71 research outputs found

    Q fever presenting as miliary pneumonia: Case imagery and differential diagnosis

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    Abstract: Case/imagery description: A 56-year-old immunocompetent male consulted for one month of relapsing fever, moderate dyspnea, non-productive cough, headaches, and myalgias. Past medical history was unremarkable except for exposure to a variety of livestock carcasses. A computed tomographic scan revealed innumerable randomly distributed 1-3mm micronodules. Initial diagnostic workup including bronchoalveolar lavage (BAL) was inconclusive. STUDY QUESTIONS: Is this miliary pneumonia? What diagnosis must initially be considered? In this specific case with negative BAL analysis/cultures, what would your differential diagnosis be? Is Q fever a possibility

    Étude de cohorte sur les fonctions neurocomportementales de travailleurs 14 ans aprùs la fin de l'exposition au manganùse

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    L'inhalation de particules de manganĂšse (Mn) peut causer des effets neurotoxiques qui se manifestent par des altĂ©rations des fonctions neurocomportementales, nommĂ©ment des symptĂŽmes psychologiques et des dĂ©ficits cognitifs et moteurs. Une premiĂšre Ă©tude fut menĂ©e en 1990 sur les fonctions neurocomportementales de travailleurs exposĂ©s au Mn dans une usine de production d'alliages ferro-Mn et silico-Mn; des hommes cols bleus non-exposĂ©s au Mn servirent de groupe de comparaison (rĂ©fĂ©rents). Pour chaque travailleur, l'exposition aux poussiĂšres et aux fumĂ©es de Mn dans l'air au moment de l'Ă©tude a Ă©tĂ© estimĂ©e et un indice d'exposition cumulĂ©e sur toute la durĂ©e d'emploi dans l'usine a Ă©tĂ© calculĂ©. L'usine a arrĂȘtĂ© ses opĂ©rations quelques mois aprĂšs la fin de cette Ă©tude, mais cette fermeture n'Ă©tait pas liĂ©e aux rĂ©sultats de l'Ă©tude. Dans la premiĂšre partie de la thĂšse, l'objectif Ă©tait d'examiner l'effet modificateur de l'Ăąge dans les altĂ©rations neurocomportementales. L'analyse des donnĂ©es appariĂ©es (74 paires) a montrĂ© que les diffĂ©rences de scores aux tests neurocomportementaux entre les travailleurs exposĂ©s au Mn et les rĂ©fĂ©rents (ces diffĂ©rences reprĂ©sentant l'effet du Mn) augmentaient significativement avec l'Ăąge pour la mĂ©moire, la concentration, la flexibilitĂ© cognitive, la stabilitĂ© des mains et la sensibilitĂ© tactile. L'Ăąge n'Ă©tait pas associĂ© Ă  la concentration de Mn dans l'air au moment de l'Ă©tude, ni Ă  l'exposition cumulĂ©e, indiquant que les dĂ©ficits plus prononcĂ©s les travailleurs plus ĂągĂ©s ne peuvent pas ĂȘtre expliquĂ©s par une exposition supĂ©rieure chez ces derniers. Ces rĂ©sultats indiquent que, Ă  exposition Ă©gale, les travailleurs plus ĂągĂ©s sont davantage affectĂ©s que les plus jeunes par les effets du Mn sur certaines fonctions nerveuses. Pour la seconde partie de la thĂšse, nous avons menĂ© une Ă©tude de suivi auprĂšs de 78 anciens employĂ©s de l'usine et 81 rĂ©fĂ©rents afin de vĂ©rifier le degrĂ© de rĂ©versibilitĂ© ou d'aggravation des atteintes neurofonctionnelles 14 ans aprĂšs la fin de l'exposition. Les travailleurs ayant Ă©tĂ© exposĂ©s au Mn ainsi que les rĂ©fĂ©rents ayant acceptĂ© de participer Ă  l'Ă©tude de suivi ont complĂ©tĂ© une batterie de tests similaire Ă  celle utilisĂ©e en 1990. Nous avons Ă©mis l'hypothĂšse que ces atteintes s'aggraveraient avec le temps, et qu'elles seraient donc plus marquĂ©es au moment du suivi (2004) que lors de l'Ă©tude initiale (1990). En effet, la progression des signes neurologiques a Ă©tĂ© rapportĂ©e lors d'Ă©tudes longitudinales portant sur des travailleurs gravement intoxiquĂ©s au Mn, ainsi que des travailleurs exposĂ©s Ă  d'autres substances neurotoxiques, notamment les solvants organiques et le plomb. Globalement, les rĂ©sultats indiquent que la performance pour plusieurs des tests que les travailleurs exposĂ©s avaient moins bien rĂ©ussi en 1990 n'Ă©tait pas diffĂ©rente entre les exposĂ©s et les rĂ©fĂ©rents en 2004. NĂ©anmoins, les dĂ©ficits de vitesse motrice (membres supĂ©rieurs) observĂ©s en 1990 Ă©taient toujours prĂ©sents en 2004. Par ailleurs, les travailleurs ayant Ă©tĂ© exposĂ©s au Mn et qui Ă©taient ĂągĂ©s de plus de 45 ans lorsque l'exposition a cessĂ©e ont obtenu une performance significativement infĂ©rieure aux rĂ©fĂ©rents d'Ăąge similaire Ă  trois tests de flexibilitĂ© cognitive. Ensuite, pour certains tests moteurs et cognitifs, la performance Ă©tait significativement et inversement associĂ©e Ă  l'exposition cumulĂ©e au Mn. En somme, les rĂ©sultats rĂ©vĂšlent deux trajectoires possibles : i) un maintien des dĂ©ficits, ou ii) une rĂ©cupĂ©ration des fonctions, particuliĂšrement pour les moins exposĂ©s. L'hypothĂšse d'aggravation des dĂ©ficits n'a donc pas Ă©tĂ© retenue, mais un autre suivi de la cohorte Ă  un Ăąge plus avancĂ© (ici, l'Ăąge moyen Ă©tait 57 ans au moment du suivi) serait souhaitable pour connaĂźtre l'Ă©volution des fonctions neurocomportementales en fonction de l'exposition au cours du vieillissement. Ensuite, un questionnaire portant sur les symptĂŽmes neuropsychiatriques a Ă©tĂ© ajoutĂ© Ă  la batterie de tests administrĂ©e en 2004 afin d'examiner plus profondĂ©ment ce domaine neurofonctionnel. En effet, certaines donnĂ©es dans la littĂ©rature indiquent que les questionnaires de symptĂŽmes neuropsychiatriques sont particuliĂšrement sensibles aux effets du Mn sur le systĂšme nerveux. Le rĂ©sultat des analyses a montrĂ© une relation significative entre l'exposition cumulĂ©e au Mn et les scores aux Ă©chelles Somatisation, DĂ©pression, AnxiĂ©tĂ© et HostilitĂ©. Les travailleurs dans les deux tertiles supĂ©rieurs d'exposition cumulĂ©e avaient un risque significatif d'avoir un score Ă©levĂ© aux Ă©chelles HostilitĂ©, DĂ©pression et AnxiĂ©tĂ©. Ces rĂ©sultats suggĂšrent que l'exposition cumulĂ©e au Mn est associĂ©e Ă  la gravitĂ© des symptĂŽmes neuropsychiatriques jusqu'Ă  14 ans aprĂšs la fin de l'exposition. Nos travaux ont mis en Ă©vidence la vulnĂ©rabilitĂ© des travailleurs plus ĂągĂ©s aux effets neurotoxiques du Mn. Le suivi de cette cohorte de travailleurs plusieurs annĂ©es aprĂšs la fin de l'exposition a montrĂ© un portrait complexe de changements des atteintes neurofonctionnelles, oĂč certaines atteintes sont partiellement rĂ©versibles, particuliĂšrement chez les moins exposĂ©s, alors que d'autres atteintes persistent, particuliĂšrement chez les plus ĂągĂ©s. Nous estimons que la possibilitĂ© de rĂ©cupĂ©ration neurofonctionnelle aprĂšs la fin de l'exposition devrait encourager les mesures de rĂ©duction des concentrations de Mn dans les milieux de travail concernĂ©s par ce risque. En mĂȘme temps, la persistance de certaines atteintes associĂ©es Ă  l'exposition au Mn, et cela jusqu'Ă  14 ans aprĂšs la fin de l'exposition, montre l'importance de prĂ©venir celles-ci. Il semble que l'exposition cumulĂ©e Ă  ce mĂ©tal soit dĂ©terminante dans l'apparition des signes de neurotoxicitĂ©. La concentration de Mn dans l'air de l'usine oĂč Ă©taient employĂ©s les travailleurs Ă  l'Ă©tude ici respectait la norme d'exposition, norme toujours en vigueur aujourd'hui. L'exposition cumulĂ©e au Mn Ă©tait en deçà de 100 mg/m3 x annĂ©e et a nĂ©anmoins Ă©tĂ© associĂ©e Ă  des effets nĂ©fastes durables sur certaines fonctions neurocomportementales. Or, un travailleur exposĂ© Ă  la valeur maximale lĂ©galement admise pendant 35 ans aurait un indice d'exposition cumulĂ©e encore plus Ă©levĂ©, soit de 175 mg/m3 x annĂ©e, ce qui suggĂšre que la norme actuelle d'exposition ne protĂšge probablement pas la santĂ© de tous les travailleurs.\ud ______________________________________________________________________________ \ud MOTS-CLÉS DE L’AUTEUR : manganĂšse, travailleurs, neurotoxique, neurocomportemental, exposition cumulĂ©

    Manganese in Drinking Water: Bouchard Responds

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    Hair Manganese and Hyperactive Behaviors: Pilot Study of School-Age Children Exposed through Tap Water

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    BACKGROUND: Neurotoxic effects are known to occur with inhalation of manganese particulates, but very few data are available on exposure to Mn in water. We undertook a pilot study in a community in QuĂ©bec (Canada) where naturally occurring high Mn levels were present in the public water system. Our objective was to test the hypothesis that greater exposure to Mn via drinking water would be reflected in higher Mn content in hair which, in turn, would be associated with increased level of hyperactive behaviors. METHODS: Forty-six children participated in the study, 24 boys and 22 girls, 6–15 years of age (median, 11 years). Their homes received water from one of two wells (W) with different Mn concentrations: W1: mean 610 ÎŒg/L; W2: mean 160 ÎŒg/L. The Revised Conners’ Rating Scale for parents (CPRS-R) and for teachers (CTRS-R) were administered, providing T-scores on the following subscales: Oppositional, Hyperactivity, Cognitive Problems/Inattention, and ADHD Index. RESULTS: Children whose houses were supplied by W1 had higher hair Mn (MnH) than those supplied by W2 (mean 6.2 ± 4.7 ÎŒg/g vs. 3.3 ± 3.0 ÎŒg/g, p = 0.025). MnH was significantly associated with T-scores on the CTRS-R Oppositional (p = 0.020) and Hyperactivity (p = 0.002) subscales, after adjustment for age, sex, and income. All children with Oppositional and Hyperactivity T-scores ≄ 65 had MnH > 3.0 ÎŒg/g. CONCLUSIONS: The findings of this pilot study are sufficiently compelling to warrant more extensive investigations into the risks of Mn exposure in drinking water

    Determinants of urinary concentrations of dialkyl phosphates among pregnant women in Canada — Results from the MIREC study

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    AbstractOrganophosphate (OP) insecticides are commonly used in agriculture. Their use decreased in recent years as they were gradually replaced by other pesticides, but some OPs are still among the insecticides most used in Canada. Exposure to elevated levels of OPs during pregnancy has been associated with adverse birth outcomes and poorer neurodevelopment in children. The objective of the present study was to examine the relationship between the concentrations of OP pesticides urinary dialkyl phosphate (DAP) metabolites and various factors that are potential sources of exposure or determinants of DAP levels. In the Maternal-Infant Research on Environmental Chemicals (MIREC) Study, six DAPs were measured in 1st trimester urine samples of 1884 pregnant women living in Canada. They were grouped into sums of dimethyl alkyl phosphates (DMAP) and diethyl alkyl phosphates (DEAP) for statistical analysis. We found that 93% of women had at least one DAP detected in their urine. Geometric means (GM) of specific gravity-corrected levels for urine dilution were 59 (95% CI 56–62) and 21 (95% CI 20–22) nmol/L for DMAP and DEAP, respectively. The following characteristics were significantly associated with higher urinary concentrations of DMAP or DEAP: higher education, nulliparous, normal pre-pregnancy body mass index, non-smoker, not fasting at sampling, winter season at sampling, and early and late day collection times. Dietary items that were significantly related with higher urinary concentrations included higher intake of citrus fruits, apple juice, sweet peppers, tomatoes, beans and dry peas, soy and rice beverages, whole grain bread, white wine and green and herbal teas. This study indicates that exposure to these compounds is quasi-ubiquitous. The factors associated with greater DAP levels identified here could be useful to regulatory agencies for risk analysis and management. However, some exposure misclassification might occur due to the single DAP measurement available, and to the presence of preformed DAPs in the environment

    Prenatal Exposure to Organophosphate Pesticides and IQ in 7-Year-Old Children

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    Context: Organophosphate (OP) pesticides are neurotoxic at high doses. Few studies have examined whether chronic exposure at lower levels could adversely affect children’s cognitive development

    Manganese concentrations in drinking water from villages near banana plantations with aerial mancozeb spraying in Costa Rica: Results from the Infants' Environmental Health Study (ISA)

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    AbstractElevated manganese (Mn) in drinking water has been reported worldwide. While, naturally occurring Mn in groundwater is generally the major source, anthropogenic contamination by Mn-containing fungicides such as mancozeb may also occur. The main objective of this study was to examine factors associated with Mn and ethylenethiourea (ETU), a degradation product of mancozeb, in drinking water samples from villages situated near banana plantations with aerial spraying of mancozeb. Drinking water samples (n = 126) were obtained from 124 homes of women participating in the Infants' Environmental Health Study (ISA, for its acronym in Spanish), living nearby large-scale banana plantations. Concentrations of Mn, iron (Fe), arsenic (As), lead (Pb), cadmium (Cd) and ethylenethiourea (ETU), a degradation product of mancozeb, were measured in water samples. Only six percent of samples had detectable ETU concentrations (limit of detection (LOD) = 0.15 Όg/L), whereas 94% of the samples had detectable Mn (LOD = 0.05 Όg/L). Mn concentrations were higher than 100 and 500 Όg/L in 22% and 7% of the samples, respectively. Mn was highest in samples from private and banana farm wells. Distance from a banana plantation was inversely associated with Mn concentrations, with a 61.5% decrease (95% CI: −97.0, −26.0) in Mn concentrations for each km increase in distance. Mn concentrations in water transported with trucks from one village to another were almost 1000 times higher than Mn in water obtained from taps in houses supplied by the same well but not transported, indicating environmental Mn contamination. Elevated Mn in drinking water may be partly explained by aerial spraying of mancozeb; however, naturally occurring Mn in groundwater, and intensive agriculture may also contribute. Drinking water risk assessment for mancozeb should consider Mn as a health hazard. The findings of this study evidence the need for health-based World Health Organization (WHO) guidelines on Mn in drinking water

    Neurobehavioral Function in School-Age Children Exposed to Manganese in Drinking Water

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    Background: Manganese neurotoxicity is well documented in individuals occupationally exposed to airborne particulates, but few data are available on risks from drinking-water exposure. Objective: We examined associations of exposure from concentrations of manganese in water and hair with memory, attention, motor function, and parent- and teacher-reported hyperactive behaviors. Methods: We recruited 375 children and measured manganese in home tap water (MnW) and hair (MnH). We estimated manganese intake from water ingestion. Using structural equation modeling, we estimated associations between neurobehavioral functions and MnH, MnW, and manganese intake from water. We evaluated exposure–response relationships using generalized additive models. Results: After adjusting for potential confounders, a 1-SD increase in log10 MnH was associated with a significant difference of –24% (95% CI: –36, –12%) SD in memory and –25% (95% CI: –41, –9%) SD in attention. The relations between log10 MnH and poorer memory and attention were linear. A 1-SD increase in log10 MnW was associated with a significant difference of –14% (95% CI: –24, –4%) SD in memory, and this relation was nonlinear, with a steeper decline in performance at MnW > 100 ÎŒg/L. A 1-SD increase in log10 manganese intake from water was associated with a significant difference of –11% (95% CI: –21, –0.4%) SD in motor function. The relation between log10 manganese intake and poorer motor function was linear. There was no significant association between manganese exposure and hyperactivity. Conclusion: Exposure to manganese in water was associated with poorer neurobehavioral performances in children, even at low levels commonly encountered in North America. Citation: Oulhote Y, Mergler D, Barbeau B, Bellinger DC, Bouffard T, Brodeur ME, Saint-Amour D, Legrand M, SauvĂ© S, Bouchard MF. 2014. Neurobehavioral function in school-age children exposed to manganese in drinking water. Environ Health Perspect 122:1343–1350; http://dx.doi.org/10.1289/ehp.130791

    Lead Exposure and Behavior among Young Children in Chennai, India

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    Background: Lead exposure has long been associated with deficits in IQ among children. However, few studies have assessed the impact of lead on specific domains of behavior and cognition. Objective: We evaluated the associations between lead and different domains of neurobehavior and their relative sensitivity to lead. Methods: We determined blood lead levels using a LeadCare instrument in 756 children 3–7 years of age attending pre- and elementary schools in Chennai, India. Anxiety, social problems, inattention, hyperactivity, and attention deficit hyperactivity disorder (ADHD), as well as executive function were assessed in children by their schoolteachers using Conners’ Teacher Rating Scales-39, Conners’ ADHD/Diagnostic and Statistical Manual for Mental Disorders, 4th Edition Scales (CADS), and the Behavior Rating Inventory of Executive Function questionnaires, with higher scores denoting worse behavior. Analyses were carried out using multivariate generalized estimating equations with comparisons of outcome Z-scores to assess the relative strengths of the associations between log-blood lead and the different domains of behavior. Results: Mean blood lead level was 11.4 ± 5.3 ÎŒg/dL. Blood lead was associated with higher anxiety (ÎČ = 0.27, p = 0.01), social problems (ÎČ = 0.20, p = 0.02), and higher scores in the ADHD index (ÎČ = 0.17; p = 0.05). The effect estimate was highest for global executive function (ÎČ = 0.42; p < 0.001). Conclusions: Higher blood lead levels in this population of young children is associated with increased risk of neurobehavioral deficits and ADHD, with executive function and attention being particularly vulnerable domains to the effects of lead

    Intellectual Impairment in School-Age Children Exposed to Manganese from Drinking Water

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    ABSTRACT: BACKGROUND: Manganese is an essential nutrient, but in excess it can be a potent neurotoxicant. Despite the common occurrence of manganese in groundwater, the risks associated with this source of exposure are largely unknown. OBJECTIVES: Our first aim was to assess the relations between exposure to manganese from drinking water and children's intelligence quotient (IQ). Second, we examined the relations between manganese exposures from water consumption and from the diet with children's hair manganese concentration. METHODS: This cross-sectional study included 362 children 6-13 years of age living in communities supplied by groundwater. Manganese concentration was measured in home tap water (MnW) and children's hair (MnH). We estimated manganese intake from water ingestion and the diet using a food frequency questionnaire and assessed IQ with the Wechsler Abbreviated Scale of Intelligence. RESULTS: The median MnW in children's home tap water was 34 microg/L (range, 1-2,700 microg/L). MnH increased with manganese intake from water consumption, but not with dietary manganese intake. Higher MnW and MnH were significantly associated with lower IQ scores. A 10-fold increase in MnW was associated with a decrease of 2.4 IQ points (95% confidence interval: -3.9 to -0.9; p < 0.01), adjusting for maternal intelligence, family income, and other potential confounders. There was a 6.2-point difference in IQ between children in the lowest and highest MnW quintiles. MnW was more strongly associated with Performance IQ than Verbal IQ. CONCLUSIONS: The findings of this cross-sectional study suggest that exposure to manganese at levels common in groundwater is associated with intellectual impairment in children
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