This article addresses informational barriers to energy efficiency. It is a widely acknowledged result that an energy efficiency gap exists implying that the level of energy efficiency is at an inefficiently low level. Several barriers to energy efficiency create this gap and the presence of asymmetric information is likely to be one such barrier. The article finds that problems of moral hazard and adverse selection indeed can help explain the seemingly low levels of energy efficiency. The theory reveals two implications to policies on energy efficiency. First, the development of measures to enable contractual parties to base remuneration on energy performance must be enhanced, and second, the information on technologies and the education of consumers and installers on energy efficiency must be increased. Finally, it is found that the preferred EU policy instrument on energy efficiency, so far, seems to be the use of minimum requirements. Less used in EU legislation is the use of measuring and verification as well as the use of certifications. Therefore, it is concluded that the EU should consider an increased use of these instruments.
Biogas and bio-methane that are based on energy crops are renewable energy carriers and therefore potentially contribute to climate protection. However, significant greenhouse gas (GHG) emissions resulting from agricultural production processes must be considered. Among those, the production and use of fertilizer, and the resulting leaching of nitrous oxide (N2O), are crucial factors. This article provides an integrated life cycle assessment (LCA) of biogas (i.e. bio-methane that has been upgraded and injected into the natural gas grid), taking into account the processes of fermentation, upgrading and injection to the grid for two different types of biogas plants. The analysis is based on different feedstocks from crop rotation systems for different locations in Germany. A special focus is on the sensitivity of assumptions of nitrous oxide emissions to overall GHG emissions. Much research exists on the measurement or modeling of the actual N2O emissions that result from farming processes. Since there is as yet no precise regional data, most analyses use tier-1 data from the IPCC national GHG inventories as a default. The present article coincides with recent research in indicating that this data varies at the regional level. However, it is not the scope of the article to evaluate the quality of existing data for N2O emissions, but to show the effects of different assumptions on the LCA of GHGs from bio-methane. Thus, a link between the provision of emission data and the practical implementation of biogas technology is provided. The main result is that the supply chain of substrates from agricultural processes appears to contribute the most to the GHG emissions of bio-methane. The "worst case" scenario where 5% of the nitrogen fertilizer used is emitted in form of N2O shows that the GHG mitigation potential of bio-methane versus natural gas is very small, so there is not much margin for error in the plant technology.
Hintergrund: Die Bezugsquellen und Transportwege von fossilem Erdgas werden sich in den kommenden beiden Dekaden diversifizieren. Veränderungen der Lieferstruktur, verbunden mit weiteren Transportentfernungen und dem Neubau von Pipelines sowie der verstärkte Einsatz von verflüssigtem Erdgas (LNG - Liquefied Natural Gas) sind zu erwarten. Entsprechend werden sich auch die vorgelagerten Prozessketten und die damit verknüpften THG-Emissionen verändern. Im Sinne einer korrekten und ganzheitlichen Bilanzierung der Lebenszyklusemissionen und weitgehender Treibhausgasminderungsziele, sind die vorgelagerten Emissionen eine nicht zu vernachlässigende Größe. Gleichzeitig wird Biomethan als Beimischung zum fossilen Erdgas an Bedeutung gewinnen. Obwohl seine Verbrennung als klimaneutral gewertet wird, sind die Prozesse zur Herstellung von Biomethan mit Emissionen verbunden.
Die Treibhausgasemissionen (THG) der Vorketten von in der EU eingesetzten Energieträgern werden in der neuen EU-Kraftstoffqualitätsrichtlinie (vom Dez. 2008) reguliert. Ihre Höhe und ihre Entwicklung wird für die klimapolitischen Diskussionen und politische Entscheidungen somit immer wichtiger.
Ziel: Vor dem Hintergrund der angesprochenen Aspekte sollen die zukünftige Entwicklung der Gasversorgung in Deutschland und die Veränderungen der vorgelagerten THG-Emissionen von Erdgas und Biomethan ermittelt werden. In zwei Szenarien werden die mit der Herstellung und dem Transport von Erdgas und Biomethan verknüpften Emissionen bis zum Jahr 2030 einschließlich des zu erwartenden technischen Optimierungspotenzials bilanziert. Mittels dieser Analyse können Einschätzungen der zukünftigen Emissionspfade und der durchschnittlichen Emissionen (Klimaqualität) des eingesetzten Gases (als Mischung fossiler und biogener Gase einschließlich der damit verbundenen Prozesskettenemissionen) gegeben werden. Diese können als Grundlage für energie- und klimapolitische Entscheidungen dienen.
Ergebnisse und Diskussion: Nach Erläuterung der Prozesskette von Biomethan werden die zu erwartenden technischen Entwicklungen der einzelnen Prozessschritte (Substratbereitstellung, Fermentierung, Aufbereitung, Gärrestnutzung) diskutiert und die Höhe der hiervon zu erwartenden Emissionen bilanziert. Basis sind Ergebnisse der wissenschaftlichen Begleitforschung des Wuppertal Instituts zur Einspeisung von Biomethan ins Erdgasnetz. Dabei gehen wir davon aus, dass die nächste Anlagengeneration "optimierte Technik" das aus heutiger Sicht bestehende Optimierungspotenzial des heutigen Stands der Technik ausschöpfen wird, sodass sich die spezifischen, auf den Heizwert des Biomethan bezogenen, THG-Emissionen der Vorkette von aktuell 27,8 t CO2-Äq/TJ auf 14,8 t CO2-Äq/TJ in 2030 fast halbieren werden.
Die zu erwartenden Emissionen der Erdgasprozesskette wurden in einem Vorgängerartikel bereits im Detail analysiert. Bei der Förderung und der Transportinfrastruktur ist ebenfalls eine Optimierung der Technik zu erwarten. Die dadurch erzielte Verringerung der spezifischen THG-Emissionen kann die aus den künftig längeren Transportstrecken und aufwendigen Produktionsprozessen resultierende Erhöhung ausgleichen.
Abschließend werden zwei Szenarien (Hoch- und Niedrigverbrauch) der künftigen Gasversorgung Deutschlands bis 2030 aufgestellt. Im Hochverbrauchszenario wird damit gerechnet, dass der Gaseinsatz in Deutschland um 17 % steigen wird. Im Niedrigverbrauchszenario wird er dagegen um etwa 17 % sinken. Gleichzeitig wird der Anteil von Biomethan am eingesetzten Gas auf 8 bzw. 12 % ansteigen. Die - direkten und indirekten - Treibhausgasemissionen der Gasnutzung in Deutschland werden im Niedrigverbrauchszenario um 25 %, d. h. überproportional von 215,4 Mio. t CO2-Äq auf 162,4 Mio. t CO2-Äq zurückgehen. Im Hochverbrauchsszenario steigen die Gesamtemissionen leicht um 7 % (auf 230,9 Mio. t CO2-Äq) an.
Schlussfolgerungen: Gasförmige Energieträger werden in den kommenden beiden Dekaden eine zentrale Säule der deutschen Energieversorgung bleiben. Insgesamt zeigt sich, dass die THG-Emissionen der Nutzung von Erdgas v. a. von den Verbrauchsmengen der Gasversorgung abhängig sind. Das heißt, dass sowohl aus klima- als auch aus energiepolitischer Sicht die Steigerung der Energieeffizienz ein zentraler Faktor ist. Daneben bestehen sowohl in der verstärkten Nutzung von Biomethan als auch in der weiteren Investition in emissionsoptimierte Technologien entlang der Vorketten signifikante Emissionsminderungspotenziale. Hierdurch kann die "Klimaqualität", d. h. die spezifische Treibhausgasemissionshöhe über alle Prozessstufen, des eingesetzten Gases deutlich verbessert werden. Die spezifischen Gesamtemissionen pro TJ eingesetzten Gases werden hierdurch um ca. 9 % von heute 63,3 t CO2-Äq pro TJ auf etwa 54,5 t/TJ sinken. Entscheidend ist hierfür der verstärkte Einsatz von Biomethan, dessen Verbrennung aufgrund der biogenen Herkunft des Kohlenstoffs weitgehend klimaneutral ist (im Vergleich zu direkten Emissionen von 56 t CO2/TJ bei der Verbrennung von Erdgas oder 111 t CO2/TJ bei z. B. Braunkohle). Die Vorteile der gasförmigen Energieträger in der Klimaqualität und effizienten Nutzung werden - insbesondere auch in der künftig zu erwartenden Beimischung von Biomethan - auch zukünftig Bestand haben.
This paper undertakes a step to explaining the international economics of resource productivity. It argues that natural resources are back on the agenda for four reasons: the demand on world markets continues to increase, the environmental constraints to using resources are relevant throughout their whole life cycle, the access to critical metals could become a barrier to the low carbon economy, and uneven patterns of use will probably become a source of resource conflicts. Thus, the issue is also of relevance for the transition to a low carbon economy. "Material Flow Analysis" is introduced as a tool to measure the use of natural resources within economies and internationally; such measurement methodology now is being harmonized under OECD auspices. For these reasons, the paper argues that resource productivity - that is the efficiency of using natural resources to produce goods and services in the economy - will become one of the key determinants of economic success and human well-being. An empirical chapter gives evidence on time series of resource productivity increases across a number of economies. Introducing the notion of "material flow innovation", the paper also discusses the innovation dynamics and issues of competitiveness. However, as the paper concludes, market barriers make a case for effective resource policies that should provide incentives for knowledge generation and get the prices right.
This paper reviews the current EU policy framework in view of its impact on hydrogen and fuel cell development. It screens EU energy policies, EU regulatory policies and EU spending policies. Key questions addressed are as follows: to what extent is the current policy framework conducive to hydrogen and fuel cell development? What barriers and inconsistencies can be identified? How can policies potentially promote hydrogen and fuel cells in Europe, taking into account the complex evolution of such a potentially disruptive technology? How should the EU policy framework be reformed in view of a strengthened and more coherent approach towards full deployment, taking into account recent technology-support activities? This paper concludes that the current EU policy framework does not hinder hydrogen development. Yet it does not constitute a strong push factor either. EU energy policies have the strongest impact on hydrogen and fuel cell development even though their potential is still underexploited. Regulatory policies have a weak but positive impact on hydrogen. EU spending policies show some inconsistencies. However, the large-scale market development of hydrogen and fuel cells will require a new policy approach which comprises technology-specific support as well as a supportive policy framework with a special regional dimension.
The papers for this special issue were originally contributed to the 2nd International Wuppertal Colloquium on "Sustainable Growth, Resource Productivity and Sustainable Industrial Policy - Recent Findings, new Approaches for Strategies and Policies" that was held from 10 to 12 September 2009 in Wuppertal, Germany. The intensive discussion during the Colloqium and the subsequent rigorous review process have helped to facilitate this process - we wish to thank all participants and contributers, as well as Sevan Hambarsoomian and Deniz Erdem for administrative support.
This study provides insight into the feasibility of a CO2 trunkline from the Netherlands to the Utsira formation in the Norwegian part of the North Sea, which is a large geological storage reservoir for CO2. The feasibility is investigated in competition with CO2 storage in onshore and near-offshore sinks in the Netherlands. Least-cost modelling with a MARKAL model in combination with ArcGIS was used to assess the cost-effectiveness of the trunkline as part of aDutch greenhouse gas emission reduction strategy for the Dutch electricity sector and CO2 intensive industry. The results show that under the condition that a CO2 permit price increases from €25 per tCO2 in 2010 to €60 per tCO2 in 2030, and remains at this level up to 2050, CO2 emissions in the Netherlands could reduce with 67% in 2050 compared to 1990, and investment in the Utsira trunkline may be cost-effective from 2020–2030 provided that Belgian and German CO2 is transported and stored via the Netherlands as well. In this case, by 2050 more than 2.1 GtCO2 would have been transported from the Netherlands to the Utsira formation. However, if the Utsira trunkline is not used for transportation of CO2 from Belgium and Germany, it may become cost-effective 10 years later, and less than 1.3 GtCO2 from the Netherlands would have been stored in the Utsiraformation by 2050. On the short term, CO2 storage in Dutch fields appears more cost-effective than in the Utsira formation, but as yet there are major uncertainties related to the timing and effective exploitation of the Dutch offshore storage opportunities.
The physical dimension of international trade. Part 1: Direct global flows between 1962 and 2005
(2010)
The physical dimension of international trade is attaining increased importance. This article describes a method to calculate complete physical trade flows for all countries which report their trade to the UN. The method is based on the UN Comtrade database and it was used to calculate world-wide physical trade flows for all reporting countries in nine selected years between 1962 and 2005. The results show increasing global trade with global direct material trade flows reaching about 10 billion tonnes in 2005, corresponding to a physical trade volume of about 20 billion tonnes (adding both total imports and total exports). The share from European countries is declining, mainly in favour of Asian countries. The dominant traded commodity in physical units was fossil fuels, mainly oil. Physical trade balances were used to identify the dominant resource suppliers and demanders. Australia was the principal resource supplier over the period with a diverse material export structure. It was followed by mainly oil-exporting countries with varying volumes. As regards to regions, Latin America, south-east Asian islands and central Asia were big resource exporters, mostly with increasing absolute amounts of net exports. The largest net importers were Japan, the United States and single European countries. Emerging countries like the "Asian Tigers" with major industrial productive sectors are growing net importers, some of them to an even higher degree than European countries. Altogether, with the major exception of Australia and Canada, industrialized countries are net importers and developing countries and transition countries are net exporters, but there are important differences within these groups.