71 research outputs found

    Applicability of the Caenorhabditis elegans survival, growth and reproduction test to assess the effects of biosolids used in agriculture

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    Modern high productivity agriculture has led to an impoverishment of nutrients and organic carbon in field soils, and as a consequence plants nutrition complements like fertilisers or wastes have to be used to keep high yield. These complex materials can also be a source of toxicants, depending on their origin, so there is a necessity to assess their environmental effects before field use. In this study, biosolids used in agriculture were tested as a mix with standard soil at different field dose through ecotoxicity test on the nematode Caenorhabditis elegans, endpoints for this organism being survival, growth and reproduction. In order to run these tests we first followed the standardized protocol for sediment and soil testing with C. elegans (ISO 10872, 2010). These results showed that the mixtures could be significantly different according to the type of soil (e.g. two phases system with overlaying water). Indeed, soil moistening in the standardized protocol is based on soil dry weight which means that the same amount of water is added for every soil, regardless of the water holding capacity (WHC) of the samples. Moreover, some biosolids can have a high WHC what increase humidity's differences among soil and soil mixed with biosolids when moistened as recommended by this protocol. To prevent this, improvements of the standardized protocol were developed, in which water addition is based on soil WHC instead of soil dry weight. Moreover, food volume added to the samples was lowered in order to be able to include it in the volume for soil moistening. In this context and in order to validate this new method, comparisons between standardized and optimized protocols were carried out for endpoints responses in five soils with different textures. This optimized protocol was used to assess the effect of different biosolids (limed sludge, manure ...) mixed with standard soil at different field rates and an example for a limed sludge is given. Regarding these results, improvements of the standardized protocol are adapted to assess the effects of these materials on C. elegans

    Effect of non-ageing and ageing ceria nanoparticles suspensions on fresh water micro-algae

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    When assessing the hazards properties of nanomaterials in the environment, the main research challenges are numerous. Firstly, determining if nanomaterials are more or less toxic than the bulk forms of the same materials and the extent to which toxicity is governed or influenced by the physico-chemicals properties of the nanoparticles. Secondly, it appears necessary to study the effect of nanomaterials and nanoparticles throughout their life cycle including both initial forms and physico-chemically modified form (i.e. aggregated or agglomerated forms) resulting from an ageing process. Our work focused on the effect of commercial ceria nanoparticle (nCeO2) suspensions, towards freshwater micro-algae assessing the effect nCeO2 suspensions with different agglomeration/aggregation state obtained by using an artificial ageing process. Both ageing and non-ageing nCeO2 suspensions were fully characterized using dynamic light scattering (ZetaSizer, Malvern Instruments) or laser diffraction (MasterSizer, Malvern Instruments) and transmission electron microscopy (TEM). In addition, the interaction between NPs and algae were investigated using flow-cytometry and environmental scanning electron microscope technique (E-SEM).The results obtained showed that the algae growth inhibition was similar after exposure to non-ageing or ageing nCeO2 suspensions. The results obtained from flow-cytometry and E-SEM proved that the ceria NPs are able to tightly entrap the algae cells, which could in part contribute to the effect recorded. Those results also support the fact that aggregation or agglomeration has a few influences when focusing on the standardized algae ecotoxicity test. Moreover by comparison to our previous studies performed with other ceria suspensions, it was shown that the primary particle size and consequently the particle surface area is a relevant parameter in assessing the ecotoxicity of nanoparticles

    Investigating a transcriptomic approach on marine mussel hemocytes exposed to carbon nanofibers: An in vitro/in vivo comparison

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    Manufactured nanomaterials are an ideal test case of the precautionary principle due to their novelty and potential environmental release. In the context of regulation, it is difficult to implement for manufactured nanomaterials as current testing paradigms identify risk late into the production process, slowing down innovation and increasing costs. One proposed concept, namely safe(r)-by-design , is to incorporate risk and hazard assessment into the design process of novel manufactured nanomaterials by identifying risks early. When investigating the manufacturing process for nanomaterials, differences between products will be very similar along key physicochemical properties and biological endpoints at the individual level may not be sensitive enough to detect differences whereas lower levels of biological organization may be able to detect these variations. In this sense, the present study used a transcriptomic approach on Mytilus edulis hemocytes following an in vitro and in vivo exposure to three carbon nanofibers created using different production methods. Integrative modeling was used to identify if gene expression could be in linked to physicochemical features. The results suggested that gene expression was more strongly associated with the carbon structure of the nanofibers than chemical purity. With respect to the in vitro/in vivo relationship, results suggested an inverse relationship in how the physicochemical impact gene expression

    Adapting oecd aquatic toxicity tests for use with manufactured nanomaterials: key issues and consensus recommendations

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    The unique or enhanced properties of manufactured nanomaterials (MNs) suggest that their use in nanoenabled products will continue to increase. This will result in increased potential for human and environmental exposure to MNs during manufacturing, use, and disposal of nanoenabled products. Scientifically based risk assessment for MNs necessitates the development of reproducible, standardized hazard testing methods such as those provided by the Organisation of Economic Cooperation and Development (OECD). Currently, there is no comprehensive guidance on how best to address testing issues specific to MN particulate, fibrous, or colloidal properties. This paper summarizes the findings from an expert workshop convened to develop a guidance document that addresses the difficulties encountered when testing MNs using OECD aquatic and sediment test guidelines. Critical components were identified by workshop participants that require specific guidance for MN testing: preparation of dispersions, dose metrics, the importance and challenges associated with maintaining and monitoring exposure levels, and the need for reliable methods to quantify MNs in complex media. To facilitate a scientific advance in the consistency of nanoecotoxicology test results, we identify and discuss critical considerations where expert consensus recommendations were and were not achieved and provide specific research recommendations to resolve issues for which consensus was not reached. This process will enable the development of prescriptive testing guidance for MNs. Critically, we highlight the need to quantify and properly interpret and express exposure during the bioassays used to determine hazard values

    Population Structure and Gene Flow of the Yellow Anaconda (Eunectes notaeus) in Northern Argentina

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    Yellow anacondas (Eunectes notaeus) are large, semiaquatic boid snakes found in wetland systems in South America. These snakes are commercially harvested under a sustainable management plan in Argentina, so information regarding population structuring can be helpful for determination of management units. We evaluated genetic structure and migration using partial sequences from the mitochondrial control region and mitochondrial genes cyt-b and ND4 for 183 samples collected within northern Argentina. A group of landscape features and environmental variables including several treatments of temperature and precipitation were explored as potential drivers of observed genetic patterns. We found significant population structure between most putative population comparisons and bidirectional but asymmetric migration in several cases. The configuration of rivers and wetlands was found to be significantly associated with yellow anaconda population structure (IBD), and important for gene flow, although genetic distances were not significantly correlated with the environmental variables used here. More in-depth analyses of environmental data may be needed to fully understand the importance of environmental conditions on population structure and migration. These analyses indicate that our putative populations are demographically distinct and should be treated as such in Argentina's management plan for the harvesting of yellow anacondas

    Prediction of second neurological attack in patients with clinically isolated syndrome using support vector machines

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    The aim of this study is to predict the conversion from clinically isolated syndrome to clinically definite multiple sclerosis using support vector machines. The two groups of converters and non-converters are classified using features that were calculated from baseline data of 73 patients. The data consists of standard magnetic resonance images, binary lesion masks, and clinical and demographic information. 15 features were calculated and all combinations of them were iteratively tested for their predictive capacity using polynomial kernels and radial basis functions with leave-one-out cross-validation. The accuracy of this prediction is up to 86.4% with a sensitivity and specificity in the same range indicating that this is a feasible approach for the prediction of a second clinical attack in patients with clinically isolated syndromes, and that the chosen features are appropriate. The two features gender and location of onset lesions have been used in all feature combinations leading to a high accuracy suggesting that they are highly predictive. However, it is necessary to add supporting features to maximise the accuracy. © 2013 IEEE

    Prise en compte de l’évolution de l’état d’agglomĂ©ration dans l’étude de l’écotoxicitĂ© des nanoparticules

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    When assessing the hazardous properties of nanomaterials for the environment, there are numerous significant research challenges. Among them, it appears necessary to study the effect of nanomaterials and nanoparticles throughout their life cycle including both initial forms and physico-chemically modified forms (i. e. aggregated or agglomerated forms) that may result from an ageing process. We addressed this question by focusing on the effect of commercial ceria nanoparticle (nCeO2) suspensions on freshwater micro-algae. We assessed the effect of nCeO2 suspensions with different agglomeration/aggregation states obtained by using an artificial ageing process. It was shown that the algae growth inhibition was similar after exposure to non-degraded or degraded nCeO2 suspensions. Those results support the fact that aggregation or agglomeration has little influence when focusing on the growth of algal cells. Moreover by comparison to our previous studies performed with other ceria particle suspensions, it was shown that the primary particle size and consequently the particle surface area is a relevant parameter in assessing the ecotoxicity of nanoparticles.L’utilisation grandissante de produits contenant des nanoparticules peut entraĂźner une exposition des diffĂ©rents compartiments environnementaux. Par consĂ©quent, l’évaluation des effets pour l’environnement de ces nanoparticules apparaĂźt indispensable. La spĂ©cificitĂ© et la rĂ©activitĂ© importante de ce type de composĂ©s conduit Ă©galement Ă  s’interroger sur leur comportement lors d’un relargage Ă©ventuel dans l’environnement. Cet aspect, bien que rarement renseignĂ©, se rĂ©vĂšle fondamental pour mieux apprĂ©hender l’écotoxicitĂ© de ces nanoparticules au cours de leur cycle de vie, incluant les formes altĂ©rĂ©es, potentiellement agrĂ©gĂ©es et/ou agglomĂ©rĂ©es. Ces questions ont Ă©tĂ© rĂ©cemment abordĂ©es . Dans ce cadre, l’étude d’une suspension de nanoparticules de dioxyde de cĂ©rium (CeO2 ; taille primaire = 8 nm) possĂ©dant un coating organique a Ă©tĂ© rĂ©alisĂ©e. Cette suspension est commercialisĂ©e en tant qu’agent protecteur (anti-rayure anti-UV) Ă  destination des peintures extĂ©rieures. Le comportement dans l’eau de cette suspension de nanoparticules avant et aprĂšs un processus artificiel de vieillissement ainsi que les effets sur les producteurs primaires ont Ă©tĂ© Ă©tudiĂ©s

    Devenir et impact des contaminants dans l'environnement : application Ă  la gestion des sĂ©diments et des boues d'Ă©puration. Contribution Ă  l'Ă©laboration d'une mĂ©thodologie de caractĂ©risation de l'Ă©cotoxicitĂ© des sĂ©diments dulçaquicoles contaminĂ©s : intĂ©rĂȘt de nouveaux outils Ă©cotoxicologiques. Rapport final

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    Au cours de ces derniĂšres annĂ©es, diffĂ©rentes mĂ©thodologies d’évaluation de l’écotoxicitĂ© des sĂ©diments ont Ă©tĂ© proposĂ©es.Depuis, de nouveaux outils de caractĂ©risation des dangers des sĂ©diments ont Ă©tĂ© normalisĂ©s Ă  l’ISO. C’est le cas des essais sur :- NĂ©matodes : dĂ©termination de l'effet toxique d'Ă©chantillons de sĂ©diment et de sol sur la croissance, la fertilitĂ© et la reproduction de Caenorhabditis elegans (NF ISO 10872 :2010) ;- Ostracodes : dĂ©termination de la toxicitĂ© des sĂ©diments d'eau douce envers Heterocypris incongruens (NF ISO 14371:2012) ;- BactĂ©ries : dĂ©termination de l'inhibition de l'activitĂ© dĂ©shydrogĂ©nase d'Arthrobacter globiformis - essai de contact sur solide avec le colorant redox rĂ©sazurine (ISO/FDIS 18187) ;- Macrophytes : dĂ©termination de l'effet toxique des sĂ©diments sur la croissance de Myriophyllum aquaticum (NF ISO 16191:2014).Bien que rĂ©cemment standardisĂ©s, peu de travaux renseignant sur l’utilisation de ces nouveaux protocoles d’essai dans un contexte de caractĂ©risation de l’écotoxicitĂ© des sĂ©diments sont disponibles (Höss et al. 2010 ; Feiler et al. 2013). Le prĂ©sent projet avait pour objectif d’évaluer l’applicabilitĂ© effective de ces nouveaux protocoles d’essai dans ce contexte et de juger de la pertinence et de la sensibilitĂ© de ces organismes par rapport aux essais plus classiquement rĂ©alisĂ©s (essais sur larves de chironomes notamment). La sensibilitĂ© des organismes vis-Ă -vis de substances chimiques de rĂ©fĂ©rence, la question des substrats proposĂ©s en tant que tĂ©moins ont Ă©tĂ© discutĂ©s prĂ©cĂ©demment. Les rĂ©sultats de ces travaux ont fait l’objet des deux premiers rapports d’avancement de 2013 et 2014 (DRC13-136875-13811A et DRC-15-136875-04705A).Au cours de l’annĂ©e 2015, les travaux portant sur l’utilisation de ces bioessais pour la caractĂ©risation des sĂ©diments ont Ă©tĂ© finalisĂ©s. Une derniĂšre campagne de prĂ©lĂšvement de sĂ©diments a Ă©tĂ© effectuĂ©e. L’ensemble des sĂ©diments prĂ©levĂ©s au cours des campagnes de 2014 et 2015 a Ă©tĂ© testĂ© Ă  l’aide des essais sur Caenorhabditis elegans (nĂ©matode), Heterocypris incongruens (ostracode), Myriophyllum aquaticum (macrophyte) et Arthrobacter globiformis (bactĂ©rie), mais aussi Ă  l’aide de l’essai sur Chironomus riparius renseignant sur la mortalitĂ©, l’inhibition de la croissance et l’inhibition de l’émergence des larves de diptĂšres. Les sĂ©diments des campagnes de 2014 et 2015 ont Ă©galement Ă©tĂ© analysĂ©s afin de les caractĂ©riser sur un plan physico-chimique (granulomĂ©trie, paramĂštres gĂ©ochimiques, oligo-Ă©lĂ©ments) ainsi que sur leur niveau de contamination en polluants principaux (mĂ©taux et HAP, essentiellement)

    Nanoparticules : influence des conditions d’essais et des paramĂštres physico-chimiques sur l’écotoxicitĂ© pour le milieu aquatique

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    Nanoparticles (NP) have been extensively applied in commercial products. It is consequently unavoidable that a large amount of NP will be discharged into environment, underlining the need to evaluate the ecotoxicological effect of NP towards aquatic organisms. However, relevant experts identified that “a large number of standardized test guidelines [
] are unlikely to be applicable in their present state to engineered nanomaterials” (OECD). Indeed, the potential hazard of NP may be related to unusual physicochemical properties such as their particles size, agglomerate state in suspension and/or surface chemistry. Moreover, the method performed to disperse NP and achieve the testing suspensions can be seen as a drawback since it introduces an additional variable into the test design. Our work aims at characterizing the ecotoxicity of ceria NP toward aquatics micro-algae taking into account the influence of the dispersive methods and the physico-chemical properties of NP. The results obtained clearly show that ceria NP are ecotoxic toward micro algae compare to bulk materials. The toxic effect was principally attributing to the initial particles size and, to a lesser extent, to the agglomeration state. This suggest that exposure to NP could be expressed in surface area complementary to a mass basis. In addition, we have demonstrated that ceria NP were able to entrap and wrap the algae cells, which may contribute to the nanotoxicity.La singularitĂ© des propriĂ©tĂ©s physicochimiques des nanoparticules (NP) et le fait qu’un grand nombre de produits dits « nanostructurĂ©s » sont d’ores et dĂ©jĂ  mis sur le marchĂ© en font un des sujets majeurs d’étude de ces derniĂšres annĂ©es. La dissĂ©mination de ces NP ou des rĂ©sidus nanoparticulaires dans les diffĂ©rents compartiments de l’environnement est ainsi devenue une prĂ©occupation grandissante, Ă  l’instar de l’impact potentiel qu’ils peuvent avoir sur les organismes vivants. De nombreuses questions se posent, en effet, quant Ă  l’applicabilitĂ© des outils actuels pour Ă©valuer l’écotoxicitĂ© de ces produits Ă©mergents, notamment dans un cadre rĂ©glementaire. Les mĂ©thodes de prĂ©paration et les propriĂ©tĂ©s physico-chimiques des milieux d’essai (pH, force ionique) ont notamment Ă©tĂ© identifiĂ©es comme des Ă©lĂ©ments clĂ©s dans l’évaluation de l’écotoxicitĂ© des NP. Ils vont en effet conditionner certains paramĂštres physiques de la suspension tels que l’état d’agglomĂ©ration des NP et leur stabilitĂ©, lesquels peuvent influencer leur Ă©cotoxicitĂ©. Cependant, peu de travaux concernant l’écotoxicitĂ© des NP intĂšgrent de façon systĂ©matique l’influence des conditions d’essai, de mĂȘme que l’importance des propriĂ©tĂ©s physicochimiques des NP. Ainsi, les objectifs de nos travaux sont multiples et visent Ă  Ă©tudier l’influence de diffĂ©rentes mĂ©thodes de prĂ©paration des suspensions d’essai sur l’état d’agrĂ©gation de NP, et Ă  identifier les paramĂštres physicochimiques (Ă©tat d’agglomĂ©ration, chimie de surface, taille initiale de la particule) potentiellement responsable de l’écotoxicitĂ© pour les organismes aquatiques. Nous avons pour cela entrepris l’étude de diffĂ©rentes NP d’oxydes de cĂ©rium en tant que particules modĂšles. Ces NP sont utilisĂ©es comme catalyseur dans certains moteurs diesels ou comme agent protecteur (anti-rayure, anti-UV) dans les peintures extĂ©rieures. Ils peuvent de ce fait se retrouver facilement dans l’environnement. Les effets pour le compartiment aquatique de ces NP ont Ă©tĂ© apprĂ©hendĂ©s Ă  travers l’étude de leur Ă©cotoxicitĂ© vis-Ă -vis des micro-algues d’eau douce (P. subcapitata). Ces organismes, Ă  la base des chaĂźnes trophiques aquatiques, sont classiquement utilisĂ©s en tant qu’organismes modĂšles pour la dĂ©termination de l’écotoxicitĂ© des substance

    What could be a relevant and cost & time effective tools-set for ecosystem risk assessment strategies ?

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    Socio-economic development and sustainable development politic programs are nowadays link to a sharp increase in performing ecosystems risk assessment (ERA) studies in UE countries. Some relevant methodologies have previously been proposed in order to give consensual guidances and directives in this field. Each states that, depending on the studies context, those assessments should be focused on the biological targets of one or more of the three inland environmental compartments (aquatic, terrestrial, air). This leads to usually describe ERA studies as an expensive and time consuming work, and in several cases one could question the relevancy of such extensive investigations. Many biological assessment tools from individuals bioassays to in situ studies are used in this field but few works were aimed to suggest a generic, scientifically and environmentally relevant and cost-time effective tools-set for ERA. Based on previous studies and our experience in the field of environmental risk assessment, we propose a decision tree taking into account the balance between time, cost and relevancy of various biological tools, including both ecotoxicological and ecological point of view. We also suggest that biological tools and environmental monitoring cannot be dissociated in an ERA strategies. Taking into account of this complementarity, we discuss how these tools could be selected and we finally propose an optimal base-set assessment package for ERA on the model of required data set for new existing substances in the European regulation. We think that this work is the next challenge in the way to further define consensual ERA strategies and methodologies
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