This paper investigates residential energy consumption in the UK by using a novel and topical approach based on behavioural analysis. A key lesson from recent advances in behavioural economics is that the responses of individuals to both policy incentives and uncertainty may differ from the predictions of classical rational optimising behaviour. By employing a focused case study approach using both quantitative and qualitative response analysis, it considers the motivations of residential householders in the UK to reduce fossil fuel use, with additional perspectives from UK landlords, a global environmental NGO, a senior politician, and two senior stakeholder strategy managers from a large energy company. Our interpretative behavioural analysis shows that a variety of incentives are necessary to encourage behaviour change. However, case study participants largely agree on the beneficial role of government regulation and efforts to “nudge” them in the right direction with regard to their energy use. As a means of more effectively reducing carbon dioxide emissions, we conclude that policy should focus on sustainable energy use. The findings allow us to understand why important recent policy initiatives such as the UK Green Deal failed to achieve their objectives and they suggest lessons for more effective incentive based policy making in the field of residential energy consumption.
This research aims to understand the motivations individuals have to save energy and/or use more renewable energy, so that policies such as the Green Deal can offer effective incentives. The central approach in this paper is to report on the actually observed behaviour and responses of a selected group of energy consumers extended to take account of the intentions and responses of residential landlords, policy makers and energy companies. The core of the results is a set of case studies and follow-up interview analysis. These reveal how typical policy incentives such as the UK Green Deal, which is explored in Section 2.3, are imperfectly designed and why they are likely to fail (as the Green Deal did after 3 years of operation). The approach is a new way of evaluating energy policy, and the analysis centres on two important innovations in research procedure. First, the methodology takes engineering based quantitative data obtained in the form of temperature and energy use by case study participants. We then analyse qualitative data on participants’ energy use by using social science research methods, and interpret our findings through the lens of behavioural economics literature. This mixed methodology allows triangulation of quantitative and qualitative data to confirm our findings, which are considered appropriately to contrast with the incentives offered in efficiency incentivising policies such as the Green Deal that was used in the UK between 2013 and 2015.
The research aims to clarify several aspects concerning the motivations behind domestic energy use, specifically:
1) From the observed behaviour of case study participants we can infer the outlines of an effective energy efficiency policy for domestic energy users such as:
・ If the true cost of carbon emissions is not incorporated in the policy, how does this diminish the attractiveness of the programme for domestic consumers of energy? The UK Green Deal, for example, failed to adopt this approach.
・ How best can energy efficiency incentives be simply constructed while sending clear signals about the costs of energy consumption. The UK Green Deal, for example, was unnecessarily convoluted and high transaction costs led to an uncompetitive interest rate.
・ Should energy savings be calculated on a net present value basis and how can certainty for most efficiency measures be introduced to avoid leading consumers to be wary of engaging with the domestic energy policy?
・ How can energy efficiency incentives avoid taking no account of the Rebound Effect? Most domestic participants taking part in this research agreed that they would be likely to spend energy efficiency savings made in their homes on other energy-using capital elsewhere in the economy.
2) How important is it to take account of behavioural responses to uncertainty in energy efficiency incentives? For example could “Nudging” approaches be seen by most domestic participants as an effective means of changing behaviour? Although this might not be used as a fast acting remedy, could it be more effective if used in tandem with government regulation?
3) Is there a disconnection between intention and behaviour with regard to domestic energy use, an impact on which would lessen the spur provided by energy efficiency incentives? The research is designed to reveal examples where domestic participants in the UK do not always align their intended energy using behaviour with their actual energy use behaviour. For example, some participants may allow thermal comfort to take precedence over their avowed intention to use energy more efficiently. In other words the motivation is lacking to achieve both aims.
The paper is organized in the following way: in the remainder of section one we discuss energy use; section two presents a literature review; in section three we present our methodology, and in section four present case study results and interpretation; section five concludes and discusses the implications of the research for policy development.
Energy use in buildings depends on the interaction between the occupants [
1) Occupants:
The energy requirements of the occupants need to be considered. Questions such as property tenure, number, income and age of occupants, the time the occupants spend in the property, their behaviour patterns/preferences and level of satisfaction while there, need to be addressed along with the implications for energy use.
2) The building fabric needs to be assessed in terms of type of construction, size, layout, design and energy efficiency.
3) Does the way energy is used in the building make economic sense? How efficiently spread is heating, lighting and ventilation throughout the building?
4) The location of the building is a key factor as the local climate could have a major impact on the energy requirements of the structure.
It is of significance to see how energy is consumed between sectors in the UK so that the relevance of the residential sector can be determined. Final energy consumption in 2010 for example was (
Sector | Percentage |
---|---|
transport | 35% |
domestic | 30.5% |
industrial | 17.3% |
commercial | 6.2% |
other-energy use non-energy use* | 5.7% 5.3% |
*non-energy use includes such items as chemical feedstocks, etc.
are to be displaced by renewable energy, and the UK government is to meet its target of reducing carbon emissions to 80% of 1990 levels by 2050. Renewable power sources are needed to supply the residential sector, and they must be developed in a way that balances the costs of reducing carbon dioxide emissions and thus the price paid by consumers, with the benefits of moving towards a zero carbon economy.
In the UK economy, for example, the most recent experience of a direct energy efficiency incentive scheme was the Green Deal which was started in January 2013, with the objective of encouraging residential property owners to install energy efficiency measures in their property and with a commensurate implied aim of a reduction in carbon emissions. Along with a new Energy Company Obligation (ECO) provided for in the Energy Act (2011) [
The core of such energy efficiency schemes is often designed as the provision of finance for the installation of domestic energy efficiency measures. The savings accrued from the more efficient use of energy provides the means of loan repayment, since energy efficiency investments are recouped through energy bill repayments. The financial charge can be to the property’s energy/electricity bill, and while remaining a charge connected to the house regardless of who occupies or owns it. This is why in the UK’s 2013-2015 example, the “Golden Rule”, which was a legal requirement, specified that any charge attached to an energy saving measure must be less than the expected savings from it. In this way the householder would, in theory, always benefit from having the energy efficiency measure installed in their property.
While direct incentivisation of energy efficiency in the home has now been largely discontinued in the UK; the emissions targets are challenging, so policy to encourage energy efficiency remains critical. An effective policy regime must be informed by an understanding of the financial and non-financial incentives which motivate householders to make improvements in the energy efficiency and sustainability of their property. This is especially important with regard to space and water heating which accounts for around 80% of residential energy use [
There have been many approaches to the assessment of occupant behaviour around energy use. Much of the work is based on conventional optimising models of rational economic agents. However, recent developments in behavioural economics, i.e. the incorporation into mainstream economics of findings from cognitive psychology and decision making, have led to considerable re-thinking about the design of incentive based policies to change behaviour. The early work on behavioural analysis of personal decision making was done by Kahneman and Tversky, and it is well described by Kahneman [
In this section we analyse the behavioural economics literature, including how a person’s social identity determines their choices [
Mainstream Expected Utility Theory (EUT) purports that decisions between alternatives are made on the basis of the utility value of outcomes [
A recurrent theme in Thaler [
Nudge theory, whose foundations stem from Kahneman’s work on heuristics [
In addition the Rebound Effect [
James’ [
Heuristics in “nudge” theory-overview (Thaler & Sunstein, 2009) | |
---|---|
1. Anchoring and adjustment | Using known facts and adjusting them to estimate or decide something which is unknown. |
2. Familiarity and Status quo bias | The more familiar something is, the more frequently, it is used/communicated. A misplaced sense of trust may be developed. These heuristics are influenced by advertising and mass media, and fear of the unknown. |
3. Over-optimism | People tend to under-estimate costs, timescales, and challenges, and to over-estimate rewards and the ease of dealing with unknown things. |
4. Loss aversion | The tendency for people to value actual possessions (or gains) more than potential possessions (or gains)-this creates inertia and impedes making changes. People do not like to lose possession of things, irrespective of their actual value/importance. |
5. Framing | Framing is an individual’s method of heuristically understanding reality. It can therefore include many ways of distorting the attractiveness/unattractiveness of something. |
6. Conforming with the population | People have the need for affirmation, and wish to avoid risk or embarrassment. Cultural factors enhance these effects. |
that reductions of under 2% per annum are likely to be delivered by 2020 (under the assumption of business as usual), when in fact overall reductions of approximately 6% per annum are needed to meet legally binding government targets. Interestingly, this research concludes the key barrier to achieving satisfactory residential carbon emission reduction is psychological.
In 2009, 15% of direct UK CO2 emissions were from the residential sector and this increased to 27% if indirect emissions are included. Clearly there is significant potential for the reduction of emissions via energy efficiency.
The figure shows that the absolute value of CO2 emissions has remained largely unchanged, and James [
Second, the switch from coal to gas-fired electricity generation in the 1990s resulted in a small decline in indirect emissions, and this helped to outweigh the increasing use of electricity to power household appliances. The Committee on Climate Change (CCC) [
homes resulting in a fairly flat profile for direct residential emissions observed in
The CCC’s 3rd Carbon Budget 2018-2022 [
Despite these ambitious sounding targets, the third carbon budget would deliver only 1.7% annual emissions reductions (proportion of direct emissions from the residential sector in
the cumulative effect of energy-saving measures. There is no implied recognition of any rebound effect in these budgets.
In this section we review the design of the most ambitious UK government policy to enhance residential energy saving; this was the incentive scheme called the “Green Deal”. The main components of the Green Deal scheme were on-site assessment, the installation of the efficiency measures, the provision of finance and the facility to attach a charge to a property’s energy bill, and the delivery of continuing advice and support to consumers [
The Green Deal Plan was a new type of interest bearing loan secured by a charge on the property and householders would be liable for the loan so long as they were the electricity bill payers at the property. To qualify for the Green Deal Plan, proposed energy efficiency measures installed were required to demonstrate predicted energy cost savings, which according to the Department of Energy and Climate Change website, would be mainly on space heating. A Green Deal Quality Mark, which could be used only by approved Green Deal assessors, providers and installers, was intended to reassure the public regarding the quality of energy improvements. The Green Deal provider set out the key terms of the contract with the consumer under the Green Deal Plan including interest rate (which was fixed) and repayment amounts. Repayments relating to Green Deal installations were collected by the electricity supplier via the electricity bill and passed on to the Green Deal Provider. Prospective purchasers or tenants of properties were alerted to the existence of a Green Deal Loan through mandatory Energy Performance Certificates (EPC). Green Deal loans were regulated under the Consumer Credit Act 1974. Separately to money owed to the Green Deal Provider, there may have been a charge to the householder for the Green Deal assessment, made by the initial Green Deal Assessor.
A basic structure of the Green Deal is represented in
Essentially then, the Green Deal attempted to incentivise householders to install energy efficiency measures by offering advice from trusted sources combined with a long term financing package that, it was hoped, consumers would find attractive. However, as we have described, the operation of the policy was highly complex and transaction costs were necessarily high.
From this review of energy saving incentives in theory and an important example in practice, it may be possible to learn lessons about policy design from a detailed analysis of the behaviour of a closely monitored group of participants in an energy consumption experiment. We now turn to describing the case study approach that we used to investigate these issues further.
The research involved modelling predicted energy use in seven case study properties based on both quantitative and qualitative data. Actual energy use was also measured at case study properties, and temperatures were recorded in the main living area and the main bedroom at each property. Qualitative data was gathered though interviews with one case study participant at each property. Further evidence of consumer attitudes was gained through semi structured interviews with stakeholder groups including landlords, an environmental group, an energy company, and a member of parliament. Case study participants also took part in a focus group session after most of the empirical research had been completed.
Following the literature [
Ideally we would have obtained a representative and unbiased subgroup drawn from the UK population. However, it was not feasible to obtain a random sample due to resource constraints and insufficient information about the potential sample population.
Given this information deficit, we chose to employ the technique of “snowballing”, which involves starting with one or two representative participants known to us, and then asking these participants to introduce the researcher to other members of the relevant population [
Once the participants had been selected by given ethical participation, we considered potential innate bias, but found that it was not a problem among this sample. Firstly because we had no prior knowledge of the opinions of any of the participants with regard to energy use and climate change. Secondly the specification of the precise interview questions had not been decided.
The sample participants were representative of the total potential population in the sense that their knowledge of energy use and climate change was expected to be similar, because 1) the participating householders were all familiar with the issues of energy use in houses through their professional experience; 2) the landlord participants were all aware of Green Deal initiatives; 3) the NGO, political and business respondents had specialised involvement with the use of energy policy in relation to the housing stock. We did not attempt to choose participants who were representative of the general potential population in other respects. For example, there was no deliberate choice made to achieve any balance in terms of gender, age, income or any other variable. However, the particular way in which the sample participants were representative of the total study population was considered sufficient in order to assess their motivations with regard to this research [
Hobo Pendant Temperature Data Loggers (UA-001-08) were calibrated and then placed in the main living room and the main bedroom in each case study property, and recorded temperature every 30 minutes. Monitoring took place from midnight 16 October 2013 until midnight 11 February 2014, covering most of the autumn and winter months, when energy demand would be highest. In addition to recording temperature in the case study properties, external temperature was measured with a Hobo Pendant Temperature Data Logger. All temperature data was collected from a single urban area of the East Midlands, so the external temperature data is relevant to all the case study properties. The data from the Hobo Pendants was downloaded at the end of the monitoring period using Hoboware software.
Actual energy use over the winter monitoring period of four months was measured from gas and electric meter readings at the properties. Gas meter readings were taken in cubic feet or cubic metres, (depending on the meter configurations) which were then converted to kilowatt hours.
Electricity meter readings are in kilowatt hours. When meters are dual rate, each reading is in kilowatt hours. So combined together, the total units represent the amount of energy used from the electricity supply. Receiving electricity on a dual rate basis may or may not be cost-effective, depending on the time of day when most energy is used. The cost will depend on the particular supplier tariff, and this can change over time. So for the purpose of this study, the comparative figure of interest was the actual energy use, rather than its cost.
Total energy use in kilowatt hours from each case study was calculated by combining gas consumption (where appropriate) and electricity consumption over the measured period.
Predictive energy modelling is a tool for estimating energy use in particular buildings, and was used in the UK residential sector to calculate whether a property was suitable for support under the Green Deal scheme.
The modelling method we used is the Standard Assessment Procedure, SAP 2009 [
The qualitative research consisted of semi-structured interviews to explore attitudes to energy with the seven case study participants (
Participant | Gender | Age Range | Occupation | Property Type | Property Age | Tenure |
---|---|---|---|---|---|---|
Anne | Female | 18 to 29 | Energy related researcher | Semi-detached house | 1930 | Tenant |
Arabella | Female | 30 to 40 | Energy related researcher | Semi-detached house | 1935 | Tenant |
Juliette | Female | 30 to 40 | Teacher | Semi-detached house | 1931 | Owner |
Jane | Female | 30 to 40 | Energy related researcher | Terraced house | 1890 | Tenant |
Robert | Male | 18 to 29 | Energy related researcher | Terraced House | 2012 | Owner |
Gwen | Female | 18 to 29 | Energy related researcher | Flat | 2000 | Tenant |
Wendy | Female | 30 to 40 | Energy related researcher | Flat | 1880 | Tenant |
Participant | Gender | Age Range | Occupation | Number of buy to let properties |
---|---|---|---|---|
Ava | Female | 40 to 50 | Print estimator | 4 |
Mike | Male | 40 to 50 | Business owner | 3 |
Patrick | Male | 30 to 40 | IT manager | 3 |
Participant | Gender | Age Range | Occupation | Representing |
---|---|---|---|---|
Alice | Female | 40 to 50 | Government Minister | UK Coalition government |
Daryl | Male | 30 to 40 | Senior policy executive | Large energy company |
James | Male | 30 to 40 | Senior policy executive | Large energy company |
Pauline | Female | 30 to 40 | Climate and energy specialist | Large environmental group |
The results of our qualitative research were combined with the quantitative research results in order to triangulate the findings by comparing predicted energy use with actual energy use. Also participants’ interview responses were compared with their actual behaviour. Measured temperatures in each case study property gave some appreciation of the participants’ thermal comfort range and its influence on their actual energy use.
Interview questions were devised on the basis of a number of key questions arising from previous research (e.g. [
1) How do domestic residents think about their energy use?
2) How does the form of energy residential consumers use appeal to their ideological, health or materialistic/economic consumer needs?
3) What impact has culture on energy use and can this be changed with education policy or through commercial/political marketing?
4) How does more information on domestic energy consumption, such as smart meters which provide real-time information on energy use, automatically encourage greater energy efficiency or is it more complicated than this?
5) How important/possible is it for domestic consumers to measure their energy use in all energy related activity (so they can be aware of technology efficiency rebound effects)?
6) How responsible do domestic consumers feel for their efficient use of energy?
7) How could tax incentives (which replace up-front subsidy or future government cost) be devised on a sectoral basis to make a difference?
The analysis of qualitative data may be approached in numerous ways [
Coding is one of the most common methods used to analyse and uncover concepts from qualitative data. Codes can be attached to words, phrases and sentences or whole paragraphs. This research used inferential coding to assign meaning to the descriptive or inferential information revealed during the study [
Our source data was divided into the subcategories of UK case studies, UK focus group and other UK stakeholders and also into nodes, which contain data about specific ideas/themes of analysis. Nodes were also included for positive, negative and mixed views. Inferential answers could then easily be assigned a particular viewpoint by including it in the relevant node. Matrix coding queries were done to combine results from different nodes. For example, attitudes towards climate change might be inferred from participants’ attitudes towards other factors, such as finance, how responsible people feel for their energy efficiency, etc.
Summary of UK case study participant’s household temperature and energy data (predicted and extrapolated actual)
The following composite
The concept of standard occupancy is important in rating energy use in properties, because it renders Energy Performance Certificates (EPC) a useful tool by which consumers may compare one property with another. So although the Green Deal allows some consideration of occupancy, (properties are classified as light, medium or heavy in terms of energy use), the SAP assessment concentrates
Total Energy by Type | Predicted (SAP) kWh/m2/year | Actual kWh/m2/year | Predicted energy use difference from actual (%) | UK Case Study Participant |
---|---|---|---|---|
Gas & Electricity | 317 | 352 | −10% | Anne |
Gas & Electricity | 288 | 220 | +31% | Arabella |
Gas & Electricity | 167 | 107 | +56% | Gwen |
Gas & Electricity | 262 | 205 | +28% | Jane |
Gas & Electricity | 199 | 220 | −10% | Juliette |
Gas & Electricity | 177 | 139 | +27% | Robert |
Electricity | 222 | 98 | +26% | Wendy |
on the fabric of the building and the means of energy delivery.
Therefore the SAP predicative analysis of energy use is likely to over-estimate energy use in a four-bedroom property which has only one occupant rather than a family of four. Conversely, it is likely to under-estimate the energy use of a small flat occupied by a large family using considerable amounts of heat and hot water.
Thus the standard predictive analysis can have a wide variation when compared with actual energy use in a property. Nevertheless, recommended energy efficiency measures do make sense if they have an impact on cost and individual thermal comfort.
However, even allowing for this latitude in the SAP projection as compared with actual energy use, in many of our UK case studies the discrepancy is very large. For example Robert actually uses less than half the electricity predicted, even though SAP ignores any energy requirements for cooking or the use of other electrical items, such as computers and televisions, etc. The energy prediction would have been even higher if SAP took these other items into account.
Gwen lives alone in a two-bedroom flat, yet her actual space heating energy use is almost 40% less than predicted, even though whatever heat she used would permeate most areas of her flat.
Jane lives alone in a two-bedroom mid-terraced house, and uses around half the electricity predicted by SAP.
Juliette lives alone in a three-bedroom semi-detached house. Her energy use is actually slightly more than that predicted by SAP.
Wendy lives alone in a one-bedroom mid floor flat. All her energy needs are supplied by electricity. She uses around 44% of the energy predicted.
Anne shares a three-bedroom semi-detached house with two other people. Her space heating usage is slightly more than predicted, and her electricity use is considerably more, no doubt reflecting on energy use by electrical items such as computers amongst members of the household.
Arabella shares a two-bedroom semi-detached house with one other person. Her space heating use (gas) is only about 70% of that predicted, yet electricity use is marginally higher. However, she has a bedroom electric heater, which she uses to ensure thermal comfort.
Our research therefore highlights the limitations of SAP in terms of predicting energy use and consequential potential savings under the Green Deal.
Overall, Robert and Juliette (both homeowners) live in properties with the highest average temperatures and Jane’s property records the lowest temperatures. Yet, because Robert lives in a newly built house, his energy bills are much lower than Jane’s. Wendy’s energy use is very low, but this is at least in part because she is absent from her flat on a number of occasions during the monitoring period. Gwen’s relatively modern flat also means that energy bills are low-around half that of Jane’s-even though the data indicates that she lives in relative thermal comfort. Arabella’s bedroom temperature is consistently higher than the temperature in her lounge, indicating that she uses her electric bedroom heater frequently.
At this point we turn to Tables 7-9 which collates responses to the qualitative questions reflecting the key issues of energy awareness that were discussed above.
A summary of Other UK Stakeholders responses (landlords, environmental group, energy Company, politician) is shown in
The UK case studies were chosen in order to try to gain deeper understanding of what factors would be important in motivating the participants to use energy more efficiently and/or more sustainably. The responses were related to key
Inferred Statement | Mixed View | Negative view | Positive View | Balance of view |
---|---|---|---|---|
Collective action is important | 4 | 0 | 2 | Uncertain |
Useful if we could choose the energy we get supplied to our home | 1 | 0 | 3 | Positive |
Education is the most important thing | 2 | 2 | 3 | Uncertain |
People are influenced by the culture around them | 1 | 3 | 3 | Uncertain |
What is your attitude to nuclear power | 3 | 1 | 3 | Uncertain |
Differential tariffs are a good idea | 2 | 1 | 4 | Uncertain |
Smart meters are useful | 4 | 0 | 3 | Uncertain |
People don’t think that rationally | 0 | 0 | 7 | Positive |
The government should nudge us in the right direction | 1 | 0 | 4 | Positive |
Government regulation is important in residential energy use | 0 | 1 | 4 | Positive |
What is your view on population and energy (bad effects) | 2 | 4 | 1 | Negative |
Financial situation is the driver behind energy use | 1 | 1 | 3 | Positive |
What is your attitude to the Green Deal | 3 | 3 | 1 | Uncertain |
How would you feel about being given a personal carbon allowance | 3 | 1 | 3 | Uncertain |
Would you be prepared to pay a carbon tax | 3 | 2 | 2 | Uncertain |
*Positive views agreed with the inferred statement, Negative views disagreed with the inferred statement, Uncertain views were mixed. This applies to all other groups in the study.
strands in the literature covering occupant behaviour and energy use, and participants views were considered in relation to these strands.
The Green Deal was the UK government’s flagship policy to improve energy efficiency in existing residential buildings.
Inferred Statement | Mixed View | Negative view | Positive View | Balance of view |
---|---|---|---|---|
Collective action is important | 1 | 0 | 6 | Positive |
Useful if we could choose the energy we get supplied to our home | 0 | 0 | 3 | Positive |
Education is the most important thing | 5 | 0 | 2 | Uncertain |
People are influenced by the culture around them | 2 | 1 | 4 | Uncertain |
Attitude to nuclear power | 3 | 1 | 2 | Uncertain |
Differential tariffs are a good idea | 1 | 1 | 3 | Positive |
Smart meters are useful | 1 | 0 | 6 | Positive |
The rebound effect is important | 4 | 0 | 0 | Uncertain |
People don’t think that rationally | 0 | 0 | 6 | Positive |
The government should nudge us in the right direction | 1 | 0 | 6 | Positive |
Inferred Statement | Mixed View | Negative view | Positive View | Balance of view |
---|---|---|---|---|
Attitude to the Green Deal | 8 | 0 | 1 | Uncertain |
Financial situation is the driver behind energy use | 6 | 0 | 7 | Uncertain |
Government regulation is important in residential energy use | 0 | 0 | 5 | Positive |
The government should nudge us in the right direction | 0 | 0 | 11 | Positive |
paying a carbon tax | 6 | 0 | 0 | Uncertain |
The rebound effect is important with regard to policy. | 2 | 0 | 5 | Positive |
“The Green Deal will deliver energy saving packages to millions of home across the country” [
However as
The number of households in Britain is approximately 26 million, and of these around 8 million have solid walls. Of the remaining 18 million, nearly 14 million have cavity wall insulation. The total number of properties with satisfactory loft insulation is just over 16 million. Details of cavity wall and loft insulation are shown in
However of the approximately 8 million solid wall household properties, very few have been insulated with internal/external wall insulation since 2008. Ironically, as the right hand side of
The behavioural economics insights associated with Kahneman and Thaler, suggest at least three behavioural characteristics that distort the mainstream expected utility theory approach:
・ reference dependence, i.e. households will focus only on changes to wealth, rather than allowing for the absolute level of wealth following the decision;
・ loss aversion, households will be more sensitive to (even small) losses than to gains of the same absolute value;
・ use of decision weights that are non-linearly dependent on but not equal to objective probabilities, resulting in the overweighting of low tail probabilities (large losses or gains with low objective probability) and underweighting of high tail probabilities (small losses and gains with high probabilities).
These three factors are amongst those which contribute to the empirical observation that many household investment decisions which would be adopted in an EUT model are rejected in practice.
The Green Deal appears to have been designed to address a capital market problem instead of an energy efficiency or emissions reduction target. House owners have always been free to fund energy efficiency improvements through bank loans secured on the property, but the Green Deal offered an alternative, arguably unnecessary, source of finance through a loan from the house owner’s energy supplier secured on the continued existence of an electricity or gas supply contract.
There was a fundamental contradiction in the Green Deal. While the avowed purpose of the policy was to improve energy efficiency in order to drive down greenhouse gas emissions which impose a positive social cost of carbon on the economy, this social cost was not used to evaluate the energy savings. If the cost of externalities was included as advocated by Tol [
Finally, there was much confusion in the choice of discount rates implied in the calculations. The capital market nominal rate of interest for new property loans during this period (when inflation was negligible) was in the region of 3 - 4 percent per year (this is the rate that EUT would expect consumers to use), while the government’s real social discount rate for climate change policy was in the region of 1 percent per year (as advocated for example by the Stern Review). Nevertheless the rate of interest offered on Green Deal loans was almost 7 percent per year fixed into the future, for the estimated lifespan of the energy improvement measure. Thaler [
Additional reasons that the Green Deal was not effective include:
・ The savings calculated to obtain Green Deal finance were not determined on a net present value basis. Nominal savings over the life of the energy efficient measure were estimated, and only savings made in the first year after installation were guaranteed.
・ The structure of the Green Deal was convoluted, with assessors originally intended to be independent from installers and providers (as is confirmed by Juliette’s experience, this is not always the case). This meant transaction costs were increased for all the actors involved with energy saving installations.
・ Very few energy improvement measures were likely to be cost-effective [
Case Study participants (although not other UK stakeholders) viewed the rebound effect as another reason the Green Deal was an ineffective policy. Saunders [
This research has confirmed that residential energy use is in part determined by human irrationality and policies based on Nudge theory. Research participants generally concurred that their thinking was not always highly rational. Government in particular was viewed by most participants as having the capability to influence behaviour around energy use in the residential sector. Government policy has the potential to alter heuristic behaviour to achieve more favourable outcomes using marketing and advertising measures to influence opinion. Importantly, regulation has the capacity to influence energy use, and in fact does so for example through increasingly rigorous building regulations. The success of regulatory standards in driving behaviour offers scope for future policy. For example, minimum energy efficiency standards prior to the sale of a property could be mandated. Of course the challenge of energy policy is that government cares about or at least is legally obliged to meet energy targets, while individual consumers have no such care or obligation, thus potentially making policy implementation politically difficult.
The research found definite support for financial incentives as a successful mechanism to influence behaviour. However incentives must be aligned with individual consumer needs in order to be effective. This means that policies designed to influence energy demand behaviour in the residential sector need to be nuanced, perhaps targeting different groups of people in specific ways. Variables such as income levels, cultural mores (incorporating educational, ideological ideas, and views on social identity), heuristic bias, and the potential for people to make choices need to be taken into account. Developing policy that can successfully deal with such a wide variety of influences is clearly difficult. This research shows that the Green Deal, the government’s primary residential energy policy, was never effective. Apart from its convoluted, costly structure, and because of the rebound effect, it did not effectively address the important issue of climate change. From a financial point of view, without subsidy, the rewards to the consumer were too meagre and uncertain to constitute a reasonable incentive. The non-financial incentives may have become more important over time, with slow cultural change.
A change in residential energy policy could involve a change in emphasis away from energy efficiency to energy sustainability. One possibility might be to tax fossil fuels (effectively a carbon tax), so that the price of energy from renewables and nuclear power became competitive [
Another possibility could be to levy an environmental tax on existing residential property that did not meet a certain standard of sustainability. This could be linked as a progressive surcharge on the local property tax, and thus property values. It could be made clear that the surcharge would increase by a fixed percentage each year, thus incentivising residential consumers to act immediately to improve the sustainability of their energy use.
A reversion to a system where large energy companies were mandated to improve energy efficiency/sustainability in the residential sector would be wise, as this study has shown that take-up of energy efficiency measures was unsatisfactory. This would be straightforward and could be more cost-effective than the Green Deal, as transactional costs would be lower. This could form part of a framework that encouraged householders to choose heat pumps over gas boilers, where for example, energy companies provided subsidies for research and marketing to promote this change.
This research was made possible by EPSRC support for the London-Loughbor- ough Centre for Doctoral Research in Energy Demand, grant number EP/ H009612/1.
Hallin, S., Hooper, E. and Weyman-Jones, T. (2017) Case Study Evidence and Behavioural Analysis of Residential Energy Consumption in the UK. Open Journal of Energy Efficiency, 6, 14- 40. https://doi.org/10.4236/ojee.2017.61002
The SAP procedure was applied to the case study properties in this research. Calculations were entered via computer software [
U-values, which indicate the insulation properties of materials or composite materials such as windows, doors, floors and walls, were included in the software worksheet. As there were no known actual values, reference was made to performance data tables in the SAP manual.
SAP estimates a thermal mass parameter based on the noted construction elements, such as walls, floors, doors, etc. and the total floor area. The heat loss associated with thermal bridges is the linear thermal transmittance. If this data is unknown (which was the case for the properties under study) the transmission heat transfer coefficient is calculated by reference to Appendix K in the SAP manual.
The number of occupants (which is assumed in SAP, depending on the floor area) is used to calculate water heating energy use. SAP takes account of heat loss from water storage, but this is not applicable to properties which have a combi boiler.
Boiler efficiency and standing heat loss is also included in the SAP calculation, with figures provided from the Product Characteristics Database or the manufacturer’s specification.
Internal gains from occupancy (typically 60 watts × number of occupants) and lighting (from SAP Appendix L) are included in the calculation of heating requirements. However electricity for other electrical items and energy required for cooking are ignored in the SAP calculation.
Solar gains are calculated by inputting the latitude of the property and window orientations.
SAP assumes a heating period average temperature of 21˚C for the living room area of the house with an average of 18˚C for the other areas.
To work out the energy use SAP adds up energy use from space heating, water heating, ventilation and lighting minus any energy savings from renewable energy saving technologies, such as solar PV panels. It converts the calculated total energy use which is in kWh into a power consumption figure of kWh/annum. The total energy cost for the dwelling is then worked out using standardised fuel prices (which are averages by region of prices over the previous three years).
The final SAP rating and the Environmental Impact (EI) rating is derived from a scale between 1 and 100. Higher values on the scale are associated with lower energy costs for the SAP rating or lower CO2 emissions per annum for the EI rating.
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