Refine
Year of Publication
Document Type
- Working Paper (230) (remove)
Language
- English (230) (remove)
Germany's waste management system is one of the world's most advanced - its primary objective is to dispose of waste in a way that is safe for both people and the environ- ment. However, only about 14 per cent of the raw materials used in industry are derived from recycling processes; the remainder are still sourced from primary materials. The circular economy is not yet being implemented on a large enough scale. Recyclates or recycled materials, i.e. secondary raw materials recovered from waste, are being fed back into production and usage processes at volumes that are far below what is possible. If this system were to be improved, loss of value, dependence on volatile commodity markets, lower resource productivity, and externalities in the form of environmental pollution could be avoided. A drive towards digitalisation in industry and the waste management sector could make this happen. A study by the German Federal Ministry for the Environment, Nature Conservation, Building and Nuclear Safety (BMUB) indicates that no other lead market in the environmental sector stands to benefit from digitalisation more than the circular economy - and that, at the same time, no sector has ever been so poorly positioned.
The objectives of the urban mobility transition have been clearly set out: gaining more space for urban living, reducing noise and emissions that have a negative impact on the climate and improving air quality. That means less traffic in cities and more trips made using environmentally-friendly modes of transport - i.e., walking, cycling or foot scooters or public transport. In transport policy, the focus is generally on innovative approaches to shaping the mobility transition.
This paper aims to explain the concept of exnovation in the context of the urban mobility transition and to underpin it using specific practical examples. In the course of this process, it is intended to identify the obstacles that stand in the way of rolling out the concept on an area-wide basis in order to deduce strategies and courses of action for expanding the concept in the future.
The transformation of urban mobility systems causes financial costs for the procurement and operation of innovative products and services and for the adaptation of existing infrastructure. While public budgets are limited, investments in infrastructure and transport services compete against other spending priorities, and private investors often are reluctant to invest into sustainable transport projects. Thus, cities need to seek additional funding and financing options and to develop business models to attract private sector investments in the development of the urban transport system. Moreover, financing schemes should cover the entire SUMP (Sustainable Urban Mobility Planning) cycle, starting from planning, to project implementation and procurement up to the operation and maintenance of services and infrastructures.
This requires the blending of different revenue sources, including:
project related revenue sources such as public transport fares and the lease of advertising space in buses;
the extension of the local tax base, for example through the introduction of road user charges and parking fees or the use of value capture mechanisms;
National, bilateral, and European grants;
Debt financing through loans and other instruments such as issuing green bonds. Finally, a prudential engagement of the private sector in infrastructure development and service provision can reduce the direct burden on public budgets while enhancing service quality. The applicability of specific financing options critically depends on the national legislative environment. Many of the instruments and case examples presented here may not be transferred to other Member States due to the different distribution of responsibilities and powers between the political levels in the Member States. This report, however, can inspire the search for potential funding and financing sources and is therefore aimed not only at local and regional authorities but also at decisionmakers at the national level. Still, whether a specific instrument can be used in a Member State needs to be assessed on a case-by-case base.
Towards a set of indicators on sustainable consumption and production (SCP) for EEA reporting
(2010)
What is necessary to reach net zero emissions in the transport sector on a global level? To keep limiting global warming to 1.5° C within reach, the world has to decarbonise by mid-century, with every sector contributing as much as possible as soon as possible. This paper identifies what has to be done in road transport, aviation, and shipping to achieve net zero emission in the transport sector.
For this purpose, it first sets the scene by providing an overview of the origins and impacts of the concept of net zero emissions in international climate policy as well as of the current state and future prospects of global transport emissions using currently available scenarios for low-emission and net zero transport.
While for staying below 1.5° C, the basic approach to reducing transport emissions remains unchanged from what has been suggested in the past, the set, intensity and pace of actions as to shift fundamentally. Without first drastically reducing traffic volume and shifting transport demand to low-emission modes, reaching net zero transport will not be feasible: the amount of additional electricity required to fully electrify the sector with renewable energy is otherwise just too huge.
After portraying key instruments for achieving net zero emissions in land transport, aviation, and shipping, this paper identifies key barriers for net zero transport. Based on this analysis, the authors recommend the following to be able to move transport to net zero:
1. Adapt Decarbonisation Strategies to Different Transport Sub-sectors
2. Prioritise and Significantly Increase Investment in Zero-/low-carbon Infrastructure
3. Massively Invest in the Development and Roll out of Zero-/low-emission Technologies
4. Focus on a Just Transition to Overcome Social and Political Barriers
5. Increase International Support and Cooperation
Article 6.4 of the Paris Agreement establishes a new mechanism for Parties to cooperate in achieving their nationally determined contributions (NDCs). One key innovation of the Article 6.4 mechanism is its objective to "deliver an overall mitigation in global emissions" (Art. 6.4(d)). This report develops recommendations on how to implement this objective. A key difficulty lies in the fact that even basics of how the mechanism is supposed to function have so far not been clarified by the Parties. The report therefore first sketches out what has so far been agreed and discussed on the mechanism’s activity cycle. Second, as the concept of overall mitigation has so far also not been clearly defined by Parties, the report derives a working definition from the language that was agreed in the Paris Agreement. In the next step, the report provides a survey of the options to achieve overall mitigation that have so far been discussed in the relevant literature and in the Article 6 negotiations. Many of these options were developed in the context of the Kyoto mechanisms. The report therefore discusses to what extent the options are also applicable under the Paris Agreement or whether adjustments need to be made. In the following, the options that are applicable under the Agreement are assessed on the basis of a number of criteria. The report concludes with a summary of the main findings and recommendations.
City-wide programmes of activities : an option for significant emission reductions in cities?
(2012)
The brochure summarises the project's objectives and methodological approach, its key findings as well as conclusions. Both case studies have shown that technological solutions for low carbon development should be embedded in a well-developed institutional framework to foster their deployment and implementation. Therefore, recommendations for Wuxi include examples of innovative and integrated technical projects for increasing energy and resource efficiency, combining them with recommendations for the development of institutional frameworks. One element of such a framework could be a local energy agency in Wuxi, which would offer support and expertise to potential investors in low carbon technologies. Also for the German pilot region, the brochure offers concrete recommendations how to facilitate low carbon planning within the region.
The Sino-German project "Low Carbon Future Cities" (LCFC) aims to develop a low carbon strategy for its Chinese pilot city Wuxi. The strategy primarily focuses on carbon mitigation, but also considers links with the issues of resource efficiency and adaption to climate change. This report written by Daniel Vallentin, Carmen Dienst and Chun Xia offers strategic examples of good practice and makes recommendations to Wuxi city government about the changes that key sectors can adopt in order to comply with its low carbon targets. The recommendations are based on scientific analyses which were undertaken earlier in the LCFC project.
Inducing the international diffusion of carbon capture and storage technologies in the power sector
(2007)
Although CO2 capture and storage(CCS) technologies are heatedly debated, many politicians and energy producers consider them to be a possible technical option to mitigate carbon dioxide from large-point sources. Hence, both national and international decision-makers devote a growing amount of capacities and financial resources to CCS in order to develop and demonstrate the technology and enable ist broad diffusion.The presented report concentrates on the influence of policy incentives on CCS diffusion and examines the following research question: Which policy strategy is needed to stimulate the international diffusion of carbon capture and storage technologies in the power sector? Based on the analysis of innovation-specific (e.g. CCS competitiveness and compatibility), market-related (e.g. national CO2 discharges and storage capacities) and institutional determinants (e.g. existing national and international policy frameworks) of CCS diffusion, the paper discusses the suitability of various national and international policy instruments to induce the international deployment of CCS. Afterwards, three CCS diffusion paths are derived from fundamentally different carbon stabilisation scenarios which include climate policy measures to stimulate the adoption of CO2 mitigation technologies.
Concretely defined targets are guiding policy efforts and the measures required to achieve national energy and low-carbon transformations in order to reach the maximum 2 degree climate change mitigation target agreed at the COP in Paris in 2015. Reducing energy consumption by harnessing the potential of energy efficiency, expanding the use of renewable energy resources, and transforming all sectors into low-energy and low-carbon structures is crucial. Among the G20 states, most states have set targets for renewable energies, energy efficiency, and greenhouse gas (GHG) emission reductions. Yet, it seems that starting points and target units differ a lot between the G20, and hence comparability is difficult. This topical paper presents a synopsis on the current targets within the G20. The relative lack of energy efficiency targets shows that this pillar needs much greater efforts in current and future energy policy.
This Wuppertal Paper analyses the energy transition models of Colombia and Germany. The emphasis of the exercise is on an analysis of options for the complete decarbonization of the energy system in Colombia as a Global South country. To this end, it analyses the current situation, projections, public policy and narratives, and contrasts it with Germany as one of the countries of the Global North with which Colombia has historically maintained energy trade relations and is currently collaborating in the exploration of energy alternatives for decarbonization.
Detailed analysis of sectoral energy consumption in Colombia shows the sectors with the highest fossil energy consumption (in this order): transport (fuels), industry (gas, coal), electricity generation (gas, coal) and residential (gas). We show the projected increase in demand for fuels and electricity, and calculate the amount of electricity theoretically needed to substitute fossil sources in each sector. We estimate the total electricity required for decarbonization via sector coupling and derive a first estimation of the range of additional renewable energy capacities needed to supply this demand. We find that required capacities are expectedly large (56-110 GW), depending on decarbonization pathways, and that export capacity beyond national demand may be limited.
Our analysis of the policy and scenario arena in both countries finds that Colombia is still lacking both sector-specific decarbonization strategies and an embedding in a systemic vision of a systemic energy transition. Germany has more advanced sector strategies and (national) systemic visions, but lacks embedding assumptions on energy imports in a global-system analysis, i.e. in the analysis of an energy transition in potential exporting countries like Colombia. We formulate requirements to close these gaps in our conclusions.
In this paper the results of an analysis of the material intensity of advanced composite materials are presented. The analysis is based on the MIPS-concept of the Wuppertal Institute which allows the calculation of the overall material intensity of products and services. It can be shown that the production of one kg of E-Glass fibers is connected with the consumption of 6.2 kg materials, 95 kg water and 2.1 kg oxygen which is of similar size compared to the inputs required in steel production. Material inputs required to produce one kg of p-aramid are 37 kg of materials and 19.6 kg air. Values for carbon fibers are even higher yielding to 61.1 kg of abiotic materials and 33.1 kg of air. Similarly, the production of epoxy resins is connected with larger material flows than the production of polyester resins. Of core materials, inputs per kg for PVCfoam exceed those in PUR-foam production by a factor of 1.4 in water to 2.3 in abiotic material consumption. However, ecologically decisive are not the inputs per kg but the material input per service unit. Therefore, the material input per service unit computed for the body of a passenger ship and a robot arm are compared with alternative steel and aluminium versions. Both examples show that in the case of significant inputs during the user phase of products, even a more material intensive investment in the production phase can yield significant ecological benefits over the whole life-cycle compared to metal versions. Improvements can easily reach a factor of two albeit significant potential for engine optimizations have still been neglected. Results already include the actual recycling quota of metals whereas for composites only virgin material has been calculated as any form of real recycling does not actually exist but only certain types of downrecycling. Of those treatment options, first material recycling and second the use in blast furnaces would lead to better results in resource productivity than incineration and landfills. The paper finally draws some conclusions about the potential advantages of material substitution in the automotive industry. Due to the rather short real operation time of cars during their user phase - around six months - an investment in advanced composite materials in car production only results in a significant improvement of the overall eco-efficiency of cars if it allows a substantial weight reduction of the overall vehicle.
Addressing opportunities and challenges of a sectoral approach to the Clean Development Mechanism
(2005)
Domestic emission trading systems in developing countries : state of play and future prospects
(2011)
How much is 100 billion US dollars? : Climate finance between adequacy and creative accounting
(2011)
From Clean Development Mechanism to sectoral crediting approaches : way forward or wrong turn?
(2008)
Nutrition is one of the most important areas for the great transformation. So how can a shift towards a sustainable food system be achieved? This paper addresses this question - based on more than ten years of research on sustainable nutrition at the Wuppertal Institute. It focuses on public catering, because even small changes - for example in the choice of ingredients - have a huge impact here. With appropriate policy frameworks, public catering can serve as an easily accessible place for consumers to experience sustainable food and at the same time be a reliable buyer of biodiversity and climate-friendly food from farmers. However, other actors are also needed for a transformation of the food system: The "Zukunftsimpuls" addresses politics, (agricultural) industry, science and every individual - because the transformation of the food system is a task for the entire society.
This paper examines the connection between globalisation, with its growth in world trade links, and certain ecological effects especially concerning "North-South" relations. Although world trade in the mid-nineties was significantly uncoupled from growth trends in the world economy, so that since then it has increased nearly three times faster than the global GDP, certain indicators of energy use and CO2 emissions have not developed proportionately to world trade; globalisation evidently does not lead to a situation where pressures on the environment are increasing to the same extent worldwide. This de-linking may, however, result in the kind of shifts that we examine here with reference to the material trade flows of the European Union. It will be shown that, in the course of globalisation, the countries of the EU have increasingly shifted environmental burdens on to the countries of the South, especially in the form of ecological rucksacks of imported raw materials, while at the same time reducing the pressure on their own domestic environment by extracting fewer material resources. Furthermore, goods whose production places intensive pressure on the environment (industrial emissions into the atmosphere and water, heavy metal emissions, etc.) have been increasingly imported from newly industrializing or developing countries. The greater covering of material requirements from foreign resources has served not so much the EU's internal consumption as its own production of export goods; this shows that the EU has an increasing share in the resource requirement of other economies. The paper concludes that it is absolutely necessary to consider the international dimension in any strategy for more productive use of resources in industrial countries. In the long term, the EU's resource use should also be reduced in absolute terms. This will also be necessary in order to reduce the pressure on the environment due to imports and exports.