion à long terme des risques pour la ressource en eau. Une première étude en microcosmes a montré la biodégradation, même dans les conditions les plus réductrices, des composés cibles dont le benzène. Cette étude a confirmé que la disponibilité en oxydant est un facteur limitant et que le phosphate est un levier puissant pour stimuler la croissance bactérienne. Une seconde étude sur site a prouvé la faisabilité de la biostimulation par injection de nitrate et de phosphate dans la nappe et son efficacité pour l'abattement des concentrations en polluants dissous. L'utilisation du radon comme traceur pour estimer la saturation en pétrole dans l'aquifère a été évaluée dans une troisième étude. La facilité de mise en oeuvre de la méthode ainsi que les résultats offrent des perspectives intéressantes pour l'optimisation des systèmes de pompage-écrémage sur des sites ayant un NAPL. Une dernière étude portant sur la mise en place des processus d'oxydoréduction et de dégradation sur site a montré une évolution rapide des conditions après l'accident, traduisant un environnement favorable à l'atténuation naturelle. La dégradation in situ du benzène a été mise en évidence via des mesures isotopiques. / On August 7, 2009 a pipeline transporting crude oil broke in the heart of the Nature Reserve of Coussouls de Crau, and 5,100 m3 of oil were spilled over 5 hectares. Oil infiltrated through the subsurface and reached the most important regional aquifer where it formed a LNAPL that created a plume of dissolved compounds. Among these compounds, benzene is of particular concern because of its toxicity and high solubility. This thesis aims at showing that biodegradation of crude oil, especially of dissolved compounds, is a good option for long-term management of risks for the water resource. A first study in microcosms demonstrated biodegradation of targeted compounds, including benzene, even under the most reducing conditions. This study also revealed that the availability of electrons acceptors was a limiting factor and that phosphate was a powerful lever to stimulate bacterial growth. An on-site study proved the feasibility of biostimulation by nitrate and phosphate injection in the aquifer and showed that biostimulation was efficient to reduce concentrations of dissolved compounds. Naturally occurring radon was used as a tracer to estimate oil saturation in the saturated zone in a third study. The ease of implementation of this method and the results offer interesting perspectives to optimize the yield of pump-and-skim systems in LNAPL-contaminated sites. The last study focused on the implementation of redox processes and degradation in the saturated zone after the spill. This study showed that processes quickly evolved and that conditions were favorable to natural attenuation. In situ benzene degradation was proven by the measurements of stable isotopes of carbon.

Species diversity may simultaneously be a cause and a consequence of variability in population, community and ecosystem properties. Ecology has traditionally focused on elucidating the causes of biodiversity. However, in the last decade and a half ecologists have asked the opposite question: What are the consequences of species diversity? The majority of these studies elucidated the effects of species diversity within single trophic levels. Incorporating trophic complexity is the next step in this research program. In this dissertation I investigated the causes of resource species diversity, as well as the impacts that resource diversity has on rates of consumption and the stability of population, community and ecosystem properties over time in planktonic food webs. The high diversity of phytoplankton found in nature appears to defy the competitive exclusion principle, and elucidating the mechanisms which maintain this diversity continues to be a challenge. In general, variability in limiting factors is required to maintain non-neutral species diversity, but this variability can be generated by forces outside of the competitive community (i.e. exogenous), or may be the outcome of competitive interactions themselves (i.e. endogenous). Using microcosm experiments, I showed that endogenously generated variability in limiting factors was more effective at maintaining phytoplankton species diversity over the long-term, although the strength of this effect depended on the composition of the phytoplankton community. Existing resource diversity has been proposed to generally weaken consumer-resource interaction strengths and limit consumer control of resource biomass. This is because more diverse resource communities are more likely to contain inedible, unpalatable, toxic or non-nutritious species. However, when resource communities contain multiple palatable species, diversity may also accelerate consumption. Using grazing experiments with multiple zooplankton consumer species, I found that the mechanism, direction and magnitude of modulation of consumption depended on the feeding selectivity of the consumer and the composition of the resource community. By altering consumer-resource interaction strengths in the short-term, resource species diversity may impact the stability of consumer-resource dynamics in the long-term. In separate microcosm experiments, I investigated the influence of resource species diversity, community composition and consumer feeding selectivity on population, community, and ecosystem properties over time. Diversity had positive effects on phytoplankton population biomass, resource community biomass, the rate of photosynthesis, the standing stock of particulate nutrients, and the generalist consumer’s population density. It also stabilized resource community biomass and the stocks of particulate nutrients over time. Unexpectedly, diversity did not stabilize either of the consumer populations, regardless of feeding selectivity. This suggests that effects of diversity on resource community properties do not impact consumer dynamics linearly. Resource community composition was generally more important than resource species diversity in determining food web properties. The importance of community composition in determining both the causes and consequences of resource diversity in these experiments points to the importance of species’ traits and the outcomes of their interactions. I suggest that the use of complex adaptive systems theory and trait-based approaches in the future will allow a consideration of the feedbacks between the causes and consequences of species diversity in food webs. / Graduate

This diploma thesis has been carried out as a part of the project Utilization of long term (passive) sampling methods combined with in situ microcosms for assessment of (bio)degradation potential (PASSES). In the frame of the project groundwater remediation took place in the premises of Farmak a.s. in Olomouc using a pilot photooxidation unit and efficiency of the remediation was monitored through passive and active sampling methods. Pilot photooxidation unit is a technology based on the H2O2/UV-C photochemical oxidation of organic pollutants. In this work optimization tests of the pilot photooxidation unit were performed. The residence time of the groundwater in the photoreactors, required for its sufficient decontamination from pharmaceuticals and aromatic hydrocarbons, was 2.5 hours. 91% degradation of the pharmaceuticals and 80% degradation of aromatic hydrocarbons were reached during this interval. Although the removal efficiency of the pharmaceuticals by the photooxidation unit was high, the pilot photooxidation unit was not able to effectively remove the pharmaceuticals at the studied locality. By comparing the results of the pharmaceuticals from active and passive groundwater sampling during the remediation attempt, passive Polar Organic Chemical Integrative Sampler (POCIS) was found to be...

Ces travaux s’inscrivent dans une problématique actuelle de compréhension des effets, encore peu connus, des mélanges de pesticides dans le sol. Les formulations d’herbicides S-métolachlore (Dual Gold Safeneur®), mésotrione (Callisto®) et nicosulfuron (Milagro®) ont été appliquées en mélanges et à la dose agronomique recommandée. Les molécules formulées sont plus toxiques que les molécules actives seules (Microtox®) et aucun effet synergique ou antagoniste des mélanges n’a été observé. Cependant, ces mélanges impactent transitoirement et à court terme les communautés microbiennes du sol de Limagne, sans modifier les paramètres généraux de structure et d’abondance. Toutefois, des effets ont été mis en évidence sur des communautés sensibles telles que les phototrophes ou celles impliquées dans les processus de nitrification et de dénitrification. De plus, une comparaison des effets des mélanges sur les communautés phototrophes de deux sols souligne l’importante toxicité du Dual Gold Safeneur® et remet en cause son utilisation d’un point de vue écotoxicologique. / These experiments are part of the actual problematic of understanding the poorknown effects of pesticides mixtures in soil ecosystem. The herbicidal commercial formulations of S-metolachlor (Dual Gold Safeneur®), mesotrione (Callisto®) and nicosulfuron (Milagro®) were applied in mixtures at the recommended field rate. Formulated compounds are more toxic than active ingredients alone (Microtox®) and no synergistic or antagonistic effects were recorded. However, these mixtures impaired rapidly and transitory the Limagne soil microbial communities, without modifying the global parameters of structure and abundance. Effects were also recorded on sensitive communities, such as phototrophic, nitrifying and denitrifying communities. A comparison of mixtures effects on phototrophic communities from two soils underlined the high toxicity of Dual Gold Safeneur® and challenged its use from an ecotoxicological point of view..

L’objectif de ce travail de thèse vise à analyser les effets de quelques pesticides et d’un adjuvant sur des organismes marins, représentatifs de quatre niveaux trophiques, à savoir des micro-algues, un échinoderme, des bivalves et un poisson. L’analyse de la pollu-sensibilité est basée sur l’utilisation de différents bio-essais existants ou adaptés au contexte de cette étude.Les tests de toxicité ont permis d’évaluer la sensibilité de trois espèces phytoplanctoniques (Chaetoceros calcitrans, Isochrysis aff. Galbana et Tetraselmis suecica) vis-à-vis d’un fongicide l’époxiconazole (pur et en formulation commerciale Opus) et de l’adjuvant nonylphénol. D’une manière générale, la croissance de C. calcitrans et I. aff. Galbana s’avère plus sensible à l’action des contaminants étudiés. Ainsi, en utilisant pour C. calcitrans un milieu reproduisant les conditions naturelles du Golfe de Gabès, des valeurs de CE50 de 2 ,31 mg/L et 2,9 μg/l sont obtenues respectivement avec la substance active époxiconazole, et le produit formulé. Ces résultats montrent l’importance des adjuvants dans la toxicité et que les micro-algues peuvent être sensibles aux effets non-cibles d’un fongicide triazole.En outre, l’âge des cellules, les conditions d’éclairement et de composition des milieux de culture induisent des changements de sensibilité au fongicide, suggérant que la densité cellulaire est un paramètre important dans les tests de toxicité.L’analyse de quelques paramètres physiologiques montre que les contaminants utilisés induisent une augmentation du volume cellulaire, des échanges gazeux, de la teneur en pigments et en ATP. Il apparaît ainsi que les toxiques utilisés réduisent la vitesse de croissance, prolongeant le cycle cellulaire, sans affecter la production de nouveaux matériaux, nécessaires à la construction de nouvelles cellules.Par ailleurs, une étude réalisée en microcosmes lors d’un bloom de l’algue toxique Karenia selliformis dans le golfe de Gabès, montre que les différents contaminants chimiques (époxiconazole, chlorpyriphos-éthyl, nonylphénol) produisent des modifications drastiques de la structure des communautés phytoplanctoniques, fonction de la nature et de la concentration du contaminant.La toxicité des différents contaminants a été étudiée sur des animaux marins, aux stades embryo-larvaire (oursin, huître, palourde), métamorphose des larves (palourde) et survie des larves (turbot). Les résultats montrent que les larves du turbot sont les plus sensibles à l’action des contaminants avec des CE50 allant de 2,78 à 492 μg/L selon le toxique et que chez la palourde, la métamorphose est le stade le plus sensible parmi les trois stades de développement étudiés. Les contaminants utilisés produisent des anomalies du développement et des malformations embryonnaires qui peuvent induire une réduction de la production naturelle en agissant i) directement sur le développement embryo-larvaire et ii) indirectement sur la qualité et la biodisponibilité de l’aliment à travers la variation de la biomasse phytoplanctonique. Ces résultats soulignent la nécessité d’appliquer les toxiques à différents organismes marins présentant des organisations différentes pour apprécier pleinement leur impact. / This work aims to study the effects of a few pesticides and one adjuvant on marine organisms, representatives of four trophic levels : micro-algae, echinoderm, bivalves and fish. Analysis of the pollu-sensitivity was based on the utilisation of existing bio-assays or adapted to this study.Phytotoxic assessments were conducted on three phytoplanktonic species (Chaetoceros calcitrans, Isochrysis aff. Galbana et Tetraselmis suecica) using the fungicide epoxiconazole and the adjuvant nonylphenol. Sensitivity to these toxicants of C. calcitrans and I. aff. Galbana was high. Thus, when C. calcitrans was grown in a medium simulating pre-winter conditions in Gabès Gulf, EC50 values were respectively, 2.31 mg/L and 2.9 μg/L for epoxiconazole active ingredient and epoxiconazole-formulated. These results questioned the use of ecotoxicological data obtained solely using active molecules of pesticides rather the complete formulation and show that non-target micro-algae may be affected by a triazole fungicide.Moreover, cell age, light and nutrient composition induced changes in epoxiconazole sensitivity, suggesting that cellular density is an important parameter in toxicity tests.Analysis of a few physiological parameters show that contaminants used in this study induce an increase of pigment content, ATP synthesis, and rates of oxygen exchanges while the cell volume enlarges. Consequently, the toxicants might reduce the growth rate, by a prolongation of the cell cycle without affecting the production of new material for the construction of new cells.Bioassays were conducted using microcosms during a bloom of the toxic algae Karenia selliformis in the Gulf of Gabès. The different toxicants (epoxiconazole, chlorpyrifos-éthyl, nonyphenol) produced drastic changes in the phytoplankton communities, depending on the type and concentration of the contaminant.Phytotoxic assessments were conducted on marine animal models, using different developmental stages: embryo-larval development (sea urchin, oyster, and clam), metamorphosis larvae (clam) and larvae survival (turbot). Results show that turbot larvae are most sensitive to the action of contaminants with EC50 values ranging from 2.78 to 492 μg/L depending on the toxic and that the metamorphosis is the stage the most sensitive of the three stages of development of clam studied.The pollutants produced developmental and embryonic abnormalities that might induce a reduction in the natural production by acting i) directly on the development of the marine organisms and ii) indirectly on the quality and bioavailability of food through the variation of phytoplankton biomass.These results underline the need to study pollutant effects on marine organisms having different organizations to evaluate their full impact.