توانا سازی فن آوری برای مدیریت تقاضای انرژی صنعتی
|کد مقاله||سال انتشار||مقاله انگلیسی||ترجمه فارسی||تعداد کلمات|
|8825||2008||10 صفحه PDF||سفارش دهید||8977 کلمه|
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Publisher : Elsevier - Science Direct (الزویر - ساینس دایرکت)
Journal : Energy Policy, Volume 36, Issue 12, December 2008, Pages 4434–4443
This state-of-science review sets out to provide an indicative assessment of enabling technologies for reducing UK industrial energy demand and carbon emissions to 2050. In the short term, i.e. the period that will rely on current or existing technologies, the road map and priorities are clear. A variety of available technologies will lead to energy demand reduction in industrial processes, boiler operation, compressed air usage, electric motor efficiency, heating and lighting, and ancillary uses such as transport. The prospects for the commercial exploitation of innovative technologies by the middle of the 21st century are more speculative. Emphasis is therefore placed on the range of technology assessment methods that are likely to provide policy makers with a guide to progress in the development of high-temperature processes, improved materials, process integration and intensification, and improved industrial process control and monitoring. Key among the appraisal methods applicable to the energy sector is thermodynamic analysis, making use of energy, exergy and ‘exergoeconomic’ techniques. Technical and economic barriers will limit the improvement potential to perhaps a 30% cut in industrial energy use, which would make a significant contribution to reducing energy demand and carbon emissions in UK industry. Non-technological drivers for, and barriers to, the take-up of innovative, low-carbon energy technologies for industry are also outlined.
1.1. Background The 2007 Energy White Paper (Department of Trade and Industry, 2007) accepted that Britain should put itself on a path to achieve significant carbon reductions, mainly by adopting a range of energy efficiency measures and renewable energy technologies. Techniques for carbon capture and storage (or ‘carbon sequestration’) were also identified as an important element in any energy research, development and demonstration (RD&D) programme. Targets for new renewable electricity supply were set at 10% by 2010 and 20% by 2020. It is going to be difficult for renewables (principally wind power) to fill the ‘electricity gap’. The UK Government is supportive of building a new generation of nuclear reactors to replace those currently undergoing, or approaching, decommissioning (Department of Trade and Industry, 2007). This, together with carbon capture and storage technologies and an increased reliance on imported natural gas for combined cycle gas turbine plants, might represent the future of the electricity supply side. Carbon dioxide (CO2) accounts for some 80% of the total greenhouse gas emissions in the UK (Department of Trade and Industry, 2000). On the supply side, the energy sector is responsible for around 95% of these emissions, whereas on the demand side the industrial sector accounts for around 30%. The switch from coal to natural gas stimulated by energy market liberalisation has had a favourable, but relatively short term, effect on greenhouse gas emissions. Consequently, the legally binding post-Kyoto EU target of reducing a basket of greenhouse gases to 12.5% below 1990 levels over the period 2008–2012 will require only modest governmental intervention, over and above falls in emissions stimulated by energy market liberalisation. But the UK adopted a tighter ‘domestic’ goal in 1997 aimed at a 20% cut in CO2 emissions below 1990 levels by 2010. Recent trends in national CO2 emissions indicate that it is unlikely that this national target will be met, and this has recently been recognised by the UK Government. However, in the medium term, even greater carbon reductions will be required in order to stabilise the global climate system. The Royal Commission on Environmental Pollution (2000), for example, has argued that the UK should take the lead, by adopting a target of reducing CO2 emissions by some 60% from 1997 levels by about 2050. The UK Government is presently committed, through its 2007 Energy White Paper, to developing a sustainable energy economy in the 21st century and to taking a lead in reducing CO2 emissions among the industrialised countries (i.e. those of the Organisation for Economic Co-operation and Development). An aspirational target of reducing these emissions to 60% of their existing figure by 2050 has been adopted in line with the Royal Commission on Environmental Pollution recommendation. The only way in which this fall could be achieved is by significantly reducing primary energy consumption to 45–75% of the present demand (Hammond, 2003), depending on the energy technology mix (fossil fuels, nuclear power or renewable energy technologies). This requires the widespread adoption of energy-saving measures across the economy that, in turn, would necessitate action by many individual stakeholders. It is in this context that this state-of-science review sets out to provide an indicative assessment of enabling technologies for reducing UK industrial energy demand and carbon emissions out to 2050. In the short term, during the period that will rely on the adoption of current or existing technologies, the road map and priorities are relatively clear. But the prospects for the commercial exploitation of innovative technologies by the middle of the 21st century are highly speculative. Emphasis is therefore laid on the range of technology assessment methods that are likely to provide policy makers with a guide to the potential for improvements. Key among the appraisal methods applicable to the energy sector is thermodynamic analysis: energy, exergy and ‘exergoeconomic’ techniques. They provide an indication of the maximum improvement potential available from different enabling technologies. These approaches are supplemented by useful techniques such as environmental life-cycle assessment (LCA), environmental cost–benefit analysis and the generation of cost curves. 1.2. Character of the industrial sector The industrial sector in the UK is the only one that has experienced a significant fall of roughly 40% in final energy demand since the first oil price shock of 1973/1974 (see Fig. 1). This was in spite of a rise of over 40% in industrial output in ‘value added’ terms. However, the consequent aggregate reduction in energy intensity (MJ/£ of gross value added) masks different underlying causes: • End-use efficiency: It has been estimated (Engineering Council, 1998) that around 80% of the fall in industrial energy intensity between 1965 and 1995 was induced by the price mechanism. • Structural changes in industry: The relative size of the industrial sector has shrunk, with a move away from heavy industries (Hammond, 1998), particularly in manufacturing and mining, as well as the adoption of more energy-efficient technologies (like electric arc processing). Many industrial sub-sectors have undergone major rationalisations, thus enabling significant energetic and financial economies of scale. • Fuel switching: Coal use in UK industry has declined steadily since the early 1960s in favour of ‘cleaner’ fuel (Hammond, 1998; Hammond and Stapleton, 2001). Oil use also fell rapidly from 1973 onwards, with a couple of step changes associated with the two price hikes in the early 1970s and early 1980s (see Fig. 1). Both natural gas and electricity consumption increased to market shares of some 25% and 33%, respectively. They are cleaner, more readily controllable and, arguably, cheaper for the business concerned. The industrial sector is very diverse in terms of manufacturing processes, ranging from highly energy-intensive steel production and petrochemicals processing to low-energy electronics fabrication. Whereas the former typically employs large quantities of (often high-temperature) process energy, the latter tends to be dominated by energy uses associated with space heating. Future Energy Solutions and the Carbon Consortium (2005) identified around 350 separate combinations of sub-sectors, devices and technologies in their recent study of the potential for carbon reduction from UK industry. Each combination offers quite different prospects for energy efficiency improvements and carbon reductions, which are strongly dependent on the specific technological applications. This large variation across industry does not facilitate a cross-cutting, ‘one size fits all’ approach to the adaptation of new technologies in order to reduce energy demand, but, rather, requires tailored solutions for separate industries. Conversely, certain behavioural or good-practice measures are suitable for adoption across the board precisely because of their explicit independence from the type of technology employed. In the period up to 2030, the European Commission expects that the EU25 economy will continue to be more focused towards ‘high value added’ products, which are less material- and energy-intensive, as well as undergoing restructuring in favour of services (European Commission, 2002). It believes that the potential for reducing CO2 emissions emanating from industry is likely to be limited. Others take a more optimistic view: see, for example, Hammond and Stapleton (2001) and von Weizsacker et al. (1999). Best available electrical technologies and heat pumps have been proposed by the Commission as attractive and cost-effective options, while acknowledging that this will incur additional costs over and above the baseline scenario out to 2010; perhaps 14–30% for energy-intensive industries and 9–21% for others.
نتیجه گیری انگلیسی
The only way the 2050 Royal Commission on Environmental Pollution carbon reduction target—60% from 1997 levels by about 2050—could actually be achieved is by significantly reducing primary energy consumption to 45–75% of the present figure. This requires the widespread adoption of energy-saving measures across the economy, and that has been acknowledged in the 2007 Energy White Paper (Department of Trade and Industry, 2007). This state-of-science review has set out to provide an indicative assessment of enabling technologies for reducing UK industrial energy demand and carbon emissions out to 2050. In the short term, in the period that will rely on the adoption of current or existing technologies, the road map and priorities are relatively clear. Here, there is a variety of available technologies that will lead to a reduction in the demand for energy in industrial processes, boiler operation, compressed-air usage, electric-motor efficiency, the effectiveness of heating and lighting systems and other ancillary uses (such as transport). But the prospects for the commercial exploitation of innovative technologies by the middle of the 21st century are highly speculative. Emphasis is therefore placed on the range of technology assessment methods that are likely to provide policy makers with a guide to progress in the development of high-temperature processes, improved materials, process intensification and improved industrial process control and monitoring. It is in these areas that thermodynamic analysis can make a major contribution to identifying where the improvement potential lies. For example, exergy analysis can provide an indication of the maximum improvement potential available from different enabling technologies. However, it is important to recognise that this ‘maximum’—perhaps an 80% improvement in end-use efficiency in some cases—cannot be achieved in practice. Technical and economic barriers will limit the improvement potential to something closer to 30%. Even that would make a significant contribution to energy demand and carbon reduction in UK industry. Recent trends in energy prices, specifically those of natural gas, and the implementation of national and European legislation have resulted in stronger drivers for industrial energy demand management technology. Innovation in ZLC technologies can secure both economic and environmental objectives. However, there still exist many barriers to the uptake of this technology, the most significant of which appears to be ‘ignorance, inertia and lack of interest’ (Carbon Trust, 2005). There is often poor awareness of baseline energy consumption, the specific ZLC technologies that are available and of the associated economics. Industry needs to be made aware of the portfolio of technology options that are likely to come on stream in the period to 2050. The Carbon Trust (2005) has argued for private and public support for such innovations (like those outlined in 3.2 and 4.2) in order to ‘move them down the cost curve to make them competitive’. Greater awareness of the importance of appraisal methods for industrial energy technologies (particularly the thermodynamic methods outlined in Section 2.2) needs to be encouraged in both the public and private sectors. The Research Councils, the Carbon Trust and the trade associations may have a crucial role to play here. Various policy instruments will inevitably be required to encourage the introduction of energy efficiency measures in the face of market barriers. The two main candidates for intervention are economic instruments (carbon and/or energy taxes, and traded permits) and utility regulation in the wider interests of environmental protection. The Royal Commission on Environmental Pollution (2000) and others favour replacing the present Climate Change Levy with a general carbon tax based on CO2 emitted per unit energy supplied. This should be applied upstream, where fossil fuels are first purchased, and cover all sectors. The Royal Commission argued (2000) that carbon tax revenues should then be employed to reduce fuel poverty, invest in energy efficiency measures, increase the viability of other low-carbon energy alternatives and to protect UK industrial competitiveness. The 2007 Energy White Paper advocated building and product efficiency standards, CO2 emissions trading, tax incentives, and advice and information, alongside the EU Emissions Trading Scheme.