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In this paper we investigate the prospects for the large-scale use of low-emission energy technologies in Africa. Many African countries have recently experienced substantial economic growth and aim at fulfilling much of the energy needs associated with continuing along paths of economic expansion by exploiting their large domestic potentials of renewable forms of energy. Important benefits of the abundant renewable energy resources in Africa are that they allow for stimulating economic development, increasing energy access and alleviating poverty, while simultaneously avoiding emissions of greenhouse gases. In this study we analyse what the likely energy demand in Africa could be until 2050, and inspect multiple scenarios for the concomitant levels of greenhouse gas emissions and emission intensities. We use the TIAM-ECN model for our study, which enawbbles detailed energy systems research through a technology-rich cost-minimisation procedure. The results from our analysis fully support an Africa-led effort to substantially enhance the use of the continent's renewable energy potential. But they suggest that the current aim of achieving 300 GW of additional renewable electricity generation capacity by 2030 is perhaps unrealistic, even given high GDP and population growth: we find figures that are close to half this level. On the other hand, we find evidence for leap-frogging opportunities, by which renewable energy options rather than fossil fuels could constitute the cost-optimal solution to fulfil most of Africa's growing energy requirements. An important benefit of leap-frogging is that it avoids an ultimately expensive fossil fuels lock-in that would fix the carbon footprint of the continent until at least the middle of the century.

In this paper we investigate the prospects for the large-scale use of low-emission energy technologies in Africa. Many African countries have recently experienced substantial economic growth and aim at fulfilling much of the energy needs associated with continuing along paths of economic expansion by exploiting their large domestic potentials of renewable forms of energy. Important benefits of the abundant renewable energy resources in Africa are that they allow for stimulating economic development, increasing energy access and alleviating poverty, while simultaneously avoiding emissions of greenhouse gases. In this study we analyse what the likely energy demand in Africa could be until 2050, and inspect multiple scenarios for the concomitant levels of greenhouse gas emissions and emission intensities. We use the TIAM-ECN model for our study, which enawbbles detailed energy systems research through a technology-rich cost-minimisation procedure. The results from our analysis fully support an Africa-led effort to substantially enhance the use of the continent's renewable energy potential. But they suggest that the current aim of achieving 300 GW of additional renewable electricity generation capacity by 2030 is perhaps unrealistic, even given high GDP and population growth: we find figures that are close to half this level. On the other hand, we find evidence for leap-frogging opportunities, by which renewable energy options rather than fossil fuels could constitute the cost-optimal solution to fulfil most of Africa's growing energy requirements. An important benefit of leap-frogging is that it avoids an ultimately expensive fossil fuels lock-in that would fix the carbon footprint of the continent until at least the middle of the century.

This paper introduces an integrative approach to hedonic house price modeling which utilizes high density 3D airborne laser scanning (ALS) data. In general, it is shown that extracting exploratory variables using 3D analysis – thus explicitly considering high-rise buildings, shadowing effects, etc. – is crucial in complex urban environments and is limited in well-established raster-based modeling. This is fundamental in large-scale urban analyses where essential determinants influencing real estate prices are constantly missing and are not accessible in official and mass appraiser databases. More specifically, the advantages of this methodology are demonstrated by means of a novel and economically important externality, namely incoming solar radiation, derived separately for each flat. Findings from an empirical case study in Vienna, Austria, applying a non-linear generalized additive hedonic model, suggest that solar radiation is significantly capitalized in flat prices. A model comparison clearly proves that the hedonic model accounting for ALS-based solar radiation performs significantly superior. Compared to a model without this externality, it increases the model’s explanatory power by approximately 13% and additionally reduces the prediction error by around 15%. The results provide strong evidence that explanatory variables originating from ALS, explicitly regarding the immediate 3D surroundings, enhance traditional hedonic models in urban environments.

This paper introduces an integrative approach to hedonic house price modeling which utilizes high density 3D airborne laser scanning (ALS) data. In general, it is shown that extracting exploratory variables using 3D analysis – thus explicitly considering high-rise buildings, shadowing effects, etc. – is crucial in complex urban environments and is limited in well-established raster-based modeling. This is fundamental in large-scale urban analyses where essential determinants influencing real estate prices are constantly missing and are not accessible in official and mass appraiser databases. More specifically, the advantages of this methodology are demonstrated by means of a novel and economically important externality, namely incoming solar radiation, derived separately for each flat. Findings from an empirical case study in Vienna, Austria, applying a non-linear generalized additive hedonic model, suggest that solar radiation is significantly capitalized in flat prices. A model comparison clearly proves that the hedonic model accounting for ALS-based solar radiation performs significantly superior. Compared to a model without this externality, it increases the model’s explanatory power by approximately 13% and additionally reduces the prediction error by around 15%. The results provide strong evidence that explanatory variables originating from ALS, explicitly regarding the immediate 3D surroundings, enhance traditional hedonic models in urban environments.

During their lifespan, products can cause severe environmental and social impacts in all stages of their lifecycle. The circular economy with its focus on closing and slowing material and energy loops is a means to reduce these broad impacts. Circular economy forms the basis of the EU’s ambitions to reconcile present economic activities within the planetary boundaries while meeting its aim for climate neutrality by 2050. Electronic and electronics equipment is a key product focus area for the European Commission, during the waste stage. Similar to other EU Directives, current electronics waste legislation will be updated in the coming years. The transition to a circular economy will require new and modified roles and responsibilities for actors, e.g. government, businesses and citizens. This report provides a detailed exploration of the governance issues within the current electronics waste policy, focusing on the instrument of extended producer responsibility. Through three detailed case studies of Italy, France and the Netherlands, the key organisational and policy features are explained, and the strengths and weaknesses are outlined. Based on the analysis of the case studies, we argue the subsequent developments for extended producer responsibility for waste electrical and electronic equipment to include the four followings aspects in its development: 1. Introducing the modulation of fees at the European level: the fee paid by producers for the collection and recycling of their products should be modulated based on the circularity and sustainability of the product in question. Fee modulation is allowed under the current EU WEEE law. However, it is not applied systematically. This is already done in France for EEE based on the standardisation of components, weight and specific materials. Fee modulation guidelines have been developed by the OECD. However, the key aspect to the ability of the fees to affect product design is the size of the fee. Studies have illustrated that current fees are between 0.2 and 2% of the product price. Higher levels of fees, e.g. more than the 2% product price, combined with a visible fee are recommended to be implemented at the EU level; 2. Broadening the scope of which actors are included in national EPR systems while promoting high R-strategies: the types of actors and responsibilities within the extended producer responsibility schemes need to be broadened. This is possible under EU law and has partly been done in France, where civic actors are now included in the functioning and directing of the schemes. However, the transition to a circular economy requires the promotion of more than just recycling of EEE to the other R-strategies. This requires systematically integrating the other economic actors in the design and functioning of the system, e.g. Repair, Remanufacturing etc.; 3. Measures to promote the highest value recycling of collected WEEE: products that reach their end-of-life they need to be effectively collected and treated to the best standard. The current targets and quality measures promote the collection and recycling of electronics based on mass, not on a specific material or quality criteria. A standard for the treatment of WEEE EN 45558 is available, although it is not mandatory. We recommend this standard be made mandatory across the EU. In addition, we call for a systematic pan-EU assessment of available and future recycling technologies, possibilities for urban mining from WEEE, and funding options needed to direct this, specifically in the area of critical raw materials recovery from electronics; 4. Expanding the scope of EPR beyond national borders: the scope of extended producer responsibility schemes needs to be expanded to account for the multiple uses of the product and the responsibility when products move internationally. While EPR has shown great ability to shift WEEE away from landfilling. The complexity of systems, rules and their enforcement between member states and beyond has led to varying national rules and issues of transparency between jurisdictions. The quantity of producers, importers, distributors and second-hand sellers makes the tracking and monitoring of WEEE within and between national jurisdictions challenging, especially for the export of collected and secondary products. In particular, this relates to the need for a solid understanding of the quantities of WEEE moving between jurisdictions and suitable mechanisms in place to finance the appropriate disposal. The highly international nature of WEEE supply chains and global trade and flows of WEEE have led some to call for a ‘global EPR’ or ‘ultimate producer responsibility’ system.

During their lifespan, products can cause severe environmental and social impacts in all stages of their lifecycle. The circular economy with its focus on closing and slowing material and energy loops is a means to reduce these broad impacts. Circular economy forms the basis of the EU’s ambitions to reconcile present economic activities within the planetary boundaries while meeting its aim for climate neutrality by 2050. Electronic and electronics equipment is a key product focus area for the European Commission, during the waste stage. Similar to other EU Directives, current electronics waste legislation will be updated in the coming years. The transition to a circular economy will require new and modified roles and responsibilities for actors, e.g. government, businesses and citizens. This report provides a detailed exploration of the governance issues within the current electronics waste policy, focusing on the instrument of extended producer responsibility. Through three detailed case studies of Italy, France and the Netherlands, the key organisational and policy features are explained, and the strengths and weaknesses are outlined. Based on the analysis of the case studies, we argue the subsequent developments for extended producer responsibility for waste electrical and electronic equipment to include the four followings aspects in its development: 1. Introducing the modulation of fees at the European level: the fee paid by producers for the collection and recycling of their products should be modulated based on the circularity and sustainability of the product in question. Fee modulation is allowed under the current EU WEEE law. However, it is not applied systematically. This is already done in France for EEE based on the standardisation of components, weight and specific materials. Fee modulation guidelines have been developed by the OECD. However, the key aspect to the ability of the fees to affect product design is the size of the fee. Studies have illustrated that current fees are between 0.2 and 2% of the product price. Higher levels of fees, e.g. more than the 2% product price, combined with a visible fee are recommended to be implemented at the EU level; 2. Broadening the scope of which actors are included in national EPR systems while promoting high R-strategies: the types of actors and responsibilities within the extended producer responsibility schemes need to be broadened. This is possible under EU law and has partly been done in France, where civic actors are now included in the functioning and directing of the schemes. However, the transition to a circular economy requires the promotion of more than just recycling of EEE to the other R-strategies. This requires systematically integrating the other economic actors in the design and functioning of the system, e.g. Repair, Remanufacturing etc.; 3. Measures to promote the highest value recycling of collected WEEE: products that reach their end-of-life they need to be effectively collected and treated to the best standard. The current targets and quality measures promote the collection and recycling of electronics based on mass, not on a specific material or quality criteria. A standard for the treatment of WEEE EN 45558 is available, although it is not mandatory. We recommend this standard be made mandatory across the EU. In addition, we call for a systematic pan-EU assessment of available and future recycling technologies, possibilities for urban mining from WEEE, and funding options needed to direct this, specifically in the area of critical raw materials recovery from electronics; 4. Expanding the scope of EPR beyond national borders: the scope of extended producer responsibility schemes needs to be expanded to account for the multiple uses of the product and the responsibility when products move internationally. While EPR has shown great ability to shift WEEE away from landfilling. The complexity of systems, rules and their enforcement between member states and beyond has led to varying national rules and issues of transparency between jurisdictions. The quantity of producers, importers, distributors and second-hand sellers makes the tracking and monitoring of WEEE within and between national jurisdictions challenging, especially for the export of collected and secondary products. In particular, this relates to the need for a solid understanding of the quantities of WEEE moving between jurisdictions and suitable mechanisms in place to finance the appropriate disposal. The highly international nature of WEEE supply chains and global trade and flows of WEEE have led some to call for a ‘global EPR’ or ‘ultimate producer responsibility’ system.