Desenvolvimento de novos biolubrificantes hidráulicos derivados dos óleos de maracujá e de moringa in natura e epoxidados

With the increasing environmental awareness, maximizing biodegradability and minimizing ecotoxicity is the main driving force for new technological developments. Thus, can be developed new biodegradable lubricants for use in environmentally sensitive areas. The aim of this study was to obtain new bio-lubricants from passion fruit (Passiflora edulis Sims f. flavicarpa Degener) and moringa (Moringa oleifera Lamarck) epoxidized oils and develop a new additive package using experimental design for their use as a hydraulic fluid. In the first stage of this work was performed the optimization of the epoxidation process of the oils using fractional experimental design 24-1 , varying the temperature, reaction time, ratio of formic acid and hydrogen peroxide. In the second step was investigated the selectivity, thermodynamics and kinetics of the reaction for obtaining the two epoxides at 30, 50 and 70 °C. The result of the experimental design confirmed that the epoxidation of passion fruit oil requires 2 hours of reaction, 50 °C and a ratio H2O2/C=C/HCOOH (1:1:1). For moringa oil were required 2 hours reaction, 50 °C and a ratio of H2O2/C=C/HCOOH (1:1:1.5). The results of the final conversions were equal to 83.09% (± 0.3) for passion fruit oil epoxide and 91.02 (±0,4) for moringa oil epoxide. Following was made the 23 factorial design to evaluate which are the best concentrations of corrosion inhibitor and anti-wear (IC), antioxidant (BHA) and extreme pressure (EP) additives. The bio-lubricants obtained in this step were characterized according to DIN 51524 (Part 2 HLP) and DIN 51517 (Part 3 CLP) standards. The epoxidation process of the oils was able to improve the oxidative stability and reduce the total acid number, when compared to the in natura oils. Moreover, the epoxidized oils best solubilized additives, resulting in increased performance as a lubricant. In terms of physicochemical performance, the best lubricant fluid was the epoxidized moringa oil with additives (EMO-ADI), followed by the epoxidized passion fruit oil with additives (EPF-ADI) and, finally, the passion fruit in natura oil without additives (PFO). Lastly, was made the investigation of the tribological behavior under conditions of boundary lubrication for these lubricants. The tribological performance of the developed lubricants was analyzed on a HFRR equipment (High Frequency Reciprocating Rig) and the coefficient of friction, which occurs during the contact and the formation of the lubricating film, was measured. The wear was evaluated through optical microscopy and scanning electron microscopy (SEM). The results showed that the addition of extreme pressure (EP) and anti-wear and corrosion inhibitor (CI) additives significantly improve the tribological properties of the fluids. In all assays, was formed a lubricating film that is responsible for reducing the coefficient of metal-to-metal wear. It was observed that the addition of EP and IC additives in the in natura vegetable oils of passion fruit and moringa did not favor a significant reduction in wear. The bio-lubricants developed from passion fruit and moringa oils modified via epoxidation presented satisfactory tribological properties and shown to be potential lubricants for replacement of commercial mineral-based fluids.

Immunostimulatory effects of different aspects of aquaculture on the host response in the edible sea urchin, paracentrotus lividus

Aquaculture is a fast-growing industry contributing to global food security and sustainable aquaculture, which may reduce pressures on capture fisheries. The overall objective of this thesis was to look at the immunostimulatory effects of different aspects of aquaculture on the host response of the edible sea urchin, Paracentrotus lividus, which are a prized delicacy (roe) in many Asian and Mediterranean countries. In Chapter 1, the importance of understanding the biology, ecology, and physiology of P. lividus, as well as the current status in the culture of this organism for mass production and introducing the thesis objectives for following chapters is discussed. As the research commenced, the difficulties of identifying individuals for repeat sampling became clear; therefore, Chapter 2 was a tagging experiment that indicated PIT tagging was a successful way of identifying individual sea urchins over time with a high tag retention rate. However, it was also found that repeat sampling via syringe to measure host response of an individual caused stress which masked results and thus animals would be sampled and sacrificed going forward. Additionally, from personal observations and discussion with peers, it was suggested to look at the effect that diet has on sea urchin immune function and the parameters I measured which led to Chapter 3. In this chapter, both Laminaria digitata and Mytilus edulis were shown to influence measured immune parameters of differential cell counts, nitric oxide production, and lysozyme activity. Therefore, trials commencing after Trial 5 in Chapter 4, were modified to include starvation in order to remove any effect of diet. Another important aspect of culturing any organism is the study of their immune function and its response to several immunostimulatory agents (Chapter 4). Zymosan A was shown to be an effective immunostimulatory agent in P. lividus. Further work on handled/stored animals (Chapter 5) showed Zymosan A reduced the measured levels of some immune parameters measured relative to the control, which may reduce the amount of stress in the animals. In Chapter 6, animals were infected with Vibrio anguillarum and, although V. anguillarum, impacted immune parameters of P. lividus, it did not cause mortality as predicted. Lastly, throughout this thesis work, it was noted that the immune parameters measured produced different values at different times of the year (Chapter 7); therefore, using collated baseline (control) data, results were compiled to observe seasonal effects. It was determined that both seasonality and sourcing sites influenced immune parameter measurements taken at different times throughout the year. In conclusion, this thesis work fits into the framework of development of aquaculture practices that affect immune function of the host and future research focusing on the edible sea urchin, P. lividus.

Impacts of seawater acidification on mantle gene expression patterns of the Baltic Sea blue mussel: implications for shell formation and energy metabolism, link to supplementary material

Marine organisms have to cope with increasing CO2 partial pressures and decreasing pH in the oceans. We elucidated the impacts of an 8-week acclimation period to four seawater pCO2 treatments (39, 113, 243 and 405 Pa/385, 1,120, 2,400 and 4,000 µatm) on mantle gene expression patterns in the blue mussel Mytilus edulis from the Baltic Sea. Based on the M. edulis mantle tissue transcriptome, the expression of several genes involved in metabolism, calcification and stress responses was assessed in the outer (marginal and pallial zone) and the inner mantle tissues (central zone) using quantitative real-time PCR. The expression of genes involved in energy and protein metabolism (F-ATPase, hexokinase and elongation factor alpha) was strongly affected by acclimation to moderately elevated CO2 partial pressures. Expression of a chitinase, potentially important for the calcification process, was strongly depressed (maximum ninefold), correlating with a linear decrease in shell growth observed in the experimental animals. Interestingly, shell matrix protein candidate genes were less affected by CO2 in both tissues. A compensatory process toward enhanced shell protection is indicated by a massive increase in the expression of tyrosinase, a gene involved in periostracum formation (maximum 220-fold). Using correlation matrices and a force-directed layout network graph, we were able to uncover possible underlying regulatory networks and the connections between different pathways, thereby providing a molecular basis of observed changes in animal physiology in response to ocean acidification.

(Table 3, Page 417) Table 3. The concentrations of Zn, Cu, Pb, Cd, Ni, Co, Ag, Mn and Fe in a soluble in 1M HCl fraction of ferromanganese nodules of Slupsk Furrow in the southern Baltic sea

The concentration of Zn, Cu, Pb, Cd, Ni, Co, Ag, Mn, Fe, Ca, Mg, K and Na in molluscs Macoma balthica, Mya arenaria, Cardium glaucum, Mytilus edulis and Astarte borealis from the southern Baltic was determined. The surface sediments and ferromanganese concretions associated with the molluscs were also analysed for concentration of these metals. Species- and region-dependent differences in the metal levels of the organisms were observed. The properties of molluscs analysed which have a tendency toward elevated biological tolerance of selected trace metals were specified. The interelement relationship between metal concentrations in the soft tissue and the shell was estimated and was discussed.

The influence of mussel-modified habitat on Fucus serratus L. a rocky intertidal canopy-forming macroalga

The influence of habitat modification by Mytilus edulis L. on the settlement and development of Fucus serratus populations was investigated on rocky shores of the Isle of Anglesey, North Wales. Settlement of fucoids was higher inside mussel habitat than outside on one of two shores studied. The effect of microhabitat on survival of fucoid germlings was examined by transplanting the germlings into and outside mussel habitats, each with and without the exclusion of grazers. Observation showed that periwinkles and top shells were abundant in mussel habitat, while limpets dominated bare rock. Exclusion of grazers greatly enhanced the survival of fucoid germlings in both habitats, indicating that while mussel habitat supports a different grazer assemblage to bare rock, both assemblages are important in limiting fucoid recruitment. The risk of dislodgement was assessed and compared between fucoids growing on mussel shells and bare rock. In situ pull-tests showed that less force was required to detach large fertile thalli growing on mussel shells than those growing on the rock. Adhesion was generally broken between the mussel and the rock rather than between the holdfast and the mussel. These observations indicate that mussels provide an unstable substrate for mature fucoids. Overall results suggest that a negative effect of mussel-modified habitat on fucoids is profound in adults; but the effect is context-dependent in juveniles and can be positive at settlement. Results from a survey on population structure of fucoids across two shores showed that there were greater numbers of large fertile fucoids growing directly attached to rock than on mussel shells, while there was no difference for juvenile fucoids confirming the experimental results. Moreover thalli larger than 60 cm were found only on the rock but not on shells. This finding suggests that a mussel dominated habitat may have a significant impact on reproductive output in fucoid populations.

The influence of mussel-modified habitat on Fucus serratus L. a rocky intertidal canopy-forming macroalga

The influence of habitat modification by Mytilus edulis L. on the settlement and development of Fucus serratus populations was investigated on rocky shores of the Isle of Anglesey, North Wales. Settlement of fucoids was higher inside mussel habitat than outside on one of two shores studied. The effect of microhabitat on survival of fucoid germlings was examined by transplanting the germlings into and outside mussel habitats, each with and without the exclusion of grazers. Observation showed that periwinkles and top shells were abundant in mussel habitat, while limpets dominated bare rock. Exclusion of grazers greatly enhanced the survival of fucoid germlings in both habitats, indicating that while mussel habitat supports a different grazer assemblage to bare rock, both assemblages are important in limiting fucoid recruitment. The risk of dislodgement was assessed and compared between fucoids growing on mussel shells and bare rock. In situ pull-tests showed that less force was required to detach large fertile thalli growing on mussel shells than those growing on the rock. Adhesion was generally broken between the mussel and the rock rather than between the holdfast and the mussel. These observations indicate that mussels provide an unstable substrate for mature fucoids. Overall results suggest that a negative effect of mussel-modified habitat on fucoids is profound in adults; but the effect is context-dependent in juveniles and can be positive at settlement. Results from a survey on population structure of fucoids across two shores showed that there were greater numbers of large fertile fucoids growing directly attached to rock than on mussel shells, while there was no difference for juvenile fucoids confirming the experimental results. Moreover thalli larger than 60 cm were found only on the rock but not on shells. This finding suggests that a mussel dominated habitat may have a significant impact on reproductive output in fucoid populations.

Benthic assemblages associated with native and non-native oysters are similar

Invasive species can impact native species and alter assemblage structure, which affects associated ecosystem functioning. The pervasive Pacific oyster, Crassostrea gigas, has been shown to affect the diversity and composition of many host ecosystems. We tested for effects of the presence of the invasive C. gigas on native assemblages by comparing them directly to assemblages associated with the declining native European oyster, Ostrea edulis. The presence of both oyster species was manipulated in intertidal and subtidal habitats and reefs were constructed at horizontal and vertical orientation to the substratum. After 12 months, species diversity and benthic assemblage structure between assemblages with C. gigas and O. edulis were similar, but differed between habitats and orientation, suggesting that both oyster species were functionally similar in terms of biodiversity facilitation. These findings support evidence, that non-native species could play an important role in maintaining biodiversity in systems with declining populations of native species.

Apport d'un programme de génétique à une filière de production aquacole : l'exemple de l'ostréiculture

Two oyster species are currently present along the French coasts : the indigenous European flat oyster (Ostrea edulis), and the Pacific cupped oyster (Crassostrea gigas), that has been introduced from Japan since the beginning of the 70ies. The flat oyster successively suffered from two protozoan diseases during the 60ies and its production decreased from 20 000 tons/year by that time to 1 500 tons/year nowadays. Consequently, the oyster production is principally (99%) based upon the Pacific oyster species with approximately 150 000 tons/year among which 90% are grown from the natural spat. However, the hatchery production of this species is developing and was estimated to 400 to 800 millions spat in 2002. Moreover, strengthened relationships between IFREMER and the 5 commercial hatcheries, that all joined the SYSAAF (Union of the French poultry, shellfish and fish farming selectors), allow to plan for new genetic breeding programs. At the end of the 80ies, IFREMER initiated a genetic breeding program for the resistance of the European flat oyster to the bonamiosis, and obtained strains more tolerant to this disease. After two generations of massal selection, molecular markers had identified a reduced genetic basis in this program. It was then reoriented to an intra-familial selection. However, we were confronted to a zootechnic problem to manage such a scheme and we compromised by an intra-cohorts of families selection scheme managed using molecular markers. The program has now reached the transfer level with experimentation at a professional scale. Concerning the Pacific cupped oyster, and in parallel with the obtaining and the study of polyploids, performance of different Asian cupped oyster strains were compared to the one introduced in France thirty years ago and currently suffering from summer mortalities. The local strain exhibited better performance, certainly based upon a good local adaptation. In other respects, although early growth is a relevant criteria for selection for growth to commercial stage, it is not to be privileged in the context of an oyster producing region with a limited food availability. Contrary, the spat summer mortality became a priority for numerous teams (genetic, physiology, pathology, ecology,...) joined in the MOREST program. The first results showed important survival differences between fullsib and halsib families. They indicate a genetic determinism to this character "survival" and promote for its selection.

Can survival of European flat oysters following experimental infection with Bonamia ostreae be predicted using QTLs?

The present study identifies quantitative trait loci (QTLs) in response to an experimental infection with the parasite responsible for bonamiosis, Bonamia ostreae, in two segregating families of the European flat oyster, Ostrea edulis. We first constructed a genetic-linkage map for each studied family and improved the existing genetic-linkage map for the European flat oyster with a set of SNP markers. This latter map now combines the best accuracy and the best estimate of the genome coverage available for an oyster species. Secondly, by comparing the QTLs detected in this study with those previously published for O. edulis in similar experimental conditions, we identified several potential QTLs that were identical between the different families, and also new specific QTLs. We also detected, within the confidence interval of several QTL regions, some previously predicted candidate genes differentially expressed during an infection with B. ostreae, providing new candidate genome regions which should now be studied more specifically.

Climate Change Influences Carrying Capacity in a Coastal Embayment Dedicated to Shellfish Aquaculture

A spatially explicit coupled hydrodynamic-biogeochemical model was developed to study a coastal ecosystem under the combined effects of mussel aquaculture, nutrient loading and climate change. The model was applied to St Peter's Bay (SPB), Prince Edward Island, Eastern Canada. Approximately 40 % of the SPB area is dedicated to mussel (Mytilus edulis) longline culture. Results indicate that the two main food sources for mussels, phytoplankton and organic detritus, are most depleted in the central part of the embayment. Results also suggest that the system is near its ultimate capacity, a state where the energy cycle is restricted to nitrogen-phytoplankton-detritus-mussels with few resources left to be transferred to higher trophic levels. Annually, mussel meat harvesting extracts nitrogen (N) resources equivalent to 42 % of river inputs or 46.5 % of the net phytoplankton primary production. Under such extractive pressure, the phytoplankton biomass is being curtailed to 1980's levels when aquaculture was not yet developed and N loading was half the present level. Current mussel stocks also decrease bay-scale sedimentation rates by 14 %. Finally, a climate change scenario (year 2050) predicted a 30 % increase in mussel production, largely driven by more efficient utilization of the phytoplankton spring bloom. However, the predicted elevated summer temperatures (> 25 A degrees C) may also have deleterious physiological effects on mussels and possibly increase summer mortality levels. In conclusion, cultivated bivalves may play an important role in remediating the negative impacts of land-derived nutrient loading. Climate change may lead to increases in production and ecological carrying capacity as long as the cultivated species can tolerate warmer summer conditions.

Site n°5. The Pertuis Breton (Bay of Biscay) France

1.This report presents the results of a field study conducted in the ECASA test site nOS in the Pertuis Breton, France. The site is located on the Atlantic West coasts. It is open to the bay of Biscay, but is slightly protected against westerly winds. The bay has been exploited by intertidal mussels culture for centuries. 2. Within the bay, mussels (Mytilus edulis) are cultivated either by the traditional pole technique, around the bay or on longlines in the centre of the bay. The area occupied by these longline s represents 250 ha, and the resulting annual production is 1 000 tonnes of mussels. The average depth at mid tide is of 13.8 m. The sediment is sandy, with a small fraction of mud. 3. The site is subject to several regular monitoring through the local implementation of national networks aiming at protecting the environment and marine resources, on pollutants (RNO), microbiological quality of the waters (REMI), phytoplanktonic toxic species (REPHY) and growth and mortality of molluscs (REMORA). Benthic macrofauna was studied in 1976. 4. Five sampling sations were chosen along a line, starting under the longlines, and at distances of 50, 100, 200, and 400 metres from the area cultivated. A reference station was chosen in a different direction at 2300 metres of the cultivated area. Sampling methods are described in the text. _Sediments were sampled for different analyses: grain size, content in organic matter, total organic carbon and nitrogen, and phytic pigments (chlorophyll a and phaeopigments). Redox were measured in cores. The macrofauna living into the sediment was also sampled. The water column was sampled for physical (temperature, transparency) and chemical parametres, including oxygen content, salinity, organic matter, dissolved nitrogen forms, phosphates and silicates. Results from benthic macrofauna surveys indicate that there were no significant differences between the different stations and the reference station, all being classified as slightly disturbed. The bay is submitted to freshwater runoffs from two adjacent rivers. 7. The sediment is slightly modified by the culture of bivalves. Total organic carbon, total nitrogen, Eh values and pheopigments were significantly higher under the trestles than in any other stations. Other stations often did not differ from the reference station. 8. The effects of shellfish culture on the water column were. However, it was observed a small decrease of the food available to the molluscs near the rearing 9. The DEB model was able to describe and predict adequately the growth of oysters, both in the Baie des Veys and in the Loch Creran. The parametres for its use in other environment are given, but a tuning of one parametre should be performed with the help of authors. 10. Among the indicators and models for use in are as of intertidal bivalve culture, it is recommended to use the sediment quality index, TOC (Total Organic Carbon), redox and pheopigments, in surficial sediment, AMBI for the macrofauna, chlorophyll a contents and nitrogen forms in the water column, and models describing the carrying capacity, filtration rate of molluscs, and a DEB model to predict the growth of molluscs.

Bilan 2015 du dispositif national de surveillance de la santé des mollusques marins

Depuis 1992, la surveillance de la santé des mollusques marins du littoral français est assurée par le réseau de Pathologie des Mollusques (Repamo). Ses activités s’inscrivent dans le cadre de la Directive Européenne 2006/88/CE. Depuis son évaluation par la plateforme nationale d’épidémiosurveillance en santé animale en 2012, l’objectif de surveillance est la détection précoce des infections dues à des organismes pathogènes exotiques et émergents affectant les mollusques marins sauvages et d’élevage. L’année 2015 est la première année de transition pour laquelle un début d’évolution des modalités de surveillance de la santé des mollusques marins animées par l’Ifremer a été amorcé. Un dispositif hybride de surveillance a été mis en place, s’appuyant sur l’existant et intégrant des débuts d’évolution. La surveillance événementielle a constitué l’activité principale du dispositif en 2015 et s’est appuyée sur des réseaux existants : (1) la surveillance des mortalités observées sur des animaux sentinelles déployés sur les sites ateliers des réseaux Ifremer RESCO 2 (12 sites) pour l’huître creuse Crassostrea gigas et MYTILOBS 2 (8 sites) pour la moule bleue Mytilus edulis. Pour l’huître creuse Crassostrea gigas, la mortalité cumulée moyenne était de 50,3% (écart-type 10,9%) pour le naissain standardisé Ifremer (NSI), de 11,0% (écart-type 9,1%) pour les huîtres de 18 mois et de 7,3% (écart-type 5,6%) pour les huîtres de 30 mois. Les mortalités ont été observées principalement entre le début du mois de mai et la mi-juillet. Lors de ces épisodes de mortalité, des prélèvements d’animaux ont été réalisés en vue d’analyses diagnostiques : 7 prélèvements pour le NSI, 2 pour les huîtres de 18 mois et 1 pour les huîtres de 30 mois. Aucun agent réglementé n’a été détecté dans les échantillons d’huîtres creuses prélevés et analysés. Le virus OsHV-1 a été détecté dans les 7 échantillons analysés de NSI, dans 2 échantillons analysés d’huîtres de 18 mois et dans 1 échantillon analysé d’huîtres de 30 mois. La bactérie Vibrio aestuarianus a été détectée dans 5 échantillons analysés de NSI, dans 1 échantillon d’huîtres de 18 mois et dans 1’échantillon d’huîtres de 30 mois. Pour la moule bleue Mytilus edulis, des mortalités cumulées variant de 9% sur le site du Vivier à 51% sur le site des filières du Pertuis Breton ont été estimées. Les mortalités ont été observées au printemps sur des moules âgées d’une année et en automne sur des moules plus jeunes. Lors de ces épisodes de mortalités, des prélèvements d’animaux ont été réalisés en vue d’analyses diagnostiques : 2 prélèvements pour les moules d’une année et 1 pour les jeunes moules. Ces prélèvements ont eu lieu dans le Pertuis Breton. Aucun agent réglementé n’a été détecté dans les échantillons de moules prélevés et analysés. Des bactéries du groupe Splendidus ont été détectées dans les 3 échantillons de moules analysés. (2) la surveillance s’appuyant sur les déclarations de mortalités de mollusques par les conchyliculteurs et pêcheurs à pied professionnels auprès des Directions départementales des territoires et de la mer (DDTM). Cette modalité s’applique aux huîtres creuses et aux moules bleues lorsqu’il n’existe pas de site atelier RESCO 2 ou MYTILOBS 2 dans la zone où des mortalités sont déclarées par les conchyliculteurs ou pêcheurs à pied. Le réseau REPAMO 2 a réalisé 22 interventions, dont 15 pour les moules Mytilus edulis, 4 pour les coques Cerastoderma edule, 2 pour les palourdes Ruditapes sp. et 1pour les coquilles saint Jacques Pecten maximus. La recherche d’agents infectieux dans ces espèces de mollusques prélevés lors de hausse de mortalité a permis de mettre en évidence les parasites réglementés Perkinsus olseni dans 1 lot de palourdes, et Marteilia refringens dans 4 lots de moules, ainsi que le virus OsHV-1 dans 1 lot de palourdes et 1 lot de coques, la bactérie Vibrio aestuarianus dans 3 lots de coques, et des bactéries du groupe Splendidus dans 3 lots de coques et dans 13 lots de moules. L’année 2015 a également permis la démonstration sur un site atelier d’un exercice de surveillance programmée, ciblée et fondée sur les risques d’introduction et d’installation d’un organisme pathogène exotique. Elle a concerné le parasite Mikrocytos mackini de l’huître creuse Crassostrea gigas, sur un site atelier de la Charente-Maritime, suivi par le réseau RESCO 2. Le parasite Mikrocytos mackini n’a pas été détecté. En revanche, le parasite Marteilia refringens a été détecté dans ¾ des prélèvements d’huîtres réalisés. Dans le cadre du soutien scientifique et technique de l’évolution de la surveillance événementielle, l’année 2015 a également permis de poursuivre la démarche relative aux développements méthodologiques en lien avec la surveillance événementielle des mortalités de mollusques marins. Une étude de faisabilité de la recherche prospective de regroupements spatio-temporels d’événements de mortalités d’huîtres creuses a été préparée en collaboration avec tous les acteurs de la santé des mollusques marins en Normandie. Un outil de collecte et d’analyse des données de signalements des mortalités, automatisé, simple d’utilisation et flexible, a été élaboré.

Mortalités de moules bleues dans les Pertuis Charentais: description et facteurs liés – MORBLEU

Depuis 2014, des surmortalités anormales affectent les cheptels mytilicoles tant adultes que juvéniles avec des mortalités massives pouvant atteindre 100% (Béchemin et al. 2015). Les objectifs généraux de ce projet sont d’identifier des facteurs potentiellement corrélés avec les mortalités de moules observées dans les Pertuis Charentais: facteurs environnementaux biotiques, abiotiques et hydrodynamiques) et facteurs intrinsèques aux animaux (traits d'histoire de vie, qualité cytogénétique et physiologie). Après une introduction bibliographique complète, différentes questions sont ici abordées. 1. Historique des mortalités 2014-2015 ? Grâce { différentes sources d’information nous avons pu retracer les évènements de mortalités de 2014 et 2015 et valider l’échantillonnage réalisé en 2015 dans Morbleu (au niveau temporel et spatial). 2. Les mortalités 2014 et 2015 sont-elles exceptionnelles ? Existe-t-il un lien avec les fluctuations environnementales ? Pour cela, nous avons porté un regard rétrospectif sur 15 années de données acquises dans les réseaux portés par Ifremer afin de définir un niveau de mortalité « anormale » et d’explorer de potentiels liens avec les fluctuations environnementales. Nous avons pu observer que (1) les épisodes de mortalités de 2014 et 2015 peuvent être qualifiés d’exceptionnels, (2) ils sont survenus dans des conditions climatiques plutôt chaudes et pluvieuses associées à des indices de diversité phytoplanctoniques bas (nombre de taxons et équilibre quantitatif entre ces taxons). 3. Dans quelles conditions les mortalités de moules sont-elles survenues en 2015 ? Nous présentons ici dispositif mis en place sur nos 4 sites ateliers (Filière, Boyard, Eperon et Loix) et l’ensemble des échantillons et mesures collectées (environnement abiotique ou biotique, ou connectivité hydrodynamique des masses d’eaux). Cette action de recherche a nécessité 16 campagnes et aboutit à la bancarisation de 805 échantillons, certains prévelés au cours des mortalités observées sur les animaux déployés. Les mortalités observées en 2015 sont survenues dans un contexte environnemental abiotique différent de celui observé en 2014 (absence de dessalure comparable à celles observées en 2014, différence dans la contribution relative des fleuves aux masses d’eau). Néanmoins, les conditions hydrodynamiques et la connectivité entre les sites du Pertuis Breton et les côtes vendéennes sont quant à elle comparables entre ces 2 années. 4. Quelle(s) ont été la(les) espèce(s) ou population(s) de moules affectée(s) ? Différentes espèces et populations étant présentes sur les côtes française, nous avons cherché à préciser les ascendances génétiques sur des animaux moribonds et vivants prélevés (MORBLEU et mortalité déclarées MYTILOBS-2). Pour 99% d’entre eux, les animaux analysés ont pu être affiliés au fond génétique M. edulis européen du Golf de Gascogne. Toutefois la présence d’ascendance trossulus sur certains individus est à considérer. Avec les marqueurs utilisés, aucune différence génétique entre les animaux moribonds et survivants n’a pas être observée, les mortalités touchant certains hybrides edulis/galloprovincialis en proportion identique à celle de M. edulis. 5. Quelle était la qualité cytogénétique des animaux en 2015 ? Pourrait-il exister un lien avec les mortalités observées ? Nous avons échantillonné des animaux prélevés sur 7 sites mytilicoles avant et après la mortalité de l’année 2015. Les analyses de la qualité cytogénétique de ces animaux est toujours en cours. 6. Ces animaux étaient-ils dans des conditions physiologiques particulières ? des échantillons de moules vivantes, collectés avant, après et au cours des mortalités, sur des sites impactés et peu/pas impactés ont été analysés par une approche transcriptomique à haut débit (RNA-seq). L’échantillonnage 2015 ayant été tardif dans l’année (prélèvements jusqu’en juillet 2015), la réalisation de l’approche transcriptomique a été retardée. Le traitement des données de séquençage est encore en cours d’analyse. Ainsi cette année nous a permis (1) de confronter les données environnementales à 15 années de mesures, (2) de mettre en place un dispositif et d’échantillonner au cours d’un épisode de mortalité, (3) de préciser le fond génétique des animaux affectés. Cependant les prélèvements ayant été tardifs, de nombreuses analyses sont encore en cours de traitement.