Is Brexit an opportunity to rethink UK carbon pricing?

The UK’s exit from the European Union will make changes to UK carbon pricing unavoidable. Given the complexities and inefficiencies of the current policy mix, could Brexit be viewed as an opportunity for radical policy change in this area? And, if so, what is likely to be the best outcome?

The UK played a critical role in establishing the EU Emissions Trading System (EU ETS), the EU’s flagship climate policy. The UK has also provided an important and influential voice in the repeated attempts to reform the scheme and to tighten the overall cap. Despite the continuing problems of oversupply and low carbon prices, the EU ETS remains the EU’s flagship climate policy, and looks likely to retain that status for quite some time. In this context, Brexit creates two important challenges. It creates uncertainty about the future development of:

  • UK carbon prices with potentially negative implications for low-carbon investment in the UK
  • EU carbon prices, including the risk that Phase 4 of the EU ETS will be less stringent as a result of the UK’s withdrawal. If EU allowance prices continue on their downward trajectory, the limited incentives provided by the EU-ETS will be further undermined.

The timing of any changes in the UK’s involvement in the EU-ETS is important and will depend upon the broader timing of the Brexit process, and in particular when Article 50 is triggered. The preferred breakpoint for changes to the UK’s involvement would be end-December 2020 when Phase 3 comes to an end. If, however, the breakpoint comes earlier during Phase 3 or (more likely) later during Phase 4, it is likely to create messy difficulties in managing the transition which will only add to the burden on civil servants – as well as increasing the uncertainty for investors.

The nature of the UK’s future involvement in the EU-ETS is likely to be critical for the success of UK climate policy – and early guidance on this will be important for investor confidence. At present, there appear to be three options for UK carbon pricing post-Brexit, namely the Norway model, the Linking model and the Unilateral model.

The Norway model would involve the UK joining the European Economic Area (EEA) and thereby gaining full access to the single market. This would require the UK to fully adopt EU standards and regulations, including the EU ETS. This model currently applies to Iceland and Liechtenstein, as well as Norway, and, since it allows full participation in the EU ETS, would involve the minimum of changes to UK legislation. The critical drawback of this model is that it gives the UK little or no influence on the content of relevant EU legislation, including future targets in the EU ETS. Since this runs counter to the intent of the ‘Leave’ campaign, full participation in the EAA seems unlikely to be politically feasible, thereby ruling out the ‘Norway model’ for the EU ETS.

The Linking model would involve the UK establishing its own emissions trading scheme and then negotiating a bilateral link with the EU ETS under the terms of Article 25 of the Directive. This approach is currently being followed by Switzerland – although the agreement has not been finalised. Switzerland is one of four members of the European Free Trade Association (EFTA) and, although joining EFTA may bring some benefits to the UK, it should not be a precondition for establishing a link to the EU ETS. Creating a separate emissions trading scheme and negotiating the terms of linking is likely to be a time-consuming process, although it could be greatly simplified by modelling the UK scheme as closely as possible on the current rules of the EU-ETS.

The main benefit of linking would be to reduce UK compliance costs through EU-wide allowance trading. But if the EU allowance price continues to be extremely low throughout Phase 4, this could also be considered a drawback. Oversupply in the EU ETS led the UK to impose a Carbon Price Floor (CPF) on the fuels used for electricity generation as a second-best means of encouraging domestic low-carbon investment. But while this may facilitate the low carbon transition in the UK, it provides no additional environmental benefit. Any additional abatement in the UK simply ‘frees up’ EU allowances that can be either sold or banked, and hence used for compliance elsewhere within the EU ETS, with the result that the CPF achieves no additional reduction in carbon emissions.[1] In addition, while the CPF raises the net carbon price faced by UK installations, it lowers the EU ETS allowance price. This means that any additional incentive to low carbon investment in the UK is offset by a reduced incentive for low carbon investment in the rest of the EU.

Identical comments apply to policies encouraging renewable electricity generation or improvements in the efficiency of electricity use. Hence, if the UK continues to participate within EU-ETS – either directly, or indirectly via a link – the ultimate environmental benefits of any policies that affect the ‘trading sectors’ in the UK will be contingent on the stringency of the EU-ETS cap. And post Brexit, the UK will no longer have any influence on the negotiation of that cap.

A third way: the UK establishes its own carbon pricing scheme

These problems point to the potential benefits of a third Unilateral model in which the UK establishes its own domestic carbon pricing scheme, but does not – at least at this stage – seek a link to the EU-ETS. This could take the form of a domestic emissions trading scheme, or it could be a revenue neutral carbon tax that either covered the same sectors or extended more widely throughout the economy. For example, such a tax could apply downstream to the public, commercial and industrial sectors, or upstream to fossil fuel producers – thereby encompassing the entire economy.

Of these two options, a carbon tax with a broad tax base has much to commend it. At present, the UK has a complex and overlapping mix of policies, including the Climate Change Levy, Climate Change Agreements, Carbon Price Floor and (until 2019) the Carbon Reduction Commitment. These policies  distort the incentives for emission reduction between sectors and fuels, increase the administrative burden for industry and regulators, and create opportunities for rent seeking and regulatory capture. As demonstrated by this report from 2002, this problem goes back many years.

Withdrawal from the EU ETS could provide the opportunity to rationalise and simplify this policy mix, while at the same time replacing the low and volatile carbon price from the EU-ETS with a higher and stable carbon price that gave confidence to investors and underpinned the UK carbon budgets. In the absence of a link to the EU-ETS, such a tax would also ensure that low carbon investment in the UK led to real emission reductions. With a wide base, such tax could also generate substantial revenue that could be used to reduce distortionary taxes, compensate losers or fund other low carbon investments.

As ever, the major political obstacles to such a tax would be the potential impact on low-income households and on energy intensive industries. These obstacles also apply to the EU-ETS, but the low carbon prices observed to date have made them less salient. Although these obstacles are challenging to resolve, potential solutions are available for both. For example, unlike the levies used to fund schemes such as the Renewables Obligation, the revenue raised from a carbon tax may be used to compensate low-income households. Similarly, energy intensive industries could potentially be protected through a system of border carbon adjustments (BCAs). While this would be challenging to establish, the UK’s exit from EU may make the process more straightforward.

In addition, a domestic carbon tax would not rule out the benefits of international carbon trading, since it should be feasible to develop some form of link in the future – either to the EU ETS, or to the broader international scheme that may evolve from the Article 6 of the Paris Agreement. For example, companies could be allowed to pay taxes at a higher level than their obligation and thereby receive tax credits that could be sold into an ETS. A robust carbon pricing scheme in the UK may also have an indirect but potentially positive influence upon future negotiations of the EU ETS, through encouraging agreement on a more stringent cap.

The political and practical challenges of redesigning UK carbon pricing should not be underestimated. Moreover, given the current political climate and the multiple difficulties created by Brexit, the political will to do so may not be there. Nevertheless, the UK’s exit from the EU makes significant changes to the current system unavoidable. Given the drawbacks of the Norway and Linking models, and the complexities and inefficiencies of the current policy mix, Brexit could be viewed as an opportunity (a policy window) for radical policy change in this area.

[1] The resulting allowance surplus and low carbon price may encourage the negotiation of a more stringent cap in subsequent phases, but this indirect impact is highly uncertain.

Professor Sorrell is currently Professor of Energy Policy in the Science Policy Research Unit (SPRU) at the University of Sussex, Co-Director of the Centre on Innovation and Energy Demand (CIED) and member of the Sussex Energy Group (SEG).Steve Sorrell

*Image by Arnold Paul cropped by Gralo shared under Creative Commons licence (CC BY-SA 3.0)

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We Need a Lorry-Load of Energy Savings; in the new ECO, the Government Delivers a Hatchback

by Jan Rosenow and Richard Cowart

The United Kingdom was once a world leader in energy savings. We proved that investing in buildings, insulating lofts, and switching to efficient boilers, motors, and lighting created jobs, saved money, and lowered the environmental costs of energy systems. But in recent years we have turned our back on our own evidence, reducing the breadth and depth of energy efficiency programmes.

In this less ambitious scene, the government has finally revealed its plans for the next phase of the Energy Company Obligation (ECO). Happily, the new version contains some important design improvements over earlier plans. Unhappily, the programme as a whole is still too narrow and too small, failing to deliver bill savings to the vast majority of UK households (businesses remain unserved too). Read more ›

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Exergy Economics Workshop 2016

Over 40 economists, engineers and social scientists converged last week on the sunny University of Sussex campus for the second International Exergy Economics Workshop. Organised by the Centre on Innovation and Energy Demand (CIED) and the Centre on Industrial Energy, Materials and Products (CIE-MAP), the workshop was a chance for researchers to come together to share knowledge, discuss progress, and initiate future research collaborations in exergy economics.

Exergy economics is a nascent and heterodox approach to studying energy use within the economy. It is differentiated from conventional energy economics in its use of useful exergy as a measure of the quantity of energy flows, as opposed to the more conventional indicators of primary or final energy.

photo of participants standing on some grass outside

Participants who took part in the Exergy Economics workshop 2016.

But what is useful exergy? For an in-depth explanation, see the exergy economics website. In brief, exergy is a measure of the ability of an energy flow to perform physical work, a form of energy which is of a very high thermodynamic quality. Thermal energy – heat – is of an intrinsically low quality, in the sense that it cannot be fully converted to other energy forms, such as electricity. Whereas energy cannot be created nor destroyed – merely converted from one form to another – exergy can, and is, dissipated (destroyed) in every real conversion process. Simply adding together thermal and kinetic (motion) energy on a like-for-like basis is equivalent to adding apples and oranges. This fact has implications for the consistency of macro-level economic studies on energy use.

As an example, consider a can of kerosene within an insulated room. When burned, this slightly raises the room temperature, although the total amount of energy in the room is conserved. The quality of the energy, however, has diminished. In the form of heat it is less able to perform physical tasks (such as moving a car) than the initial chemical energy in the fuel. This is because the exergy which was initially present has largely been destroyed.

The second distinct aspect of exergy economics is that rather than the primary or final stages of the energy chain, it is the useful stage – the output of end-use conversion devices such as cars, furnaces or space heaters, for example – that is focused upon; hence the term useful exergy. Although it’s more difficult to estimate the useful energy (or exergy) output of these devices at the national level, it is useful exergy that is required to fulfil the need for society’s energy services (personal and freight mobility, illumination, thermal comfort, etc).

Whilst the burgeoning exergy economics literature is complementary to more conventional energy economics, it can potentially provide interesting new insights. In particular, evidence has emerged suggesting that useful exergy consumption provides a much larger contribution to growth in economic output than is implied by its smallcost share” (i.e. the share of national accounts representing payments to the energy sector). This possibility raises implications for the feasibility of easily achieving decoupling of energy consumption from economic growth, and in turn the ability to achieve carbon reduction commitments alongside continued growth in output.

The two-day workshop was organised as a means for showcasing the progress in, and raising the profile of, exergy economics. Attendees were encouraged to critically reflect upon the framework and answer the following questions:

  1. What are the strengths, weaknesses and state-of-the-art in exergy economics research?
  2. What are the conflicts and synergies between exergy economics and mainstream economics?
  3. What are the contributions of exergy economics to climate change and sustainability analysis?
  4. What are the potential policy implications of this work?
  5. Which future research directions in the area appear most promising?

To answer these questions, the workshop incorporated a number of parallel sessions, as well as more reflective breakout groups, facilitating numerous interesting discussions and insights. Attendees were challenged to define new areas of research, and many productive research collaborations are likely to emerge from it. A number of general themes emerged:

  • The link between useful exergy, energy services and human well-being: Whilst useful exergy has to date been a valuable way of describing the energy system from primary to useful stages, there is also promising potential for the field in describing the relationship between energy services (e.g. thermal comfort, transport and illumination), material services, and human well-being. If we can define a level of services needed for well-being – cooking requirements in a developing context, for example – what are the commensurate useful exergy (and thus primary energy) needs, and, in turn, what environmental impacts can be expected from this? A number of researchers are currently examining these links using an interesting variety of epistemological frameworks.
  • New insights into suppressing the environmental impacts of energy use: The concept of energy and material efficiency is at the centre of useful exergy analysis. Analysing energy systems from an exergy point of view can help us to locate the ‘low-hanging fruit’ of efficiency improvements and reduce carbon emissions. Furthermore, what are the policy implications for carbon reduction commitments if it is more difficult to decouple energy use from economic output than previously thought? Lastly, exergy may provide a basis for measuring the scarcity of a natural resource; given resource depletion concerns, how might we harness this to consider shifting taxation away from capital and onto environmental degradation?
  • The relationship between energy use and economic output: As mentioned, there are already some very interesting insights emerging using exergy analysis. But how might this area of research be extended? Different measures of output, new models, and a greater focus on the role of money and finance were all discussed. Moreover, how does the community reach out to mainstream economics more effectively? Michael Kumhof, director of research at the Bank of England, presented a fascinating plenary to the attendees on the significant role that energy (and particularly oil) plays in economic output.

In all, the workshop was very successful, and participants came away with an enhanced understanding both of the critical environmental issues facing society today, and of one technique for understanding them. Of course, as humble interdisciplinary researchers, we acknowledge the limitations of any one method of enquiry for solving a plethora of complex societal issues. But we believe that exergy economics has great potential for providing us with insights both new and exciting.

For more information on this event, as well as exergy economics more broadly, visit the exergy economics website.

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Back to the DTI? – The merger of DECC and BIS is a new opportunity to integrate energy and industrial policies

Department of Energy & Climate Change, Westminster (image by Nigel Cox and licensed for reuse under this Creative Commons Licence)

Department of Energy & Climate Change, Westminster (image by Nigel Cox and licensed for reuse under this Creative Commons Licence)

As part of the new Prime Minister’s extensive reshuffle late last week, it was announced that the Departments of Energy and Climate Change (DECC) and Business, Innovation and Skills (BIS) are to merge to form a new Department of Business, Energy and Industrial Strategy (BEIS). Taken at face value, this looks like a backwards step to a time when energy and climate policy were much less important. But is the creation of BEIS necessarily a bad thing? Read more ›

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South Africa: could gas pave the way towards greener sources of energy?

In South Africa, the process of mining coal for power generation or for export is increasingly becoming difficult, because the ability to source finances in a carbon conscious market is limited. The country wants to reduce its dependence on coal and believes that in order to meet uncertain electricity demand, a smaller, more modular, and flexible form of electricity generation is needed. Liquefied natural gas (LNG), which burns more cleanly than any other fossil fuel, is deemed critical for paving the way towards an energy transition from dirtier coal to a greener source of energy. Gas complements not only renewable energy penetration, but it also speaks to regional trade ambitions within the Southern African Development Community (SADC), energy diversification, as well as integration into re-industrialization policies.

Coal miner with a helmet and headlamp

Coal miner returning home after his shift underground. Sourcing financing for coal mining is becoming more difficult in an increasingly carbon conscious market. Credit: Jan Truter (CC BY-NC-ND 2.0)

The technology to transport LNG via ships is also becoming more sophisticated, which would allow it to bypass the conventional route of pipelines. Therefore, a co-evolution of technology maturity, market dynamics, user preferences, energy and industrial policy are aligning to enable gas use in the country.

With this as its backdrop, South Africa launched its Gas Industrialization Unit (GIU) on 16 May 2016 in Cape Town. There are no indications as yet as to where the LNG may be imported or which ports are likely to be the first to gain such an initiative. This is now the second gas initiative by the government. Earlier last year the Department of Energy directed the department to procure a 3.12 GW gas-fired power plant to contribute towards the energy security of the country through the Independent Power Producer Programme (IPP).

It is envisaged that the Gas IPP will serve as a catalyst for industrial development, as it has been indicated that gas could also be a feedstock for new industrial uses, a source of heat for industrial process and for conversion of Gas to Liquid fuels (GTL). Although South Africa does have potential domestic shale gas reserves located within the Karoo region, this development will take many years to realise. Thus, the immediate plans for the Gas IPP is to import Liquefied Natural Gas (LNG) through its three ports: Saldanha Bay (West Coast near Cape Town), Coega (Port Elizabeth) and Richards Bay (Durban).

Both initiatives are running in parallel with significant coordination between actors that include government, industries, academia and state-owned entities.

The Gas IPP is thought at this preliminary stage to be coordinated in a bundled offshore project. This means the entire value chain from LNG sourcing, Floating Storage and Regasification Unit (FSRU), pipeline to shore, and gas to power plant is to be procured by an independent private entity. Naturally, this would mean that as the Gas IPP is rolled out, bidding would be in the form of a consortium that would require substantial coordination between upstream, midstream and downstream players. Implementation of this programme will prove a challenging task. The challenges include not only coordination between players, but also the dollar base indexation of import LNG prices, which will have a direct impact on domestic electricity tariffs in South Africa. The country is already facing huge public resistance to electricity increases and its domestic currency is weakening against the US dollar. There are also potential implications for existing regulations, such as the Gas Act, the Ports Act, and the Electricity Regulation Act (ERA), which have not yet been applied or tested with this new initiative.

Despite these challenges, there is a substantial push to use gas in the country. South Africa’s policy community keeps emphasising the importance of regional trade between SADC. The main drivers include significant offshore natural gas finds in northern Mozambique, particularly in the Rovuma Basin and Namibian Kudu gas fields. Botswana also has coal bed methane gas, a form of natural gas extracted from coal beds.

Interestingly, these developments are occurring during challenging major shifts in the global LNG market. Traditional buyers, such as Japan, are reducing their LNG imports due to their plans to restart their nuclear reactors. Moreover, countries such as Australia and the USA are starting to increase their capacity to export LNG through various infrastructure developments. Thus, the current perception is that a global supply glut of LNG is expected, with reorientation of traditional buyers and sellers. Furthermore, LNG is also increasingly being perceived as the new “oil” commodity, not only because oil is undergoing uncertainty, but also LNG is becoming easier to ship through advances in liquefaction technologies.

All this will make the South African gas policy and market developments interesting ones to follow.

Blanche Ting is currently a doctoral researcher based at the Science Policy Research Unit (SPRU) and a member of the Sussex Energy Group at the University of Sussex. Her research is focused on South Africa’s electricity system, with case studies on Independent Power Producers (IPPs), namely gas, renewable and coal and the implications on the dominant state owned monopoly of Eskom. She holds two Masters degrees in Climate Change and Development from the Institute of Development Studies (IDS), UK as a Mandela-Sussex Scholar (2011) and a Masters in Bioprocess Engineering from the University of Cape Town (2004). Her interests are energy transitions in resource base economies, particularly in Africa and Latin America.

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The views and opinions expressed here are solely those of the individual authors and do not represent Sussex Energy Group.

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