849 resultados para Drivers of resilience


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We analysed long-term variations in grain-size distribution in sediments from Gåsfjärden, a fjord-like inlet on the south-west Baltic Sea, and explored potential drivers of the recorded changes in sediment grain-size data. Over the last 5.4 thousand years (ka), the relative sea level decreased 17 m in the study region, caused by isostatic land uplift. As a consequence, Gåsfjärden has been transformed from an open coastal setting into a semi-closed inlet surrounded on the east by numerous small islands. To quantitatively estimate the morphological changes in Gåsfjärden over the last 5.4 ka and to further link the changes to our grain-size data, a digital elevation model (DEM)-based openness index was calculated. In the period between 5.4 and 4.4 ka BP, the inlet was characterised by the largest openness index. During this interval, the highest sand contents (~0.4 %) and silt/clay ratios (~0. 3) in the sediment sequence were recorded, indicating relatively high bottom water energy. After 4.4 ka BP, the average sand content was halved to ~0.2 % and the silt/clay ratios showed a significant decreasing trend over the last 4 ka. These changes are found to be associated with the gradual embayment of Gåsfjärden as represented in the openness index. The silt/clay ratios exhibited a delayed and slower change compared with the sand contents, which further suggest that finer particles are less sensitive to changes in hydrodynamic energy. Our DEM-based coastal openness index has proved to be a useful tool for interpreting the sedimentary grain-size record.

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This data set contains aboveground community biomass in 2009 (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 2009 just prior to mowing (during peak standing biomass in early June 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 three 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 all biomass measures 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.

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This data set contains aboveground community biomass in 2010 (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 2010 just prior to mowing (during peak standing biomass in early June 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 two 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 all biomass measures 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.

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The reform of cities spaces and housing has been a key issue with campaigners on the left for more than a century. These campaigns have found allies in the work of socially committed photographers from Jacob Riis at the turn of the twentieth century to Margaret Morton and Camilo Jose Vergara today. Globally the current phase of neo-liberalism has brought its own issues to the city as ‘regeneration’ strategies dispossess the urban poor in areas that are potentially lucrative to real estate development. In this process known as ‘accumulation by dispossession’ large profits are accumulated in the process of dispossessing people of their land, rights and homes. Central to the theoretical component of this paper, is an interrogation of contemporary ideas on the production and photographic representation of urban space. The research hence questions photography’s ability to make ‘legible’ the key drivers of today’s emergent terrains and to visualize their connections to the networks of power and capital that articulate the current political economy (Sassen 2011:36). One strand here will be the ‘fleshing out’ of the cultural practices behind photographers mediating urban development (Jones 2013: 1.2). Alongside current corporate depictions historical precedents will be discussed. Photographers as far back as Charles Marville in Paris of the 1850’s have documented urban reconstruction (Kennel 2013). Often employed by those undertaking the demolition, these photographic images frequently suppress certain narratives of the unbuilding process. Acting as a propaganda tool they eliminate the impact on the lives of inhabitants or the economic realities driving the valorization of reconstruction schemes (James 2004). Reformist documentary images have also played their part in justifying large-scale urban reconstruction that involved the eventual displacement of existing communities (Rose 1997: Blaikie 2006). Focusing on the gentrification of social housing in Pendleton, Salford (Greater Manchester) the presentation will explore the artists’ own work through a critical discussion, photographic images and excerpts from site writing they’ve undertaken in the area since 2004. It asks can an alternative photographic and visual strategy provide a meaningful political counter narrative to combat persuasive corporate discourses on ‘urban revitalization’? The paper will explore strategies and techniques of witnessing and ask whether these types of record can counter neo-liberal visualizations that mediate the material transformation of city areas. Can such representations begin a critical conversation about the nature of urban change and who benefits from these transformations (Wyly 2010)? Can we develop this critical photography into a type of practice that moves beyond generalisations and talks about social relations though an ‘explicit analysis of society’ (Rosler 2004:195).

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Coastal zones with their natural and societal subsystems are exposed to rapid changes and pressures on resources. Scarcity of space and impacts of climate change are prominent drivers of land use and adaptation management today. Necessary modifications to present land use management strategies and schemes influence both the structures of coastal communities and the ecosystems involved. Approaches to identify the impacts and account for (i) the linkages between social references and needs and (ii) ecosystem services in coastal zones have been largely absent. The presented method focuses on improving the inclusion of ecosystem services in planning processes and clarifies the linkages with social impacts. In this study, fourteen stakeholders in decisionmaking on land use planning in the region of Krummhörn (northwestern Germany, southern North Sea coastal region) conducted a regional participative and informal process for local planning capable to adapt to climate driven changes. It is argued that scientific and practical implications of this integrated assessment focus on multifunctional options and contribute to more sustainable practices in future land use planning. The method operationalizes the ecosystem service approach and social impact analysis and demonstrates that social demands and provision of ecosystem services are inherently connected.

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Urban regions worldwide are increasingly facing the challenge of dealing with highly dynamic metropolitan growth and, at the same time, institutional changes like decentralisation and globalisation. These kinds of changes express themselves most evidently in peri-urban areas, where urban and rural life meets. These peri-urban areas in particular have been the stage for rapid physical, social and economic transformations, both in developed and developing countries. Peri-urbanization takes place here. Based on literature review, this paper presents an effort to identify generic attributes of peri-urbanisation and the way in which development planning tends to reply. Three major attributes are identified: peri-urban space (the spatial expression of peri-urban development), peri-urban life (the functional appearance of land uses, activities and peri-urban innovation), and peri-urban change (a causal and temporal perspective featuring flows and drivers of change). It is also shown that prevalent institutional replies in planning and development generally fail to acknowledge the dynamic and increasingly fragmented attributes of global peri-urbanisation.

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En trabajos anteriores, hemos avanzado en la identificación y diferenciación de tres categorías de potencias: potencias mundiales, potencias medias y potencias regionales. Pero, más allá de las potencias mundiales y las potencias medias que se encuentran en el centro del sistema-mundial, y las potencias regionales que se ubican en la semiperiferia, ¿es posible hablar de potencias que se encuentren en la periferia? Como se trata de Estados periféricos, ¿pueden ser calificados como “potencias”? ¿En qué radicaría su relevancia y envergadura? Dichas “potencias” ¿pueden ser agrupadas en una nueva categoría? De ser así ¿qué características compartirían? El objetivo de este documento es proponer una nueva  categoría de potencias en el sistema internacional: las potencias subregionales.

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Objective: To evaluate the relationship between Perceived Psychological well-being, Optimism and Resilience in women survivors of breast cancer.Method: The sample was composed of 30 women diagnosed with breast cancer who were undergoing adjuvant treatment in Oncology Units General Hospital of Jerez de la Frontera and the University Hospital Puerta del Mar (Cadiz). The average age was 47.47 years (SD = 6,356) and the average of months from diagnosis of the disease was 9.93 (SD = 8,541). Scale of Psychological Well-being administered Perceived Ryff (1989), the Life Orientation Test Revised (LOT-R) Scheier, Carver and Bridges (1994) and the Scale of Resilience Wagnild and Young (1993) to assess psychological well-being the dispositional optimism and resilience respectivelyResults: Descriptive analyzes show that women diagnosed with breast cancer have levels of psychological well-being, dispositional optimism and higher than the average values provided by Resilience scales. On the other hand, regression analyses revealed that only some of the dimensions of resilience allowed to explain and predict some dimensions of psychological wellbeing, not dispositional optimism.Conclusions: The results seem to confirm the idea that if the capacity of women with breast moderate negative affect generated by the diagnosis itself and the consequences of their cancer treatment works and to promote their adaptation to the new situation we can contribute to increasing psychological well-being.

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Dit onderzoek bestudeerde het verband tussen probleemgerichte- en emotiegerichte coping en eetproblematiek en onderzocht daarnaast of mentale veerkracht de relaties tussen probleemgerichte en emotiegerichte coping enerzijds en eetproblematiek anderzijds beïnvloedt. Het doel van dit onderzoek was het verkrijgen van meer inzicht in de rol van mentale veerkracht als mogelijke moderator van de relatie tussen coping en eetproblematiek. Er is een eenmalige meting verricht bij jong volwassen vrouwen van 18 t/m 30 jaar uit de algemene populatie. Via e-mail en sociale media zijn online vragenlijsten verspreid die bruikbare gegevens opleverden van in totaal 188 vrouwen. Meetinstrumenten. Coping is gemeten middels de Utrechtse Coping Lijst (UCL) (Schreurs, Willige, van de Tellegen & Brosschot, 1988; Schreurs, Willige, van de Tellegen & Brosschot, 1993); mentale veerkracht is gemeten met behulp van de Resilience Scale-Nederlandse versie (RS-nl) (Portzky, 2008); en de mate van eetproblematiek is gemeten met de Eating Disorder Examination Questionnaire (EDE-Q) (Fairburn & Beglin, 1994). De resultaten hebben aangetoond dat er een significant negatief verband bestaat tussen probleemgerichte coping en mate van eetproblematiek en een significant positief verband tussen emotiegerichte coping en eetproblematiek. De negatieve samenhang tussen probleemgerichte coping en eetproblematiek bleek sterker bij een lagere mate van mentale veerkracht. De positieve samenhang tussen emotiegerichte coping en eetproblematiek bleek eveneens sterker bij een lagere mentale veerkracht. Personen met een lage mentale veerkracht en een ineffectieve (emotiegerichte of weinig probleemgerichte) copingstijl bleken de meeste eetproblemen te ervaren, bij een hoge mentale veerkracht werd de minste eetproblematiek gerapporteerd, ongeacht de gehanteerde copingstijl.