313 resultados para Occupational exposure limits


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La manipulation de végétaux ou de débris végétaux dans des espaces fermés (hangar pour le compostage, serres pour les cultures) est fréquemment effectuée en France. Néanmoins, le niveau d'exposition des travailleurs des différentes filières concernées aux bioaérosols dégagés par ces substrats, est peu connu. Dans cette note, deux études ont été choisies pour illustrer l'ampleur de ce type d'exposition dans des espaces fermés. La première publication concerne un centre de compostage et la deuxième publication cible des serres de culture de la tomate et du concombre. L'extrapolation des résultats obtenus à partir de prélèvements d'ambiance à l'exposition professionnelle des travailleurs est tout particulièrement discutée.

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Le taux de retour au travail après greffe est généralement bas. Or, on sait que le retour au travail après greffe améliore la qualité de vie des transplantés. Le but de notre étude était donc de comprendre les raisons possibles à ce faible taux en montrant les facteurs professionnels, individuels ou médicaux pouvant l'influencer. Parmi les 61 greffés rénaux ou hépatiques suivis au centre de transplantation d'organe (CTO) du CHUV, 39% ont repris le travail après greffe. Trois facteurs étaient significatifs de retour au travail après greffe, à savoir «travail avant greffe», «diplôme» et «âge < 45 ans». Ainsi, il est utile pour la pratique médicale de connaître les facteurs potentiels influençant le retour au travail car cela permet d'évaluer, au stade prégreffe, les chances de retour au travail et si besoin de proposer des mesures spécifiques le favorisant.

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L' évaluation quantitative des dangers et des expositions aux nanomatériaux se heurte à de nombreuses incertitudes qui ne seront levées qu'à mesure de la progression des connaissances scientifiques de leurs propriétés. L' une des conséquences de ces incertitudes est que les valeurs limites d'exposition professionnelle définies actuellement pour les poussières ne sont pas nécessairement pertinentes aux nanomatériaux. En l'absence de référentiel quantitatif et, à la demande de la DGS pour éclairer les réflexions de l' AFNOR et de l'ISO sur le sujet, une démarche de gestion graduée des risques (control banding) a été élaborée au sein de l' Anses. Ce développement a été réalisé à l'aide d'un groupe d'experts rapporteurs rattaché au Comité d'experts spécialisés évaluation des risques liés aux agents physiques, aux nouvelles technologies et aux grands aménagements. La mise en oeuvre de la démarche de gestion graduée des risques proposée repose sur quatre grandes étapes: 1. Le recueil des informations. Cette étape consiste à réunir les informations disponibles sur les dangers du nanomatériau manufacturé considéré ; ainsi que sur l'exposition potentielle des personnes aux postes de travail (observation sur le terrain, mesures, etc.). 2. L'attribution d'une bande de danger. Le danger potentiel du nanomatériau manufacturé présent, qu'il soit brut où incorporé dans une matrice (liquide ou solide) est évalué dans cette étape. La bande danger attribuée tient compte de la dangerosité du produit bulk ou de sa substance analogue à l'échelle non-nanométrique, de la bio-persistance du matériau (pour les matériaux fibreux), de sa solubilité et de son éventuelle réactivité. 3. Attribution d'une bande d'exposition. La bande d'exposition du nanomatériau manufacturé considéré ou du produit en contenant est définie par le niveau de potentiel d'émission du produit. Elle tient compte de sa forme physique (solide, liquide, poudre aérosol), de sa pulvérulence et de sa volatilité. Le nombre de travailleurs, la fréquence, la durée d'exposition ainsi que la quantité mise en oeuvre ne sont pas pris en compte, contrairement à une évaluation classique des risques chimiques. 4. Obtention d'une bande de maîtrise des risques. Le croisement des bandes de dangers et d'exposition préalablement attribuées permet de défi nir le niveau de maîtrise du risque. Il fait correspondre les moyens techniques et organisationnels à mettre en oeuvre pour maintenir le risque au niveau le plus faible possible. Un plan d'action est ensuite défi ni pour garantir l'effi cacité de la prévention recommandée par le niveau de maîtrise déterminé. Il tient compte des mesures de prévention déjà existantes et les renforce si nécessaire. Si les mesures indiquées par le niveau de maîtrise de risque ne sont pas réalisables, par exemple, pour des raisons techniques ou budgétaires, une évaluation de risque approfondie devra être réalisée par un expert. La gestion graduée des risques est une méthode alternative pour réaliser une évaluation qualitative de risques et mettre en place des moyens de prévention sans recourir à une évaluation quantitative des risques. Son utilisation semble particulièrement adaptée au contexte des nanomatériaux manufacturés, pour lequel les choix de valeurs de référence (Valeurs limites d'exposition en milieu professionnel) et des techniques de mesurage appropriées souffrent d'une grande incertitude. La démarche proposée repose sur des critères simples, accessibles dans la littérature scientifi que ou via les données techniques relatives aux produits utilisés. Pour autant, sa mise en oeuvre requiert des compétences minimales dans les domaines de la prévention des risques chimiques (chimie, toxicologie, etc.), des nanosciences et des nanotechnologies.

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L'article présente les étapes de la mise en place d'une veille bibliographique (ou veille scientifique) thématique effectuée conjointement depuis 2005 par 4 institutions francophones du domaine de la santé au travail : l'INRS (France), l'IRSST (Québec), l'IST (Suisse) et l'UCL (Belgique).La thématique suivie est celle de la surveillance biologique de l'exposition aux produits chimiques en milieu de travail. Les données recueillies et mises en forme par les documentalistes servent aux chercheurs spécialistes du sujet non seulement pour suivre les nouveautés du domaine, mais aussi pour documenter des cours et mettre à jour des guides de surveillance biologique. Les différentes étapes de l'approche méthodologique du projet sont décrites : le choix des bases de données à interroger et la mise au point de la stratégie de recherche, la mise en place d'une procédure de partage des tâches pour toutes les étapes du processus de veille qui se répètent à chaque mise à jour (interrogation, création de bases de données avec le logiciel Reference Manager, mise en forme et indexation des références, création et mise à disposition des partenaires des bases de données consolidées au fil du temps avec tous les articles analysés), les moyens administratifs, humains et techniques d'échange de fichiers et les essais pour élargir la veille à la surveillance de pages Web sélectionnées.Un bilan chiffré des six années de la veille est également donné.L'information récoltée et analysée durant les deux dernières années par les partenaires du projet fera l'objet d'un second article axé sur les principales tendances de la thématique choisie.

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Pollution of air, water and soil by industrial chemicals presents a potential health risk to humans. Such chemicals can enter the human body by three routes, namely by inhalation, dermal absorption, and ingestion and in special cases by injection (needle sticks, bites, cuts, etc.). In the workplace, pulmonary and dermal absorption are the main routes of entry, but poor personal hygiene and work habits can result in ingestion that contributes to the dose. Air monitoring provides reliable information on inhalation exposure, and patches can be used to estimate dermal exposure. Local adverse effects, such as skin and eye irritation, or nose and lung irritation, are closely related to the external exposure. Systemic adverse effects, on the other hand, are related to the absorbed amount (dose), or to the level of the pollutant or its metabolite in the target organ. Human biological monitoring is becoming a powerful tool for scientists and policy makers to assess and manage the risk of exposure to chemicals both in the general population and at the workpalce. This chapter will focus on the occupational environment keeping in mind that biological monitoring in humans is a very actual issue in public health politics, in environmental medicine, and in science in general.

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Occupational exposure to metals such as cobalt and beryllium represents a risk factor for respiratory health and can cause immune-mediated diseases. However, the way they act may be different. We show here that the two metals have a divergent effect on peripheral T lymphocytes and monocytes: BeSO(4) induces cell death in monocytes but not in T lymphocytes, which instead respond by producing Interferon gamma (IFN-γ); conversely, CoCl(2) induces apoptosis in T lymphocytes but not in monocytes. Interestingly, both metals induce p53 overexpression but with a dramatic different outcome. This is because the effect of p53 in CoCl(2)-treated monocytes is counteracted by the antiapoptotic activity of cytoplasmic p21(Cip1/WAF1), the activation of nuclear factor κB, and the inflammasome danger signaling pathway leading to the production of proinflammatory cytokines. However, CoCl(2)-treated monocytes do not fully differentiate into macrophage or dendritic cells, as inferred by the lack of expression of CD16 and CD83, respectively. Furthermore, the expression of HLA-class II molecules, as well as the capability of capturing and presenting the antigens, decreased with time. In conclusion, cobalt keeps monocytes in a partially activated, proinflammatory state that can contribute to some of the pathologies associated with the exposure to this metal.

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La variabilité interindividuelle au sein de la population générale se manifeste à plusieurs niveaux aussi bien externe pour des différences physiologiques qu'interne pour des différences toxicocinétiques et toxicodynamiques . Face à une agression chimique par exemple, nous ne réagissons en effet pas tous de manière identique. Entre le moment de l'exposition à un composé toxique et la maladie, une suite d'évènements biologiques peut survenir. La façon dont cette suite d'évènements se développera chez une personne dépend de sa susceptibilité individuelle aux risques chimiques. Celle-ci peut être déterminée par des facteurs génétiques, physiopathologiques (âge, sexe, grossesse, hormones, maladies, alimentation, etc.) et environnementaux. [Auteur]

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Carriage of animal-associated methicillin-resistant Staphylococcus aureus (MRSA) clonal complex 398 (CC398) is common among pig farmers. This study was conducted (i) to investigate whether pig farmers are colonized with pig-specific S. aureus genotypes other than CC398 and (ii) to survey antimicrobial resistance of S. aureus isolates from pigs and pig farmers. Forty-eight S. aureus isolates from pig farmers and veterinarians and 130 isolates from pigs collected in Western Switzerland were genotyped by spa typing and amplified fragment length polymorphism (AFLP). Antimicrobial resistance profiles were determined for representative sample of the isolates. The data obtained earlier on healthy S. aureus carriers without exposure to agriculture were used for comparison. The genotype composition of S. aureus isolates from pig farmers and veterinarians was similar to isolates from pigs with predominant AFLP clusters CC398, CC9, and CC49. The resistance to tetracycline and macrolides (clarithromycin) was common among the isolates from farmers and veterinarians (52 and 21%, respectively) and similar to resistance levels in isolates from pigs (39 and 23%, respectively). This was in contrast to isolates from persons without contact with agriculture, where no (0/128) isolates were resistant to tetracycline and 3% of the isolates were resistant to clarithromycin. MRSA CC398 was isolated from pigs (n = 11) and pig farmers (n = 5). These data imply that zoonotic transmission of multidrug-resistant S. aureus from pigs to farmers is frequent, and well-known MRSA transmission merely represents the tip of the iceberg for this phenomenon. We speculate that the relatively low frequency of MRSA isolation is related to lower antimicrobial use in Switzerland compared to, for example, the Netherlands.

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QUESTIONS UNDER STUDY: Hospitality workers are a population particularly at risk from the noxious effects of environmental tobacco smoke (ETS). The Canton of Vaud, Switzerland banned smoking in public places in September 2009. This prospective study addresses the impact of the ban on the health of hospitality workers. METHODS: ETS exposure was evaluated using a passive sampling device that measures airborne nicotine; lung function was assessed by spirometry; health-related quality of life, ETS exposure symptoms and satisfaction were measured by questionnaire. RESULTS: 105 participants (smokers and non-smokers) were recruited initially and 66 were followed up after one year. ETS exposure was significantly lower after the ban. Hospitality workers had lower pre-ban forced expiratory volume in one second (FEV1) and forced vital capacity (FVC) values than expected. FEV1 remained stable after the ban, with a near-significant increase in the subgroup of asthmatics only. FVC increased at one year follow-up from 90.42% to 93.05% (p = 0.02) in the entire cohort; women, non-smokers and older participants gained the greatest benefit. The health survey showed an increase in physical wellbeing after the ban, the greatest benefit being observed in non-smokers. ETS exposure symptoms were less frequent after the ban, especially red and irritated eyes and sneezing. The new law was judged useful and satisfactory by the vast majority of employees, including smokers. CONCLUSION: The recent cantonal ban on smoking in public places brought about an improvement in lung function, physical well-being and ETS symptoms of hospitality workers, including smokers.

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INTRODUCTION: Occupational exposure to bioaerosols in wastewater treatment plants (WWTP) and its consequence on workers׳ health are well documented. Most studies were devoted to enumerating and identifying cultivable bacteria and fungi, as well as measuring concentrations of airborne endotoxins, as these are the main health-related factors found in WWTP. Surprisingly, very few studies have investigated the presence and concentrations of airborne virus in WWTP. However, many enteric viruses are present in wastewater and, due to their small size, they should become aerosolized. Two in particular, the norovirus and the adenovirus, are extremely widespread and are the major causes of infectious gastrointestinal diseases reported around the world. The third one, hepatitis E virus, has an emerging status. GOAL AND METHODS: This study׳s objectives were to detect and quantify the presence and concentrations of 3 different viruses (adenovirus, norovirus and the hepatitis E virus) in air samples from 31 WWTPs by using quantitative polymerase chain reaction (qPCR) during two different seasons and two consecutive years. RESULTS: Adenovirus was present in 100% of summer WWTP samples and 97% of winter samples. The highest airborne concentration measured was 2.27×10(6) genome equivalent/m(3) and, on average, these were higher in summer than in winter. Norovirus was detected in only 3 of the 123 air samples, and the hepatitis E virus was not detected. CONCLUSIONS: Concentrations of potentially pathogenic viral particles in WWTP air are non-negligible and could partly explain the work-related gastrointestinal symptoms often reported in employees in this sector.

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Background Addressing the risks of nanoparticles requires knowledge about their hazards, which is generated progressively, but also about occupational exposure and liberation into the environment. However, currently such information is not systematically collected, therefore the risk assessment of this exposure or liberation lacks quantitative data. In 2006 a targeted telephone survey among Swiss companies (1) showed the usage of nanoparticles in a few selected companies but did not provide data to extrapolate on the totality of the Swiss workforce. The goal of this study was to evaluate in a representative way the current prevalence and level of nanoparticle usage in Swiss industry, the health, safety and environment measures, and the number of potentially exposed workers. Results A representative, stratified mail survey was conducted among 1,626 clients of the Swiss National Accident Insurance Fund (SUVA). SUVA insures about 80,000 manufacturing firms, which represent 84% of all Swiss manufacturing companies. 947 companies answered the survey (58.3% response rate). Extrapolation to all Swiss manufacturing companies results in 1,309 workers (95%-confidence interval, 1,073 to 1,545) across the Swiss manufacturing sector being potentially exposed to nanoparticles in 586 companies (95%-CI: 145 to 1'027). This corresponds to 0.08% (95%-CI: 0.06% to 0.09%) of all Swiss manufacturing sector workers and to 0.6% (95%-CI: 0.2% to 1.1%) of companies. The industrial chemistry sector showed the highest percentage of companies using nanoparticles (21.2% of those surveyed) and a high percentage of potentially exposed workers (0.5% of workers in these companies), but many other important sectors also reported nanoparticles. Personal protection equipment was the predominant protection strategy. Only a minority applied specific environmental protection measures. Conclusions This is the first representative nationwide study on the prevalence of nanoparticle usage across a manufacturing sector. The information about the number of companies can be used for quantitative risk assessment. Furthermore it can help policy makers designing strategies to support companies in the responsible development of safer nanomaterial use. Noting the low prevalence of nanoparticle usage, there would still seem to be time to introduce necessary protection methods in a proactive and cost effective way in Swiss industry. But if the predicted "nano-revolution" becomes true, now is the time to take action.

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The safe and responsible development of engineered nanomaterials (ENM), nanotechnology-based materials and products, together with the definition of regulatory measures and implementation of "nano"-legislation in Europe require a widely supported scientific basis and sufficient high quality data upon which to base decisions. At the very core of such a scientific basis is a general agreement on key issues related to risk assessment of ENMs which encompass the key parameters to characterise ENMs, appropriate methods of analysis and best approach to express the effect of ENMs in widely accepted dose response toxicity tests. The following major conclusions were drawn: Due to high batch variability of ENMs characteristics of commercially available and to a lesser degree laboratory made ENMs it is not possible to make general statements regarding the toxicity resulting from exposure to ENMs. 1) Concomitant with using the OECD priority list of ENMs, other criteria for selection of ENMs like relevance for mechanistic (scientific) studies or risk assessment-based studies, widespread availability (and thus high expected volumes of use) or consumer concern (route of consumer exposure depending on application) could be helpful. The OECD priority list is focussing on validity of OECD tests. Therefore source material will be first in scope for testing. However for risk assessment it is much more relevant to have toxicity data from material as present in products/matrices to which men and environment are be exposed. 2) For most, if not all characteristics of ENMs, standardized methods analytical methods, though not necessarily validated, are available. Generally these methods are only able to determine one single characteristic and some of them can be rather expensive. Practically, it is currently not feasible to fully characterise ENMs. Many techniques that are available to measure the same nanomaterial characteristic produce contrasting results (e.g. reported sizes of ENMs). It was recommended that at least two complementary techniques should be employed to determine a metric of ENMs. The first great challenge is to prioritise metrics which are relevant in the assessment of biological dose response relations and to develop analytical methods for characterising ENMs in biological matrices. It was generally agreed that one metric is not sufficient to describe fully ENMs. 3) Characterisation of ENMs in biological matrices starts with sample preparation. It was concluded that there currently is no standard approach/protocol for sample preparation to control agglomeration/aggregation and (re)dispersion. It was recommended harmonization should be initiated and that exchange of protocols should take place. The precise methods used to disperse ENMs should be specifically, yet succinctly described within the experimental section of a publication. 4) ENMs need to be characterised in the matrix as it is presented to the test system (in vitro/ in vivo). 5) Alternative approaches (e.g. biological or in silico systems) for the characterisation of ENMS are simply not possible with the current knowledge. Contributors: Iseult Lynch, Hans Marvin, Kenneth Dawson, Markus Berges, Diane Braguer, Hugh J. Byrne, Alan Casey, Gordon Chambers, Martin Clift, Giuliano Elia1, Teresa F. Fernandes, Lise Fjellsbø, Peter Hatto, Lucienne Juillerat, Christoph Klein, Wolfgang Kreyling, Carmen Nickel1, and Vicki Stone.