Language and gender: from linguistic and textual perspectives
In: Studier i modern språkvetenskap N.S., 14
In: Acta Universitatis Stockholmiensis
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In: Studier i modern språkvetenskap N.S., 14
In: Acta Universitatis Stockholmiensis
This chapter provides an overview of the status and trends in biodiversity and ecosystem function through assessment of key species and habitats, and summarizes the ecological status of selected Nordic regions. Important habitats across the Nordic coastal region include sea grass beds, kelp forests, blue mussel beds and soft sediments. Declines in sea grass have occurred since the 1970's, most likely due to eutrophication and overfishing. Norwegian kelp forests are recovering following severe losses in the 1960–1970's, most likely due to increased water temperature and changes in grazing pressure. Seabird populations have declined significantly during the last decades, reaching historical lows. Knowledge gaps are identified and a common biodiversity indicator system across the Nordic region is suggested. An indigenous local knowledge perspective is also presented.
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This thesis aims to explain how small states, in this case Sweden, security politics adapts to new circumstances after great conflicts in the 20th century. The analytical model is built by a combination of the opposite theories of international politics, realism and idealism, combined with actor based and structure based perspectives and thus creating a four field analytical matrix. The empirical foundation constitutes of three post conflict periods; post-first world war, post-second world war and post-cold war periods. For every period three cases are analyzed; one foreign politics initiative, one association to an international organization and one defence politics decision. In the post-first world war period the focus is on the Swedish intervention of the Åland archipelago, the association to the League of Nations and disarmament decision in 1925. In the post-second world war period the focus is on the association of Sweden to the United Nations, the Swedish initiative to a Scandinavian defence alliance and the defence decision of 1948. In the post-cold war period the focus is on the Swedish association to the European Union, the Swedish participation in the NATO led IFOR operation in Bosnia and the defence decision in 1996. The main conclusions of these investigations are that small states, like Sweden, both are restricted in their foreign and security politics by international structures and able to use the same structure to promote their interests. Time is a key element for analyzing both structural and actor based aspects of a small states capacity. Also, in the case of Sweden, there tends to be a tension between an idealistic dominated politics and a realistic dominated politics when it comes to foreign and security politics, and that idealism seems to have increased in the latter period.
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This chapter examines the conceptual framework boxes and fluxes on "Institutions and governance and other indirect drivers" (Ch. 1, Fig. 1). International and EU governance of relevance for ecosystem services, biodiversity and water is presented. Policy integration, policy coherence, management regimes and stakeholder involvement is reflected upon. The chapter contributes to further understanding of the current and future challenges for sustainable use and conservation of biodiversity and ecosystem services. It provides insights in options for integrating biodiversity and ecosystem services into sustainable development strategies and provides examples of current policy conflicts, along with trade-offs and innovative governance strategies for management of natural resources. Policy-makers need to find ways to handle policy conflicts, improve integration of different stakeholders' perspectives and value dimensions including ILK in policymaking, develop new data collection methods for linking biodiversity and ecosystem services, and develop governance systems that enhance transparency, sustainability and human well-being.
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Antimicrobial resistance (AMR) is one of the biggest threats against public health in the world. Antimicrobial substances are used within all different sectors and contribute to development of AMR. Global action against irresponsible use of antibiotics and further development of AMR has been of great concern in the last years and risk factors are being pointed out. Low- and middle-income countries (LMICs) have a precarious role in the matter. Insufficient health care systems, poor law enforcement and, high accessibility of over-the-counter drugs (OTCs) are contributing to the unregulated use of antibiotics. Poorly developed surveillance programmes make it hard to correctly analyse the situation of both antimicrobial use (AMU) and AMR. Bangladesh, like its neighbouring countries, faces a lot of challenges regarding public health. One of the major concerns related to public health is access to safe food. Food products can be contaminated with toxins, chemical substances, and microbial organisms, including AMR-bacteria. Furthermore, national programmes for surveillance of AMU and AMR are inadequate. In this study, data from previously done field studies by Bangladesh Livestock Research Institute (BLRI), Bangladesh Food Safety Authority (BFSA), International Livestock Research Institute (ILRI), and International Food Policy Research Institute (IFPRI) and newly collected information from interviews were put together to analyse the AMR situation in Bangladesh. Sampling of food products (tomato, chicken, fish) from traditional markets and supermarkets was done at three locations representing rural, peri-urban, and urban areas from November 2018 to June 2019. Samples were tested for prevalence of Salmonella spp, Escherichia coli, Vibrio cholerae. Samples positive for bacteria were tested for antimicrobial susceptibility through disc diffusion test. As a supplement to the analysis of samples, questionnaires to the vendors of the food products were made to provide background information. During 2020, statistical analysis of previously collected data and interviews with stakeholders working with AMR was made. The interviews aimed to serve as baseline information about current conditions regarding AMU and AMR. 320 cultivations of 1589 (20.1%) were positive for bacterial prevalence. 319 of these were tested for antimicrobial susceptibility where 203 (63.6%) were found to be multidrug-resistant (MDR) (resistant to three or more antibiotic groups). Furthermore, interviews with stakeholders stated that surveillance of AMU and AMR in Bangladesh is inadequate, especially within the animal and agriculture sector, and that a one health approach on a government level is needed to improve the situation. To be able to fully analyse the AMR situation in Bangladesh, a nation-wide study would need to be conducted, within all sectors, including both AMU and AMR testing.
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This study was made with the purposes of characterizing milk supply and marketing chains, postproduction losses of milk, and evaluating the potential of supply chain management approach to reduce milk losses in Ethiopia. Primary data were collected by semi-structured survey questionnaire and interview of key informants. The collected data were analyzed using SPSS and Microsoft Excel sheets. Mapping, characterizations, and descriptive statistics were used to analyze the collected data. Both quantitative and qualitative-narrative methods were used in analysis. The finding revealed that farmers, cooperatives/unions, traders, and catering institutions were the major chain actors in milk chain in the study area. With 73% of milk sold by farmers passing through cooperatives/unions to the next chain actors, cooperatives/unions were the focal firms in this supply chain. Production was characterized by smallholders with few numbers of cows and low productivity of milk per cow per day. Cow breed and lack of access to credit were identified as critical resource and the most constraint that hinder production improvement. Marketing relationships among the chain actors were characterized as lacking long-term market orientation and were mostly on the spot and transaction based. The assessment on the enabling environment indicated further need of support from governmental and non-governmental stakeholders to build the capacity of chain actors, particularly the farmers. The study indicated existence of significant amount of milk losses in the milk chain. With 39% of the total losses happening at cooperatives/union stage, cooperatives/unions were identified as loss hotspot point in the chain. Poor milk handling practice at the collection points, lack of immediate acceptors, milk carrying tools used, means of transport used, and ineffective communication with other partner in the chain were identified in order of severity as important problems causing milk losses in the study area. Based on the study results and review of others' work in similar contexts, this study argued for SCM to be part of solution in improving this dairy chain. The study showed cases where effectively implemented SCM approach converted dairy chains from chains characterized by dismantled, high conflicts of interests among the chain actors, and high losses of food in the chain to chains with mutual interest trying to maximize the profit to the whole chain actors. Integrated and collective actions by all chain actors aiming at reducing costs, improving quality, and minimizing food losses in the chain were central to these efforts. Therefore, SCM approach needs to be part of the solution in increasing profitability and reducing milk losses in Ethiopia in general and in the study area in particular. However, the needs for detailed further study, some of which are recommended by this study, are worthwhile.
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The literature highlights how climate change might challenge the definitions of wine geographical indications (GIs) in Europe. The central issue addressed in this thesis is whether European GI viticultural systems could tackle climate change via initiating adaptive institutional change processes to relax the constraints imposed by GI production standards. To do so, drawing from institutional economics theory and literature on cooperatives and collective brand, we developed a novel agent-based model (ABM) representing an abstract GI wine production system in the European Union (EU). Using illustrative data, our model allows testing different impact scenarios driven by climate change, spatial heterogeneity, and alternative institutional settings (i.e., voting mechanism). We used the model to explore individual and collective components of climate resilience and the relationship between economic agents and their environment. We compared the average output of 100 simulations for each of the 12 different climate-landscape-institution scenarios. The inclusion of endogenous institutional change led to considerable variations in all target variables, including the emergence of complex/chaotic behaviours. It enabled the system to reduce farm exits, increase profitability and collective brand value. We showed how landscape heterogeneity has a twofold role in the climate resilience of the system. It increases individual adaptability but obstructs collective adaptive capacity through institutional change. The two different voting mechanisms considered (i.e., relative and absolute majority) did not produce any discernible result. The study highlights the importance of policies oriented to strengthening investments in intangibles and facilitating GI rule amendments, especially in sectors where cooperatives predominate due to poor intangible investments capability and other issues connected to member heterogeneity.
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In: Multiethnica, Band 40
Corporate Social Responsibility (CSR) is a widely debated concept among academics, practitioners and non-practitioners. By definition, CSR concerns the economic, legal, political, environmental and social responsibilities of a business to its stakeholders and society at large. The conventional view of the role of business in society is to act as a market place and make a profit, in a space where demand meets supply. However, extending the role of CSR to include ethical responsibilities often raises questions of why and how? In this thesis, a qualitative research design was used to examine how businesses, more specifically Swedish food retailers, approach their extended responsibilities in society. The analysis focused in particular on collaborations between retail food businesses and other actors. Food retailers hold a key position in forming a link between producers and consumers in the value chain. They are socially and economically tied to a number of problems facing consumers on local level and in the wider global community, such as climate change, food security and public health. Such problems are often complex and based on value conflicts among various stakeholders, and therefore cannot be resolved in isolation. In conditions of social connectedness, responsibility lies with all actors, with businesses considered to have a privileged position in terms of their negotiating power and ability for collective action. The food retail sector is therefore an interesting empirical setting for studying CSR. In four empirical studies, different CSR activities in Swedish food retailers' approaches to taking responsibility for social, environmental or political issues linked directly or indirectly linked to their operations were scrutinised. These activities included different forms of stakeholder engagement, such as partnership, dialogue or multi-stakeholder initiatives. The results indicated that through CSR, food retailers in collaboration with other actors can co-create value and proactively engage in driving (social) change. Responsibility can thus be viewed as the shared objective of collaborations between businesses, organisations and society at large, rather than being attributable to a single actor.
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In: Statsvetenskaplig tidskrift, Band 111, Heft 1, S. 41-47
ISSN: 0039-0747
Presents a research design on why and how states should manage cultural diversity with the emphasis that different combinations of neutrality and recognition work better depending on the circumstances. The concept of difference, reason for toleration, the concept of harm and the ends of toleration are discussed. Research design from case selection to material is briefly brought up. L. Pitkaniemi
In: Politiikka: Valtiotieteellisen Yhdistyksen julkaisu, Band 53, Heft 1, S. 87-88
ISSN: 0032-3365
Strindberg's strategies of commitment, disengagement and new commitment across the border between literature and politics represent an intriguing intellectual adventure we can follow throughout his life as a writer. My article focuses on Strindberg's dilemma as it took form in the first half of the 1880s, and observes it through his fundamental and controversial relationship with the Swedish journalist, literary critic and Social-democratic political leader Hjalmar Branting, with the Danish playwright, literary critic, journalist and radical liberal politician Edvard Brandes, and with the Norwegian writer, politically engaged intellectual and nasjonalskald Bjørnstjerne Bjørnson. For a period they all experienced, along with Strindberg, the ambivalence of working in a social field where art and politics were intertwined, and were to a certain extent involved in the same project, each with his own interpretation. For Strindberg the writer, defending his autonomy from the political field in the end became crucial. What did his colleagues expect from his work? How did Strindberg react to their expectations? What is his legacy today with respect to stances such as intellectual autonomy from power, democratic rule, pacifism and critique of civilization, but also anti-feminism and anti-Semitism? Strindberg's unruly genius illustrates that it is at times difficult to draw the dividing line between radicalism and reaction, and that the great modernists were often also great anti-modernists.
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In: Politiikka: Valtiotieteellisen Yhdistyksen julkaisu, Band 52, Heft 3, S. 250-251
ISSN: 0032-3365
In: Skogs- och lantbrukshistoriska meddelanden 54
The global growth in energy demand continues, but the way of meeting rising energy needs is not sustainable. The use of biomass energy is a widely accepted strategy towards sustainable development that sees the fastest rate with the most of increase in power generation followed by strong rises in the consumption of biofuels for transport. Agriculture, forestry and wood energy sector are the leading sources of biomass for bioenergy. However, to be acceptable, biomass feedstock must be produced sustainably. Bioenergy from sustainably managed systems could provide a renewable and carbon neutral source of energy. Bioenergy systems can be relatively complex, intersectoral and site- and scale-specific. The environmental benefits of biomass-for-energy production systems can vary strongly, depending on site properties, climate, management system and input intensities. Bioenergy supply is closely linked to issues of water and land use. It is important to understand the effects of introducing it as well as it is necessary to promote integrated and synergic policies and approaches in the sectors of forestry, agriculture, energy, industry and environment. Biofuels offer attractive solutions to reducing GHG emissions, addressing energy security concerns and have also other socio-economic advantages. Currently produced biofuels are classified as first-generation. Some first-generation biofuels, such as for example ethanol from corn possibly have a limited role in the future transport fuel mix, other ones such as ethanol from sugarcane or biodiesel made from oils extracted from rerennial crops, as well as non-food and industrial crops requiring minimal input and maintenance and offering several benefits over conventional annual crops for ethanol production are promising. Sugarcane ethanol has greenhouse gas (GHG) emissions avoidance potential; can be produced sustainably; can be cost effective without governments support mechanisms, provide useful and valuable co-products; and, if carefully managed with due regard given to sustainable land use, can support the drive for sustainable development in many developing countries. Sugarcane ethanol - currently the most effective biofuel at displacing GHG emissions - is already mitigating GHGs in Brazil. Jatropha curcas L., a multipurpose, drought resistant, perennial plant has gained lot of importance for the production of biodiesel. However, it is important to point out that nearly all of studies have overstated the impacts of first-generation biofuels on global agricultural and land markets due to the fact that they have ignored the role of biofuel by-products. However, feed by-products of first-generation biofuels, such as dried distillers grains with soluble and oilseed meals are used in the livestock industry as protein and energy sources mitigates the price impacts of biofuel production as well as reduce the demand for cropland and moderate the indirect land use consequences. The production of second generation biofuels is expected to start within a few years. Many of the problems associated with first-generation biofuels can be solved by the production of second generation biofuels manufactured from abundant ligno-cellulosic materials such as cereal straw, sugar cane bagasse, forest residues, wastes and dedicated feedstocks (purpose-grown vegetative grasses, short rotation forests and other energy crops). These feedstocks are not food competitive, do not require additional agricultural land and can be grown on marginal and wasteland. Depending on the feedstock choice and the cultivation technique, second-generation biofuel production has the potential to provide benefits such as consuming waste residues and making use of abandoned land. As much as 97-98% of GHG emissions could be avoided by substituting a fossil fuel with wood fuel. Forest fertilization is an attractive option for increasing energy security and reducing net GHG emission. In addition to carbon dioxide the emissions of methane and nitrous oxides may be important factors in GHG balance of biofuels. Forest management rules, best practices for nitrogen fertilizer use and development of second generation technologies use reduce these emissions. Soils have an important role in the global budget of greenhouse gases. However, the effects of biomass production on soil properties are entirely site and practice-specific and little is known about long-term impact. Soil biological systems are resilient and they do not show any lasting impacts due to intensive site management activities. Land management practices can change dramatically the characteristic and gas exchange of an ecosystem. GHG benefits from biomass feedstock use are in some cases significantly lower if the effects of direct¹ or indirect (ILUC²) land use change are taken into account. LUC and ILUC can impact the GHG emission by affecting carbon balance in soil and thus ecosystem. To understand carbon fluxes in an ecosystem large ecosystem units and time scale are critical. Mitigation measures of the impact of land use change on greenhouse gas emissions include the use of residues as feedstock, cultivation of feedstock on abandoned arable land and use of feedstock by-products as substitutes for primary crops as animal feed. Cropping management is the other key factor in estimating GHG emissions associated with LUC and there is significant opportunity to reduce the potential carbon debt and GHG emissions through improved crop and soil management practices, including crop choice, intensity of inputs, harvesting strategy, and tilling practices. Also a system with whole trees harvesting with nutrient compensation is closely to being greenhouse-gas-neutral. Biochar applied to the soil offers a direct method for sequestrating C and generating bioenergy. However, the most recent studies showing that emissions resulting from ILUC are significant have not been systematically compared and summarized and current practices for estimating the effects of ILUC suffer from large uncertainties. Therefore, it seems to be delicate to include the ILUC effects in the GHG emission balance at a country level. The land availability is an important factor in determining bioenergy sustainability. However, even though food and biofuel/biomass can compete for land, this is not inevitably the case. The pattern of completion competition will e.g. depend on whether food security policies are in place. Moreover, the great potential for uncomplicated biomass production lies in using residues and organic waste, introduction of second generation biofuels which are more efficient in use of land and bioresources as well as restoration of degraded and wasted areas. Agroforestry has high potential for simultaneously satisfying many important objectives at ecosystems, economic and social levels. For example, as a very flexible, but low-input system, alley cropping can supply biomass resources in a sustainable way and at the same time provide ecological benefits in Central Europe. A farming system that integrates woody crops with conventional agricultural crops/pasture can more fully utilize the basic resources of water, carbon dioxide, nutrients, and sunlight, thereby producing greater total biomass yield. Overall, whether food prices will rise in parallel to an increase in biofuel demand will depend, more on trade barriers, subsidies, policies and limitations of marketing infrastructure than on lack of physical capacity. There are plant species that provide not only biofuel resources but also has the potential to sequestrate carbon to soil. For example, reed canary grass (RCG, Phalaris arundinacea L.) indicates the potential as a carbon sink. Harvest residues are increasingly utilized to produce energy. Sweden developed a series of recommendations and good-practice guidelines (GPG) for whole tree harvesting practices. Water has a multifarious relationship to energy. Biofuel production will have a relatively minor impact on the global water use. It is critically important to use low-quality water sources and to select the crops and countries that (under current production circumstances) produce bioenergy feedstock in the water-efficient way. However, local and regional impacts of biofuel production could be substantial. Knowledge of watershed characteristics, local hydrology and natural peak flow patterns coupled with site planning, location choice and species choice, are all factors that will determine whether or not this relationship is sustainable. For example, bioethanol's water requirements can range from 5 to 2138 L per liter of ethanol depending on regional irrigation practices. Moreover, sugarcane in Brazil evaporates 2,200 liters for every liter of ethanol, but this demand is met by abundant rainfall. Biomass production can have both positive and negative effects on species diversity. However, woodfuel production systems as well as agroforestry have the potential to increase biodiversity. A regional energy planning could have an important role to play in order to achieve energy-efficient and cost-efficient energy systems. Closing the loop through the optimization of all resources is essential to minimize conflicts in resource requirements as a result of increased biomass feedstock production. A systems approach where the agricultural, forestry, energy, and environmental sectors are considered as components of a single system, and environmental liabilities are used as recoverable resources for biomass feedstock production has the potential to significantly improve the economic, social, and environmental sustainability of biofuels. The LCA (life cycle analysis) approach takes into account all the input and output flows occurring in biomass production systems. The source of biomass has a big impact on LCA outcomes and there is a broad agreement in the scientific community that LCA is one of the best methodologies for the GHG balance calculation of biomass systems. Overall, maximizing benefits of bioenergy while minimizing negative impacts is most likely to occur in the presence of adequate knowledge and frameworks, such as for example certification systems, policy and guidelines. Criteria for achieving sustainability and best land use practices when producing biomass for energy must be established and adopted. ___________ ¹ Direct land-use change occurs when feedstock for biofuels purposes (e.g. soybean for biodiesel) displace a prior land-use (e.g. forest), thereby generating possible changes in the carbon stock of that land. ² Indirect land-use change (ILUC) occurs when pressure on agriculture due to the displacement of previous activity or use of the biomass induces land-use changes on other lands.
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