898 resultados para Tall fringe-rush
Resumo:
This data set contains three time series of measurements of soil carbon (particular and dissolved) from the main experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below). In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. 1. Particulate soil carbon: Stratified soil sampling was performed every two years since before sowing in April 2002 and was repeated in April 2004, 2006 and 2008 to a depth of 30 cm segmented to a depth resolution of 5 cm giving six depth subsamples per core. Total carbon concentration was analyzed on ball-milled subsamples by an elemental analyzer at 1150°C. Inorganic carbon concentration was measured by elemental analysis at 1150°C after removal of organic carbon for 16 h at 450°C in a muffle furnace. Organic carbon concentration was calculated as the difference between both measurements of total and inorganic carbon. 2. Particulate soil carbon (high intensity sampling): In one block of the Jena Experiment soil samples were taken to a depth of 1 m (segmented to a depth resolution of 5 cm giving 20 depth subsamples per core) with three replicates per block ever 5 years starting before sowing in April 2002. Samples were processed as for the more frequent sampling. 3. Dissolved organic carbon: Suction plates installed on the field site in 10, 20, 30 and 60 cm depth were used to sample soil pore water. Cumulative soil solution was sampled biweekly and analyzed for dissolved organic carbon concentration by a high TOC elemental analyzer. Annual mean values of DOC are provided.
Resumo:
This data set contains soil carbon measurements (Organic carbon, inorganic carbon, and total carbon; all measured in dried soil samples) from the main experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below). In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. Soil sampling and analysis: Stratified soil sampling was performed in April 2006 to a depth of 30 cm. Three samples per plot were taken using a split tube sampler with an inner diameter of 4.8 cm (Eijkelkamp Agrisearch Equipment, Giesbeek, the Netherlands). Sampling locations were less than 30 cm apart from sampling locations in 2002. Soil samples were segmented into 5 cm depth segments in the field (resulting in six depth layers) and made into composite samples per depth. Subsequently, samples were dried at 40°C. All soil samples were passed through a sieve with a mesh size of 2 mm. Because of much higher proportions of roots in the soil, samples in years after 2002 were further sieved to 1 mm according to common root removal methods. No additional mineral particles were removed by this procedure. Total carbon concentration was analyzed on ball-milled subsamples (time 4 min, frequency 30 s**-1) by an elemental analyzer at 1150°C (Elementaranalysator vario Max CN; Elementar Analysensysteme GmbH, Hanau, Germany). We measured inorganic carbon concentration by elemental analysis at 1150°C after removal of organic carbon for 16 h at 450°C in a muffle furnace. Organic carbon concentration was calculated as the difference between both measurements of total and inorganic carbon.
Resumo:
This data set contains measurements of plant height: vegetative height (non-flowering indviduals) and regenerative height (flowering individuals) in 2002 from the Main Experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below). In the Main Experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. In 2002, plant height was recorded twice a year: in late June and just before biomass harvest during peak standing biomass in late August. For 3 target plant individuals (if present) per sown species from the central area of the plots, vegetative height (non-flowering indviduals) and regenerative height (flowering individuals) were measured as stretched height. Provided are the indivdiual measurements and the mean over the measured plants per plot (in June) and the mean over the measured plants per plot (in August).
Resumo:
La política social y el mercado de trabajo son dimensiones del sistema social mutuamente implicadas en las sociedades industriales capitalistas. Sin embargo, una interpretación apresurada sobre el mundo social podría opacar los procesos que hacen que en un grupo de la población se yuxtapongan: una inserción laboral precaria dentro del mercado de trabajo informal junto con la (re) construcción de ese grupo como sujeto-objeto de políticas sociales. El artículo tiene por propósito problematizar las representaciones dominantes sobre el trabajo y su relación con las prácticas de organización de los hogares, considerando que en su interior la dimensión laboral se articula con otros recursos (provenientes de las políticas sociales). De modo más específico, el objetivo se orienta a la descripción y análisis de prácticas y representaciones sobre la situaci162n ocupacional de jefas/es y cónyuges que realizan actividades laborales en la informalidad de subsistencia. Se plantea como hipótesis exploratoria que en el período actual las condiciones de trabajo y representaciones de los trabajadores ocupados en ese tipo de actividades expresarían la existencia de un tipo de informalidad fuertemente segregada respecto de las actividades productivas, un en un contexto de crecimiento del empleo. También se sostiene que las formas bajo las cuales estas inserciones laborales se articulan con los planes sociales (como un nivel específico de política social) evidenciarían el carácter de la contribución estatal a la reproducción de las condiciones de vida de los trabajadores insertos en este tipo de informalidad. Los hallazgos presentados constituyen un avance de investigación sobre la reproducción de la marginalidad urbana en el Conurbano Bonaerense. Parte del trabajo de campo se realizó durante el año 2008, en un barrio del Partido de Almirante Brown. Se organizaron dos grupos de discusión: uno con mujeres perceptoras de planes y otro con hombres que realizaban changas como actividad principal. Con el objeto de aportar datos acerca de las condiciones materiales de los hogares, se aplicó un cuestionario a los participantes. Junto con esta información, se analizaron registros de campo tomados en observaciones realizadas en diversos espacios del barrio
Resumo:
This data set contains measurements of dissolved organic carbon in samples of soil water collected from the main experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below). In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. In April 2002 glass suction plates with a diameter of 12 cm, 1 cm thickness and a pore size of 1-1.6 mm (UMS GmbH, Munich, Germany) were installed in depths of 10, 20, 30 and 60 cm to collect soil solution. The sampling bottles were continuously evacuated to a negative pressure between 50 and 350 mbar, such that the suction pressure was about 50 mbar above the actual soil water tension. Thus, only the soil leachate was collected. Cumulative soil solution was sampled biweekly and analyzed for dissolved organic carbon concentration by a high TOC elemental analyzer (Elementar Analysensysteme GmbH, Hanau, Germany). Samples were analyzed as soon as possible and stored at 4°C if necessary. Often in summer, no free soil solution was available for collection, especially in the upper soil layers. Annual mean values of measured biweekly concentrations of dissolved organic carbon are provided.
Resumo:
This data set contains measurements of dissolved organic carbon in samples of soil water collected from the main experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below). In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. In April 2002 glass suction plates with a diameter of 12 cm, 1 cm thickness and a pore size of 1-1.6 mm (UMS GmbH, Munich, Germany) were installed in depths of 10, 20, 30 and 60 cm to collect soil solution. The sampling bottles were continuously evacuated to a negative pressure between 50 and 350 mbar, such that the suction pressure was about 50 mbar above the actual soil water tension. Thus, only the soil leachate was collected. Cumulative soil solution was sampled biweekly and analyzed for dissolved organic carbon concentration by a high TOC elemental analyzer (Elementar Analysensysteme GmbH, Hanau, Germany). Samples were analyzed as soon as possible and stored at 4°C if necessary. Often in summer, no free soil solution was available for collection, especially in the upper soil layers. Annual mean values of measured biweekly concentrations of dissolved organic carbon are provided.
Resumo:
This data set contains measurements of dissolved organic carbon in samples of soil water collected from the main experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below). In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. In April 2002 glass suction plates with a diameter of 12 cm, 1 cm thickness and a pore size of 1-1.6 mm (UMS GmbH, Munich, Germany) were installed in depths of 10, 20, 30 and 60 cm to collect soil solution. The sampling bottles were continuously evacuated to a negative pressure between 50 and 350 mbar, such that the suction pressure was about 50 mbar above the actual soil water tension. Thus, only the soil leachate was collected. Cumulative soil solution was sampled biweekly and analyzed for dissolved organic carbon concentration by a high TOC elemental analyzer (Elementar Analysensysteme GmbH, Hanau, Germany). Samples were analyzed as soon as possible and stored at 4°C if necessary. Often in summer, no free soil solution was available for collection, especially in the upper soil layers. Annual mean values of measured biweekly concentrations of dissolved organic carbon are provided.
Resumo:
La política social y el mercado de trabajo son dimensiones del sistema social mutuamente implicadas en las sociedades industriales capitalistas. Sin embargo, una interpretación apresurada sobre el mundo social podría opacar los procesos que hacen que en un grupo de la población se yuxtapongan: una inserción laboral precaria dentro del mercado de trabajo informal junto con la (re) construcción de ese grupo como sujeto-objeto de políticas sociales. El artículo tiene por propósito problematizar las representaciones dominantes sobre el trabajo y su relación con las prácticas de organización de los hogares, considerando que en su interior la dimensión laboral se articula con otros recursos (provenientes de las políticas sociales). De modo más específico, el objetivo se orienta a la descripción y análisis de prácticas y representaciones sobre la situaci162n ocupacional de jefas/es y cónyuges que realizan actividades laborales en la informalidad de subsistencia. Se plantea como hipótesis exploratoria que en el período actual las condiciones de trabajo y representaciones de los trabajadores ocupados en ese tipo de actividades expresarían la existencia de un tipo de informalidad fuertemente segregada respecto de las actividades productivas, un en un contexto de crecimiento del empleo. También se sostiene que las formas bajo las cuales estas inserciones laborales se articulan con los planes sociales (como un nivel específico de política social) evidenciarían el carácter de la contribución estatal a la reproducción de las condiciones de vida de los trabajadores insertos en este tipo de informalidad. Los hallazgos presentados constituyen un avance de investigación sobre la reproducción de la marginalidad urbana en el Conurbano Bonaerense. Parte del trabajo de campo se realizó durante el año 2008, en un barrio del Partido de Almirante Brown. Se organizaron dos grupos de discusión: uno con mujeres perceptoras de planes y otro con hombres que realizaban changas como actividad principal. Con el objeto de aportar datos acerca de las condiciones materiales de los hogares, se aplicó un cuestionario a los participantes. Junto con esta información, se analizaron registros de campo tomados en observaciones realizadas en diversos espacios del barrio
Resumo:
Phytoliths (siliceous plant microfossils) have been recovered from Cenozoic sediments (c. 34 to 17 Ma) in the CRP-2/2A and CRP-3 drillholes cored off Cape Roberts, Victoria Land Basin, Antarctica. The phytolith assemblages are sparse, but well-preserved and dominated by spherical forms similar to those of modern trees or shrubs. Rare phytoliths comparable to modern grass forms are also present. However, due to the paucity of phytolith data, any interpretations made are necessarily tentative. The assemblages of CRP-2/2A and the upper c. 250 m of CRP-3 are interpreted as representing a predominantly woody vegetation, including Nothofagus and Libocedrus with local areas of grass in the more exposed locations. A cool climate is interpreted to have prevailed throughout both cores. However, beneath c. 250 metres below sea floor in CRP-3, the dominant woody vegetation is supplemented by pockets of Palmae, ?Proteaceae and 'warm' climate grasses. This association represents vegetation growth in sheltered, moist sites - possibly north-facing mid-slopes or the coastal fringe. It may also represent remnant vegetation that grew in moist, temperate conditions during the Middle to Late Eocene, previously interpreted from the Southern McMurdo Sound erratics and lower part of the CIROS-1 drillhole. The phytolith analysis compares well to the terrestrial palynomorph record from both cores and provides additional independent taxonomic and climatic interpretations.
Resumo:
This data set contains aboveground community biomass (Sown plant community, Weed plant community, Dead plant material, and Unidentified plant material; all measured in biomass as dry weight) and species-specific biomass from the sown species of the main experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below). In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. Aboveground community biomass was harvested twice in 2003 just prior to mowing (during peak standing biomass in late May and in late August) on all experimental plots of the main experiment. This was done by clipping the vegetation at 3 cm above ground in four rectangles of 0.2 x 0.5 m per large plot. The location of these rectangles was assigned prior to each harvest by random selection of coordinates within the core area of the plots (i.e. the central 10 x 15 m). The positions of the rectangles within plots were identical for all plots. The harvested biomass was sorted into categories: individual species for the sown plant species, weed plant species (species not sown at the particular plot), detached dead plant material (i.e., dead plant material in the data file), and remaining plant material that could not be assigned to any category (i.e., unidentified plant material in the data file). All biomass was dried to constant weight (70°C, >= 48 h) and weighed. Sown plant community biomass was calculated as the sum of the biomass of the individual sown species. The data for individual samples and the mean over samples for the biomass measures on the community level are given. Overall, analyses of the community biomass data have identified species richness as well as functional group composition as important drivers of a positive biodiversity-productivity relationship.
Resumo:
La política social y el mercado de trabajo son dimensiones del sistema social mutuamente implicadas en las sociedades industriales capitalistas. Sin embargo, una interpretación apresurada sobre el mundo social podría opacar los procesos que hacen que en un grupo de la población se yuxtapongan: una inserción laboral precaria dentro del mercado de trabajo informal junto con la (re) construcción de ese grupo como sujeto-objeto de políticas sociales. El artículo tiene por propósito problematizar las representaciones dominantes sobre el trabajo y su relación con las prácticas de organización de los hogares, considerando que en su interior la dimensión laboral se articula con otros recursos (provenientes de las políticas sociales). De modo más específico, el objetivo se orienta a la descripción y análisis de prácticas y representaciones sobre la situaci162n ocupacional de jefas/es y cónyuges que realizan actividades laborales en la informalidad de subsistencia. Se plantea como hipótesis exploratoria que en el período actual las condiciones de trabajo y representaciones de los trabajadores ocupados en ese tipo de actividades expresarían la existencia de un tipo de informalidad fuertemente segregada respecto de las actividades productivas, un en un contexto de crecimiento del empleo. También se sostiene que las formas bajo las cuales estas inserciones laborales se articulan con los planes sociales (como un nivel específico de política social) evidenciarían el carácter de la contribución estatal a la reproducción de las condiciones de vida de los trabajadores insertos en este tipo de informalidad. Los hallazgos presentados constituyen un avance de investigación sobre la reproducción de la marginalidad urbana en el Conurbano Bonaerense. Parte del trabajo de campo se realizó durante el año 2008, en un barrio del Partido de Almirante Brown. Se organizaron dos grupos de discusión: uno con mujeres perceptoras de planes y otro con hombres que realizaban changas como actividad principal. Con el objeto de aportar datos acerca de las condiciones materiales de los hogares, se aplicó un cuestionario a los participantes. Junto con esta información, se analizaron registros de campo tomados en observaciones realizadas en diversos espacios del barrio
Resumo:
This data set contains two time series of measurements of dissolved phosphorus (organic, inorganic and total with a biweekly resolution) and dissolved inorganic phosphorus with a seasonal resolution. In addition, data on phosphorus from soil samples measured in 2007 and fractionated by different acid-extrations (Hedley fractions) are provided. All data measured at the main experiment plots of a large grassland biodiversity experiment (the Jena Experiment; see further details below). In the main experiment, 82 grassland plots of 20 x 20 m were established from a pool of 60 species belonging to four functional groups (grasses, legumes, tall and small herbs). In May 2002, varying numbers of plant species from this species pool were sown into the plots to create a gradient of plant species richness (1, 2, 4, 8, 16 and 60 species) and functional richness (1, 2, 3, 4 functional groups). Plots were maintained by bi-annual weeding and mowing. 1. Dissolved phosphorus in soil solution: Suction plates installed on the field site in 10, 20, 30 and 60 cm depth were used to sample soil pore water. Cumulatively extracted soil solution was collected every two weeks from October 2002 to May 2006. The biweekly samples from 2002, 2003 and 2004 were analyzed for dissolved organic phosphorus (DOP), dissolved inorganic phosphorus (PO4P) and dissolved total phosphorus (TDP) by Continuous Flow Analyzer (CFA SAN ++, SKALAR [Breda, The Netherlands]). 2. Seasonal values of dissolved inorganic phosphorus in soil solution were calculated as volume-weighted mean values of the biweekly measurements (spring = March to May, summer = June to August, fall = September to November, winter = December to February). 3. Phosphorus fractions in soil: Five independent soil samples per plot were taken in a depth of 0-15 cm using a soil corer with an inner diameter of 1 cm. The five samples per plot were combined to one composite sample per plot. A four-step sequential P fractionation (Hedley fractions) was applied and concentrations of P fractions in soil were measured photometrically (molybdenum blue-reactive P) with a Continuous Flow Analyzer (Bran&Luebbe, Germany).