Cause-Specific Long-Term Mortality in Survivors of Childhood Cancer in Switzerland: A Population Based Study.

Survivors of childhood cancer have a higher mortality than the general population. We describe cause-specific long-term mortality in a population-based cohort of childhood cancer survivors. We included all children diagnosed with cancer in Switzerland (1976-2007) at age 0-14 years, who survived ≥5 years after diagnosis and followed survivors until December 31, 2012. We obtained causes of death (COD) from the Swiss mortality statistics and used data from the Swiss general population to calculate age-, calendar year- and sex-standardized mortality ratios (SMR), and absolute excess risks (AER) for different COD, by Poisson regression. We included 3'965 survivors and 49'704 person years at risk. Of these, 246 (6.2%) died, which was 11 times higher than expected (SMR 11.0). Mortality was particularly high for diseases of the respiratory (SMR 14.8) and circulatory system (SMR 12.7), and for second cancers (SMR 11.6). The pattern of cause-specific mortality differed by primary cancer diagnosis, and changed with time since diagnosis. In the first 10 years after 5-year survival, 78.9% of excess deaths were caused by recurrence of the original cancer (AER 46.1). Twenty-five years after diagnosis, only 36.5% (AER 9.1) were caused by recurrence, 21.3% by second cancers (AER 5.3) and 33.3% by circulatory diseases (AER 8.3). Our study confirms an elevated mortality in survivors of childhood cancer for at least 30 years after diagnosis with an increased proportion of deaths caused by late toxicities of the treatment. The results underline the importance of clinical follow-up continuing years after the end of treatment for childhood cancer. This article is protected by copyright. All rights reserved.

Regional-Scale Mean Copepod Concentration Indicates Relative Abundance of North Atlantic Right Whales

Management plans to reduce human-caused deaths of North Atlantic right whales Eubalaena glacialis depend, in part, on knowing when and where right whales are likely to be found. Local environmental conditions that influence movements of feeding right whales, such as ultra-dense copepod patches, are unpredictable and ephemeral. We examined the utility of using the regional-scale mean copepod concentration as an indicator of the abundance of right whales in 2 critical habitats off the northeastern coast of the United States: Cape Cod Bay and Great South Channel. Right whales are usually found in Cape Cod Bay during the late winter and early spring, and in the Great South Channel during the late spring and early summer. We found a significant positive relationship between mean concentration of the copepod Calanus finmarchicus in the western Gulf of Maine and the frequency of right whale sightings in the Great South Channel. In Cape Cod Bay we found a significant positive relationship between the mean concentration of other copepods (largely Pseudocalanus spp. and Centropages spp.) and the frequency of right whale sightings. This information could be used to further our understanding of the environmental factors that drive seasonal movement and aggregation of right whales in the Gulf of Maine, and it offers a tool to resource managers and modelers who seek to predict the movements of right whales based upon the concentration of copepods.

Effects of Study Area Size on Geographic Characterizations of Health Events: Prostate Cancer Incidence in Southern New England, USA, 1994-1998.

ABSTRACT : BACKGROUND : We consider how representations of geographic variation in prostate cancer incidence across Southern New England, USA may be affected by selection of study area and/or properties of the statistical analysis. METHOD : A spatial scan statistic was used to monitor geographic variation among 35,167 incident prostate cancer cases diagnosed in Massachusetts, Connecticut and Rhode Island from 1994 to 1998, in relation to the 1990 populations of men 20+ years of age living in that region. Results from the combined-states analysis were compared to those from single-states. Impact of scanning procedures set to examine up to 50% or no more than10% of at-risk populations also was evaluated. RESULTS : With scanning set to 50%, 5 locations in the combined-states analysis were identified with markedly distinct incidence rates. Fewer than expected cases were estimated for nearly all Connecticut, Rhode Island and West Central Massachusetts, whereas census tracts on and around Cape Cod, and areas of Southwestern Connecticut and adjacent to greater Boston were estimated to have yielded more than expected incidence. Results of single-state analyses exhibited several discrepancies from the combined-states analysis. More conservative scanning found many more locations with varying incidence, but discrepancies between the combined- and single-state analysis were fewer. CONCLUSION : It is important to acknowledge the conditional nature of spatial analyses and carefully consider whether a true cluster of events is identified or artifact stemming from selection of study area size and/or scanning properties.

Specimen sapientiae Indorum veterum : id est liber ethico-politicus pervetustus ...

[Bearb.: Ibn al-Muqaffa]. Nunc primum Graece ex mss. cod. Holsteiniano prodit, cum versione nova Latina, opera Sebast. Gottofr. Starkii. Aus dem Arab. ins Griech. übers. von Simeon

Compendium historiae philosophicae antiquae, sive Philosophumena, quae sub Origenis nomine circumferuntur

Hippolytus Sanctus ; Ex. cod. Bibliothecae Mediceae a Jacobo Gronovio ... iam vero recogn. et notis uberioribus ill. passimque corr. a Joanne Christophoro Wolfio ...

Bench-scale evaluation of the activated sludge process for treatment of a high -strength chemical plant wastewater

A bench-scale treatability study was conducted on a high-strength wastewater from a chemical plant to develop an alternative for the existing waste stabilization pond treatment system. The objective of this study was to determine the treatability of the wastewater by the activated sludge process and, if treatable, to determine appropriate operating conditions, and to evaluate the degradability of bis(2-chloroethyl)ether (Chlorex) and benzene in the activated sludge system. Four 4-L Plexi-glass, complete mixing, continuous flow activated sludge reactors were operated in parallel under different operating conditions over a 6-month period. The operating conditions examined were hydraulic retention time (HRT), sludge retention time (SRT), nutrient supplement, and Chlorex/benzene spikes. Generally the activated sludge system treating high-strength wastewater was stable under large variations of organic loading and operating conditions. At an HRT of 2 days, more than 90% removal efficiency with good sludge settleability was achieved when the organic loading was less than 0.4 g BOD$\sb5$/g MLVSS/d or 0.8 g COD/g MLVSS/d. At least 20 days of SRT was required to maintain steady operation. Phosphorus addition enhanced the performance of the system especially during stressed operation. On the average, removals of benzene and Chlorex were 73-86% and 37-65%, respectively. In addition, the low-strength wastewater was treatable by activated sludge process, showing more than 90% BOD removal at a HRT of 0.5 days. In general, the sludge had poor settling characteristics. The aerated lagoon process treating high-strength wastewater also provided significant organic reduction, but did not produce an acceptable effluent concentration. ^

Mesozooplankton size data from the fjord branch Kapisigdlit located in the Godthaabsfjord system, West Greenland, 2010

Sampling was conducted from March 24 to August 5 2010, in the fjord branch Kapisigdlit located in the inner part of the Godthåbsfjord system, West Greenland. The vessel "Lille Masik" was used during all cruises except on June 17-18 where sampling was done from RV Dana (National Institute for Aquatic Resources, Denmark). A total of 15 cruises (of 1-2 days duration) 7-10 days apart was carried out along a transect composed of 6 stations (St.), spanning the length of the 26 km long fjord branch. St. 1 was located at the mouth of the fjord branch and St. 6 was located at the end of the fjord branch, in the middle of a shallower inner creek . St. 1-4 was covering deeper parts of the fjord, and St. 5 was located on the slope leading up to the shallow inner creek. Mesozooplankton was sampled by vertical net tows using a Hydrobios Multinet (type Mini) equipped with a flow meter and 50 µm mesh nets or a WP-2 net 50 µm mesh size equipped with a non-filtering cod-end. Sampling was conducted at various times of day at the different stations. The nets were hauled with a speed of 0.2-0.3 m s**-1 from 100, 75 and 50 m depth to the surface at St. 2 + 4, 5 and 6, respectively. The content was immediately preserved in buffered formalin (4% final concentration). All samples were analyzed in the Plankton sorting and identification center in Szczecin (www.nmfri.gdynia.pl). Samples containing high numbers of zooplankton were split into subsamples. All copepods and other zooplankton were identified down to lowest possible taxonomic level (approx. 400 per sample), length measured and counted. Copepods were sorted into development stages (nauplii stage 1 - copepodite stage 6) using morphological features and sizes, and up to 10 individuals of each stage was length measured.

Antropología de las relaciones transnacionales en las regiones de frontera. Hegemonía y resistencia en el Sistema Mundo (2010/2012) “HANUIN VIII”.. 16H312

La presente investigación forma parte de un ciclo integrado por siete investigaciones precedentes, cuyas referencias están incluidas en el apartado de antecedentes. Dichas investigaciones cuentan con los informes de avance y finales aprobados. Su objetivo principal es conocer y describir la complejidad de la región de frontera estudiada (Triple Frontera entre Argentina, Brasil y Paraguay) ), el núcleo duro de las relaciones directas, y las acciones propias, que desde la región, protagonizan organizaciones y movimientos sociales en relación a las cada vez mas intensas amenazas de intervención militar/”humanitaria”, por parte del poder hegemónico de Estados Unidos y la intensificación de los controles estatales nacionales que responden a las presiones internacionales. ¿Qué lugar ocupa en las estrategias de la hegemonía imperial esta región? y ¿cuales son las respuestas locales tanto en acciones como en representaciones?. El proyecto posee las siguientes sub-áreas con sus respectivos coordinadores a) Centro de estudios de la población paraguaya en Argentina (CEDAPPA); b) Centro de Estudios de Antropología y Derecho (mediante un convenio de cooperación e investigadores adscriptos) y c) Área de estudios de Historia Regional El presente proyecto es la novena etapa de una secuencia que incluye ocho proyectos precedentes del programa de incentivos. Todos, menos el último, fueron bianuales y el octavo, que finalizó en el 2012, trianual. La nómina completa de estos proyectos es la siguiente: Proyectos pertenecientes al Programa de Incentivos: "Integración Regional Fronteriza: sectores vulnerables frente al impacto global. Políticas y acciones alternativas" UNaM, Sec. de Investigación FHCS. 1994-96.Informes de avance y final aprobados. Código: H-16-001 “Hanuin I” (“Hacer nuestra la integración”) En este proyecto se adoptó este nombre general que luego se repitió en toda la secuencia y que proviene de un lema formulado en un encuentro de movimientos sociales de los cuatro países del MERCOSUR.. “Estrategias de una red de movimientos sociales argentinos, brasileños y paraguayos en el marco de la integración regional fronteriza. Factores de cohesión y de conflicto”. Sec. de Invs. y Posgrado, 1996/1998.Informes de avance y final aprobados. Código: H-16-033, “Hanuin II”. “Los movimientos sociales en la integración regional. Relaciones transfronterizas de solidaridad y lucha. La cuestión agraria integral. Secretaría de Investigación y Postgrado, FHYCS, UNaM.1999-2000 Código: H-16-034, “Hanuin III”. “Interacciones transfronterizas, procesos socioculturales emergentes en el contexto de la integración. Los movimientos sociales ante el impacto del Mercosur. (Arg., Br. y Par.) (2001-2002). Código: H-16- 035 “Hanuin IV”. 4 “Procesos transfronterizos complejos: El caso de la Triple Frontera. Movimientos y organizaciones sociales, grupos “bajo sospecha”, control y políticas públicas. (2003-2005). Código: H-16- 135., “Hanuin V”. “Hegemonías y resistencias en el sistema mundo. Estados y procesos transfronterizos. El caso de la Triple frontera. (2006-2007) Código: H-16-198. Incluye el proyecto de Voluntariado CEDAPA. Convenio entre la UNaM (FHYCS) y la Comisión de Verdad y Justicia del Paraguay “Hanuin VI”. “Antropología de los procesos transfronterizos: La Triple Frontera en el sistema mundo. Complejidad y resistencia regional” Incluye el proyecto de Voluntariado CEDAPA. Convenio entre la UNaM (FHYCS) y la Comisión de Verdad y Justicia del Paraguay. (2008-2009). 16-H-245. “Hanuin VII”. “ Antropología de las relaciones transnacionales en las regiones de frontera. Hegemonía y resistencia en el sistema mundo” Incluye el proyecto CEDAPPA, Historia Regional, convenio con el CEDEAD. (2010-2012) “Hanuin VIII”,cod. 16-H-312 La inclusión de esta iformación procura ofrecer a los posibles evaluadores datos sobre la secuencia que hoy finaliza su etapa 2010-2012, pero que se continuará en el proyecto Hanuin IX que ya fue presentado. Tambien se abre una nueva instancia con la formulación de un programa que convierte a los subproyectos en proyectos.. Dicho programa lleva por título: “Investigaciónes interdisciplinarias sobre las regiones de frontera. Estado, sistemas socioculturales y terrorios” (2013/15). Una de las conclusiones del proyecto que reseñamos, fue presisamente, la necesidad de ampliar las líneas de investigación con equipos de mayor autonomía que puedan, además, atender las exigencias de creciente incorporación de auxiliares, becarios, tesistas, investigadores adscriptos o invitados.

Egg production, hatching, faecal pellet production of Calanus finmarchicus in the North Atlantic

The samples were collected using a T-80 net (375 µm mesh size) equipped with a non-filtering cod-end in the North Atlantic during the G.O. Sars Trans-Atlantic cruise in 2013. Within 15-30 minutes after the recovery, 20 Calanus finmarchicus females were sorted out under microscope in ice chilled petri dishes and incubated individually in 600 ml polycarbonate culture bottles resulting in 20 replicate measurements. The bottles were filled with 50 µm screened seawater originated from 6 m water depth. The samples were incubated upright in thermoroom for 24 hours at the surface temperature (3°C). After the samples had been filtered (40 µm filter), female prosome length, egg as well as pellet abundance were determined. Subsequently, eggs from six females were incubated in petri dishes at 5°C. After 4 days, the number of nauplii and eggs were counted in order to calculate hatching success.

Faecal pellet production of copepoda collected in water depth up to 30 meters in the eastern Mediterranean Sea in Oktober 2008 during SES_GR2

Mesozooplankton is collected by vertical tows within the Black sea water body mass layer in the NE Aegean, using a WP-2 200 µm net equipped with a large non-filtering cod-end (10 l). Macrozooplankton organisms are removed using a 2000 µm net. A few unsorted animals (approximately 100) are placed inside several glass beaker of 250 ml filled with GF/F or 0.2 µm Nucleopore filtered seawater and with a 100 µm net placed 1 cm above the beaker bottom. Beakers are then placed in an incubator at natural light and maintaining the in situ temperature. After 1 hour pellets are separated from animals and placed in separated flasks and preserved with formalin. Pellets are counted and measured using an inverted microscope. Animals are scanned and counted using an image analysis system. Carbon- Specific faecal pellet production is calculated from a) faecal pellet production, b) individual carbon: Animals are scanned and their body area is measured using an image analysis system. Body volume is then calculated as an ellipsoid using the major and minor axis of an ellipse of same area as the body. Individual carbon is calculated from a carbon- total body volume of organisms (relationship obtained for the Mediterranean Sea by Alcaraz et al. (2003) divided by the total number of individuals scanned and c) faecal pellet carbon: Faecal pellet length and width is measured using an inverted microscope. Faecal pellet volume is calculated from length and width assuming cylindrical shape. Conversion of faecal pellet volume to carbon is done using values obtained in the Mediterranean from: a) faecal pellet density 1,29 g cm**3 (or pg µm**3) from Komar et al. (1981); b) faecal pellet DW/WW=0,23 from Elder and Fowler (1977) and c) faecal pellet C%DW=25,5 Marty et al. (1994).

Caracteres físico-químicos de efluentes de fábricas de aceite de oliva : Mendoza (Argentina)

La producción de aceite de oliva genera distintos subproductos entre los cuales el efluente o alpechín representa un serio problema mediambiental. En los países productores el alpechín es un residuo muy contaminante debido a su elevada composición orgánica, sus efectos inhibitorios y la tendencia de sus componentes a sufrir oxidación biológica. Estas características y la estacionalidad de su producción dificultan su eliminación. La industria del aceite de oliva está actualmente en expansión en Argentina. En Mendoza, dicha actividad tiene una gran tradición y un impacto ambiental considerable. El objetivo de este trabajo fue analizar los caracteres físico- químicos de los efluentes de fábricas de aceite oliva en Mendoza (Argentina) para conocer la realidad de la industria local y rever las especificaciones legales para efluentes. Los efluentes de dos fábricas fueron evaluados en tres puntos de muestreo: agua de entrada al proceso, salida de la fábrica y pileta de deposición final de los efluentes. Se analizó el contenido de iones, pH, conductividad eléctrica, DBO y DQO. Los resultados obtenidos permiten concluir que las características del efluente dependen del método de extracción utilizado y la eventual dilución con agua de lavado. La calidad del agua subterránea utilizada en el proceso no es un factor determinante para lograr un efluente fácilmente tratable. El problema medioambiental que se plantea es la producción de un efluente con alto contenido orgánico, salino y bajo pH, caracteres que impiden su vuelco en cursos de agua superficial o red de cloacas, por no cumplir con los requisitos indicados en la normativa vigente. Por lo tanto, las fábricas elaboradoras de aceite de oliva serán las encargadas de que dichos efluentes reciban un adecuado proceso de depuración que permita su eliminación o reutilización.

Calidad del agua en el área regadía del Río Mendoza (Argentina)

El río Mendoza conforma el oasis norte que es el más importante de la provincia. El crecimiento urbano ha avanzado sobre áreas originalmente agrícolas, rodeando la red de canales y desagües, que también recibe los desagües pluviales urbanos, producto de tormentas convectivas. La actividad antropogénica utiliza el recurso para bebida, saneamiento, riego, recreación, etc., y vuelca sus excedentes a la red, contaminándola. Para conocer la calidad del agua de esta cuenca se seleccionaron, estratégicamente, 15 sitios de muestreo: 3 a lo largo del río y a partir del dique derivador Cipolletti (R_I a R_III), 5 en la red de canales (C_I a C_V) y 7 ubicados en los colectores de drenaje (D_I a D_VII). Se realizaron los siguientes análisis físico-químicos y microbiológicos; en el río y en la red de canales: conductividad eléctrica, temperatura, pH, aniones y cationes (cálculo de RAS), oxígeno disuelto (OD), sólidos sedimentables, demanda química de oxígeno (DQO), bacterias aerobias mesófilas (BAM), coliformes totales y fecales y metales pesados. En la red de drenaje sólo se realizaron los cuatro primeros. Los resultados de los análisis, se incorporaron a una base de datos y se sometieron a un análisis estadístico descriptivo e inferencial. Este último consistió en la aplicación de diversas pruebas en busca de posibles diferencias entre los sitios de muestreo, para cada variable respuesta, a un α = 0.05. Se realizó el análisis de la varianza de efectos fijos y de efectos aleatorios y se probaron los supuestos de homocedasticidad y de normalidad de los errores. En el caso de violación de los supuestos, se utilizó la prueba de Kruskal- Wallis. Se compararon los siguientes sitios de muestreo entre sí: ríos, R_I-canales y drenajes. Se concluyó que hay un aumento significativo de la salinidad y la sodicidad en R_II, que los cambios de calidad ocurridos entre R_II y R_III podrían deberse al aporte de otras aguas. Con respecto a la comparación de los parámetros entre la cabeza del sistema (R_I) y la red de canales se puede decir que los aportes realizados por los escurrimientos urbanos ubicados hacia el oeste del canal Cacique Guaymallén, sumados a los vuelcos de Campo Espejo (detectados en C_II), incrementan significativamente la salinidad (+55 %) y sodicidad del agua (+95 %) respecto del punto R_I, aunque el valor de sodicidad sigue siendo bajo. También se han encontrado incrementos de salinidad (+80 %), de DQO (+1159 %) y BAM (+2873 %) con lógica disminución de OD (-58 %) en el punto C_V (canal Auxiliar Tulumaya) respecto del punto R_I, ocasionados por aportes urbanos (Gran Mendoza) sumados a la carga contaminante del canal Pescara. Los metales pesados no presentan grandes diferencias entre sitios de muestreo.

Remediation of feedlot effluents using aquatic plants

Feedlots have increased in several regions of Argentina, particularly in the Pampas. The absence of adequate treatments of the effluents produced in these establishments creates serious problems to the society. Phytoremediation can be defined as inexpensive and environmentally sustainable strategy used to remove pollutants by plants. The aim of this study was to evaluate the remediation potential of two macrophyte species (Eichhornia crassipes and Hydrocotyle ranunculoides) on a feedlot effluent. This effluent was treated with these species for 31 days. Control and macrophyte treatments decreased dissolved inorganic nitrogen (DIN), Kjeldahl nitrogen (Kj N), biological oxygen demand (BOD), chemical oxygen demand (COD), total dissolved salts (TDS), total phosphorus (TP), Pb, Zn and Cr levels. At macrophyte treatments, relatively constant pH levels were kept and decreased EC and TDS values were obtained compared to control, mitigating the release of contaminants and potential greenhouse gases to the atmosphere. Moreover, significant increases in biomass were obtained, being higher in E. crassipes. The results allow concluding that the presence of aquatic plants increases the removal rates of nutrients, organic matter and heavy metals from wastewater in approximately 10-17 days for a feedlot effluent with high organic load.

Stomach content of ringed seals (Pusa hispida) obtained from the Northeast Greenland area

The diet of ringed seals (Pusa hispida) from coastal and offshore areas of Northeast Greenland was determined by identifying, to the lowest taxonomic limit possible, all hard-part contents from the gastrointestinal tract of 51 seals sampled (2002-2004) in spring (April to June, N = 35) and autumn (September to October, N = 16). The autumn diet was characterized by high numbers of Parathemisto libellula, and the spring diet was comprised primarily of polar cod (Boreogadus saida), with few invertebrates consumed. The coastal seal diet samples had a diverse fish prey composition (during both the spring and autumn), whereas the open water seals had eaten mostly crustaceans with P. libellula being most abundant. The sample sizes from the various locations and seasons were not large enough to explore age-class effects on diet in addition. Similar to earlier studies, this study suggests that the ringed seal is a generalist that exploits prey based on availability, with a few key species dominating the diet in an area at least on a seasonal basis.