Incorporation and washout of n-3 PUFA after high dose intravenous and oral supplementation in healthy volunteers.

BACKGROUND & AIMS: Although the physiological effects of n-3 polyunsaturated fatty acids (n-3PUFA) are generally thought to require several weeks of exposure to allow their incorporation into plasma membranes, intravenous (IV) n-3PUFA attenuate the cardiovascular and neuroendocrine response to stress within 3 h. Whether oral n-3 PUFA exert similar early effects remains unknown. OBJECTIVE: To assess whether acute IV or short term oral n-3PUFA administration reproduces the metabolic effects of long term oral supplements during exercise, and how it relates to their incorporation into platelets and red blood cells (RBC) membranes. DESIGN: Prospective single center open label study in 8 healthy subjects receiving a 3-h infusion of 0.6 g/kg body weight n-3PUFA emulsion, followed one week later by an oral administration of 0.6 g/kg over 3 consecutive days. Maximal power output (cycling exercise), maximal heart rate (HR), blood lactate at exhaustion, and platelet function were measured at baseline and after IV or 3-day oral supplementation; platelet and RBC membrane composition were assessed until 15 days after n-3PUFA administration. RESULTS: Both IV and oral n-3PUFA significantly decreased maximal HR (-6% and -5%), maximal power output (-10%) and peak blood lactate (-47% and -52%) Platelet function tests were unchanged. The EPA and DHA membrane contents of RBC and platelets increased significantly, but only to 1.7-1.9% of fatty acid content. CONCLUSION: The cardiovascular and metabolic effects of n-3 PUFA during exercise occur already within 1-3 days of exposure, and may be unrelated to changes in membranes composition. Effects occur within hours of administration and are unrelated to lipid membrane composition. Trial registered at clinicaltrials.gov as NCT00516178.

Liberación de mercurio por parte de las obturaciones de amalgama dental: tipo, cantidad, método de determinación y posibles efectos adversos

Las obturaciones dentales de amalgama constituyen la fuente principal de exposición permanente de bajo nivel al vapor de mercurio (Hg°) y al mercurio inorgánico (Hg(II)) para la población general. La dosis de mercurio absorbido procedente de la amalgama es de 2.7 ¿g/día/persona para una cantidad promedio de 7.4 obturaciones. Si esta cantidad consistiera enteramente en mercurio inorgánico (Hg(II)), estaría muy por debajo de la cifra de 15 ¿g/día para una persona de 65 kg que la OMS considera como ingesta tolerable de mercurio inorgánico. En el caso de una exposición permanente a la misma cantidad, pero de vapor de mercurio (Hg0), se obtendría una concentración de 0.18 mg/m3 que puede compararse con la concentración de referencia de la EPA de 0.3 mg/m3 o con el nivel de riesgo mínimo de la ATSDR de 0.2 mg/m3. Varios estudios clínicos longitudinales y aleatorizados han evaluado la relación entre la concentración urinaria de mercurio y la exposición al mercurio procedente de las obturaciones dentales de amalgama en niños, particularmente vulnerables al Hg0, así como los posibles efectos neurológicos de tal exposición. La concentración promedio de mercurio en orina en los niños tratados con amalgama, con un promedio de 18,7 superficies obturadas, aumentó hasta un pico de 3.2 ¿g/L a los 2 años de iniciado el tratamiento y a los 7 años de seguimiento había descendido hasta los niveles basales y no se detectó ninguna alteración en las distintas exploraciones de monitorización neuropsicológica. De la misma manera, diversas investigaciones epidemiológicas no han aportado ninguna evidencia del papel de la amalgama en la posible causa o exacerbación de trastornos degenerativos como la esclerosis lateral amiotrófica, la enfermedad de Alzheimer, la esclerosis múltiple o el Parkinson. La extracción de las obturaciones de amalgama produce un aumento transitorio de los niveles de mercurio en sangre inmediatamente después de extraer las obturaciones de amalgama, pero de pequeña magnitud y que se normaliza a los 100 días, por lo que el efecto del dique de goma tiene una relevancia toxicológica menor. La conclusión de esta revisión es que la amalgama dental continúa siendo un excelente material de obturación.

Bioelectrochemical Treatment of Contaminated Groundwater

To remove these pollutants from groundwater, different technologies can be used. Currently, the Environmental Protection Agency (EPA) considers ion exchange, reverse osmosis and reverse electrodialysis to be effective methods for the decrease of their concentrations, below their limit in drinking water. These technologies have some drawbacks, such as low selectivity towards the target pollutant, high energy or chemicals requirements, and the generation of waste brine (pollutants are separated from water, not treated), which require an additional treatment. Bio Electro Chemical Systems (BES) could fill this niche

El Acceso a la universidad en el estado español en 2009: los condicionantes en el acceso y la dimensión transicional

Presentamos una actualización del análisis del acceso a la universidad española a partir de datos del módulo de la EPA 2009, un módulo que nos permite analizar también a los jóvenes independizados. Identificamos los principales condicionantes considerados y construimos un modelo de elección, añadiendo además aspectos biográficos en el análisis para mostrar la importancia de la trayectoria vital del joven en el acceso a la universidad. Las desigualdades de acceso están presentes en 2009 y tienen un impacto en la equidad social.

Intravenous fish oil blunts the physiological response to endotoxin in healthy subjects

Résumé L'administration par voie orale d'acides gras polyinsaturés de type ω-3 contenus dans l'huile de poisson exerce des effets bénéfiques sur la réponse métabolique et inflammatoire chez des sujets sains soumis à une injection d'endotoxine. Ce modèle expérimental a été validé pour l'investigation clinique. Il simule un sepsis et induit une réponse comparable à un état grippal, accompagné de modifications métaboliques et inflammatoires. L'objectif de cette étude est de déterminer les effets de l'huile de poisson administré par voie intraveineuse sur la réponse à l'endotoxine chez le sujet sain. L'hypothèse est qu'il sera possible de réduire le temps de latence en comparaison avec la voie orale. Pour ce faire, nous avons inclut dans une étude prospective randomisée 16 volontaires sains âgés de 16 à 35 ans et les avons répartis en 2 groupes : l'un recevant une émulsion lipidique contenant les acides gras polyinsaturés EPA et DHA et l'autre, sans traitement, constituant le groupe contrôle. Huit sujets reçoivent une perfusion continue de 0.5g/kg d'huile de poisson durant 6h, 48h et 24h avant la journée test. Lors de cette journée test, tous les volontaires ont reçu une dose d'endotoxine (2mg/kg) au temps t0. Les paramètres vitaux sont monitorés et enregistrés : fréquence cardiaque, respiratoire, pression artérielle, saturation artérielle en oxygène, ainsi que température. Des prises de sang sont effectuées à intervalles réguliers pour déterminer 1) l'incorporation membranaire des thrombocytes en EPA et DHA ; 2) le taux plasmatique d'hormones (insulin, glucagon, cortisol, ACTH et catécholamines), de marqueurs inflammatoires (TNF-α, IL-6, hsCRP), ainsi que de substrats énergétiques (glucose, lactate, acides gras libres et triglycérides). La dépense énergétique est déterminée par calorimétrie indirecte. L'analyse statistique est effectuée par analyse de variance (ANOVA). Les résultats montrent une incorporation significative de EPA et DHA au niveau membranaire des thrombocytes. L'huile de poisson induit une atténuation significative de la réponse neuro-endocrinienne et inflammatoire en réponse à l'injection d'endotoxine avec diminution de la fièvre (-0.7°C), ainsi que du taux plasmatique ,d'ACTH (-68%), TNF-α (-63%) et de noradrénaline (-%) dans le groupe huile de poisson. En conclusion, cette étude montre que la supplémentation de 2 doses d'huile de poisson par voie intraveineuse modifie la composition phospholipidique des membranes des thrombocytes et diminue la réaction inflammatoire et neuroendocrinienne en réponse à l'endotoxine. Ces résultats positifs ouvrent la perspective d'une supplémentation parentérale préopératoire en acides gras polyinsaturés ω-3 pour diminuer le stress lié à la chirurgie majeure.

Blunting the response to endotoxin in healthy sujects : effects of various dose of intravenous fish oil

Enjeux et contexte La recherche de cette dernière décennie sur les acides gras n-3 PUFA contenus dans l'huile de poisson a montré que ceux-ci, et particulièrement l'ΕΡΑ et le DHA, avaient des propriétés anti¬inflammatoires et anti arythmiques puissantes, potentiellement utiles chez les septiques et « cardiaques ». Les mécanismes sous-jacents sont nombreux, incluant l'incorporation des acides gras dans les membranes de phopholipides, la réduction de la production de médiateurs pro-inflammatoires (prostaglandines, leukotrienes, thromboxane), l'augmentation de la production de résolvines et protectines dérivées du DHA, et la régulation de voies de signalisation cellulaire. Cependant, les doses de n-3 PUFA utilisées dans les études cliniques et chez le sujet sain avant le travail de Yann-Karim Pittet étaient nettement supérieures aux doses nutritionnelles de l'ordre de 5-8 g/j par voie orale ou 1 g/kg par voie intraveineuse. De plus, la voie entérale avait la réputation de nécessiter plusieurs jours à semaines de traitement avant d'aboutir à une incorporation d'acides gras membranaire suffisante pour avoir un impact clinique; quant au temps minimal requis pour obtenir cet effet par voie IV, il était inconnu. Depuis, le développement d'émulsions lipidiques intraveineuses destinées à la nutrition parentérale a permis d'imaginer l'administration de prétraitements IV rapides. Pour les étudier, notre laboratoire a développé un modèle d'endotoxine (LPS d'E.Coli) qui mime les réponses physiologique, endocrinienne et biologique du sepsis chez le sujet sain, utilisant des doses de 2 ng/kg IV. Les réponses sont totalement réversibles en 8 heures. Dans le but de réduire à la fois la dose de lipides et le temps de perfusion, ce travail a étudié l'influence de 3 doses dégressives de n-3 PUFA sur les réponses à l'endotoxine, et sur l'incorporation membranaire de ces acides gras. Méthodes Etude prospective chez 3 groupes consécutifs de sujets sains soumis à un challenge d'endotoxine. Intervention : perfusions d'huile de poisson (0.5 et 0.2 g/kg de n-3 PUFA, Omegaven® 10%) ou placebo, administrées en 3 heures ou en 1 heure, soit le jour avant ou le jour-même du test d'endotoxine. Mesures : variables physiologiques (T°, fc, tension artérielle, calorimétrie indirecte) Laboratoire - prises de sang à T0, 60, 120 et 360 min après l'injection de LPS: TNF-α, hs-CRP, hormones de stress, composition en acides gras des membranes plaquettaires. Statistiques Les résultats ont été rapportés en moyennes et écarts types. Des aires sous la courbe (AUC) ont été calculées avec la méthode des parallélépipèdes pour toutes les variables déterminées de manière répétée. L'effet du temps a été exploré par des two-way ANOVA pour mesures répétées. Les comparaisons post-hoc ont été réalisées avec des tests de Dunnett's ou de Scheffe. Les modifications de composition membranaires ainsi que les AUC ont été analysées par des tests non-paramétriques (Kruskal-Wallis). Résultats Après LPS, la température, les concentrations d'ACTH et TNF-α ont augmenté dans les 3 groupes. Ces réponse ont été significativement atténuées (p<0.0001) par l'huile de poisson comparé à ce que nous avions observé dans le groupe contrôle de Pluess et al (ICM 2007). Les concentrations les plus faibles d'ACTH, de TNF-α, et les AUC les plus basses des températures, ont été observées après une dose unique de 0.2 g/kg de n-3 PUFA administrée 1 heure avant le LPS. Par contre, l'incorporation membranaire d'EPA est dose-dépendante. Conclusions Sachant que la réponse à l'endotoxine est reproductible, cette étude montre que 3 doses différentes d'huile de poisson atténuent de manière différente cette réponse. La perfusion de 0.2 g/kg administrée juste avant l'endotoxine s'est avérée la plus efficace à atténuer la réponse fébrile, les cytokines et les hormones de stress, suggérant une capture de l'endotoxine par l'émulsion lipidique qui se surajoute aux effets systémiques et membranaires.

Field Evaluation of Pavement Marking Materials, MLR-79-02, 1979

Pavement marking materials other than conventional paint must be evaluated as environmental standards become more restrictive. The new EPA classification for solvents states that all oil paints are photochemically reactive and, therefore, contribute to smog. This will eventually result in the elimination of organic solvents from all paints, which may occur in Iowa by 1985. The Special Investigations Section of the Office of Materials field reviewed all urban and rural applications of pavement marking materials in the spring of 1979. The field review consisted of a visual estimation of percent marking missing, percent satisfactory, and percent non-satisfactory; reflective readings by ERMA; and notation of special conditions which may have impacted performance. ERMA was not effective in evaluating the reflective quality of pavement marking materials. No pavement marking materials evaluated have been successful enough to date to totally replace conventional painting methods.

Planning for Water Quality, July 2012

The following document serves two purposes. First, the Environmental Protection Agency (EPA) requires a state to develop an approved Non-point Source Management Plan (NPSMP or Plan) that encompasses the nine key elements, described in full in Appendix A, to be eligible for federal Clean Water Act Section 319 funding. Second, the Plan serves as a representation of Iowa’s vision, goals, objectives and potential action steps to reduce non-point source pollution and improve water quality over the next five to ten years. This plan is not intended to be, nor should it be, limited to the Department of Natural Resources or Iowa’s Section 319 Program, but rather reflects the collective efforts and intents of the core partners and stakeholder groups that worked together to develop the goals identified herein and programmatic means of achieving those goals.

1003-001 Williamson Pond Final Report

Williamson Pond is a 26-acre publicly owned lake located about 2 miles east of the town of Williamson, in Lucas County. It has a watershed area of 1,499 acres. It has been managed since 1976 by the Lucas County Conservation Board (while still under state ownership) for fishing, boating, hunting, picnicking and other passive uses. Designated uses are Class AI, primary contact, and Class B (LW) aquatic life. Williamson Pond is on the 2004 EPA 303(d) List of Impaired Waters. A Total Maximum Daily Load (TMDL) for turbidity and nutrients at Williamson Pond was prepared by IDNR in 2005 and approved by EPA in 2006. The TMDL set reduction targets for both suspended sediment and phosphorus. The Williamson Pond Watershed Management Plan has provided the local work group and partners with information to develop and implement strategies to improve and protect water quality. These strategies are based on a three phase approach that will ultimately lead the removal of Williamson Pond from the Impaired Waters List. The goals identified in this proposal (Phase I) will reduce sediment and phosphorus delivery by 453 tons and 589 pounds annually. The Lucas County SWCD has and will continue to provide leadership on the Williamson Pond Project and has secured the partnerships necessary to address water quality problems and hired a part-time project coordinator to manage, implement, and oversee all activities pertaining to this proposal.

Health consultation : Sub-Slab Gas and Air Sampling Data Alcoa – Davenport Works CERCLIS No. IAD005270160 Riverdale, Scott County, Iowa (2005)

The U.S. Environmental Protection Agency (EPA), the Alcoa – Davenport Works Facility (Alcoa), and concerned citizens and community leaders of Riverdale, Iowa requested the Iowa Department of Public Health (IDPH) Hazardous Waste Site Health Assessment Program to evaluate the health impacts of exposures to volatile organic vapors detected within residences located immediately to the west of the Alcoa property. This health consultation addresses inhalation exposure to individuals that may have occupied the currently vacant residences in which the air sampling was completed.

Health consultation : Former Chamberlain Manufacturing Site 550 Esther Street Waterloo, Black Hawk County, Iowa (2012)

The United States Environmental Protection Agency (EPA) has requested the Iowa Department of Public Health (IDPH) to evaluate the health impacts associated with exposure to contaminants of concern that have been found at the former Chamberlain Manufacturing Site. The EPA has been involved in the investigation and remediation of the Former Chamberlain Manufacturing Site since 2005. As part of these investigative activities, on-site soil sampling and both on-and off-site groundwater sampling has been completed. In addition, sub-slab soil gas, indoor air, and ambient air sampling at properties located near the Former Chamberlain Manufacturing Site has been completed. This health consultation addresses potential health risks to the public from exposure to the soil, groundwater and potential vapors within homes or buildings at or near the Former Chamberlain Manufacturing Site. The information in this health consultation was current at the time of writing. Data that emerges later could alter this document’s conclusions and recommendations.

Health consultation : Des Moines (Ex) Ordnance Site Landfill and Lagoon Complex Prairie Trail Development Site [Ankeny] (2012)

The Prairie Trail Development Area is located in the southern portion of Ankeny, Iowa. This development area is located in an area that was formally occupied by the Des Moines Ordnance Plant. The Des Moines Ordnance Plant was constructed for the production and testing of small arms munitions for use during World War II. The Landfill and Lagoon Complex was utilized for disposal of wastes from the ordnance plant and also from various entities that utilized the site property until 1991. The United States Environmental Protection Agency (EPA) is verseeing the cleanup of the Landfill and Lagoon Complex. A portion of the remainder of the site property had been used for burning of scrap explosives, the storage and disposal of chemicals, a disposal pond, testing of products, and various munitions manufacturing activities. The Iowa Department of Natural Resources (IDNR) is overseeing the cleanup of this remaining portion of the site property. The Iowa Department of Public Health has been contacted by residents within the Prairie Trail Development Area and by individuals that have an interest in relocating to the Prairie Trail Development Area. These residents are concerned with any environmental contamination that will be left after site remedial activities are completed. These residents want to know if any remaining environmental contamination will adversely impact their health or the health of their families.

09012-009 Little River Lake Watershed Final Report

Little River Lake watershed is a 13,305 acre subwatershed of Little River. The 788 acre lake was listed as a 303d impaired water body in 2008 due to elevated turbidity and algae levels. The Decatur SWCD has prioritized water quality protection efforts within the Little River Lake watershed because 1) portions of this watershed has been identified as the primary contributor of sediment and nutrients to Little River Lake, which provides an essential source of drinking water for Decatur County and the Southern Iowa Rural Water Association; 2) the watershed provides exemplary education and project interpretation opportunities due to its proximity to Little River Lake Recreation Area, and 3) by using targeted and proven soil conservation practices to address water quality deficiencies the probability of successfully attenuating soil erosion and ameliorating water quality impairments is enhanced. The specific goals of this proposal are to: 1. reduce annual sediment, and phosphorous delivery to the lake by 11,280 tons and 14,664 lbs., respectively, via applications of conservation practices on targeted agricultural land; 2. delist the lake as an EPA 303d impaired water body via water quality enhancement; 3. obtain a “Full Support” status for the lake’s aquatic life and recreational use; 4. reduce potable water treatment costs (minimum 50% cost reduction) associated with high suspended solid levels; and 5. restore a viable sport-fish population, thereby bolstering tourism and the economy. To achieve timely project implementation the Decatur SWCD has cooperated with the IDNR Watershed Improvement Section, Fisheries Bureau, and IDALS-DSC to assess extant water quality and watershed conditions, coalesced a diverse team of committed partners and secured matching funding from multiple sources.

1017-011 Tuttle Lake Watershed Final Report

The Tuttle Lake Watershed is approximately 125,000 acres and Tuttle Lake itself is 2,270 acres; 5,609 acres of the watershed lies in Iowa territory within Emmet County. It is a sub-watershed of the larger East Fork Des Moines River Watershed, also referred to as Hydrologic Unit Code 07100003. For the purpose of this document, grant money is only being applied for the project implementation in the Iowa portion of the Tuttle Lake Watershed. Tuttle Lake was placed on the 2002 EPA 303(d) Impaired Waters List due to a “very large population of suspended algae and very high levels of inorganic turbidity.” In 2004, the Iowa Department of Natural Resources (IDNR) completed a Total Maximum Daily Load (TMDL) study on Tuttle Lake and found excess sediment and phosphorus levels being the primary pollutants causing the algae and turbidity impairment. Although two point sources were located in Minnesota, IDNR determined that the influx of nutrients is likely from agricultural runoff and re-suspension of lake sediment. The condition of Tuttle Lake is such that the reduction of sediment, nutrients [phosphorus and nitrogen] and pathogens is the primary objective. To achieve that objective, wetlands will be constructed in this first phase to reduce the delivery of nitrogen, phosphorus, and sediment to Tuttle Lake.

07025-010 College Creek Watershed Final Report

With this application, the College Creek sub-watershed in Ames represents both regional collaboration and locally directed action to improve an Iowa watershed. Already completed watershed assessment identified more than 4000 tons/yr of sediment delivered from within the Ames city limits due to degraded stream conditions. The water quality enhancement goal of this project is reducing sediment delivery specifically from unstable streambanks and degrading stream channels on College Creek, one of 4 Ames tributaries to Squaw Creek. The project will also redirect urban storm water runoff into engineered infiltration systems, intercepting it from storm drains entering College Creek. This application builds on storm water runoff demonstration projects and research already funded in the College Creek sub-watershed by EPA Region 7 and Iowa DNR. Public outreach, one of the key elements of this project, is built into every phase from engineering design feedback to construction. Innovative neighborhood learning circles are utilized to educate residents and share public feedback with project engineers to ensure that project elements are both technically appropriate and socially acceptable. All practices proposed in this project -stream stabilization, storm water infiltration, and neighborhood learning circle techniques-have already been successfully demonstrated in the College Creek sub-watershed by the City of Ames in partnership with Iowa State University.