From 2000 – 2003 the Dutch energy rebate scheme “EnergiePremieRegeling” offered cash rebates for the purchase of higher energy-efficient appliances and other products. The rebate scheme was implemented in co-operation with energy companies and reached significant savings of at least 300 GWh/year. The programme was based on dynamic requirements and achieved a permanent transformation of the market by promoting A-labelled products
The Dutch programme “EnergiePremieRegeling” (EPR) was implemented in the Netherlands between 2000-2003, aiming, inter alia, at the promotion of energy-efficient appliances by creating favourable conditions for users and investors to buy the most efficient appliances. The programme, which was implemented in co-operation with energy companies, offered cash rebates for the purchase of higher energy-efficient household appliances, like washing machines, TVs, or refrigerators (e.g. in 2002, customers received €50 for each refrigerator with energy label A and 100€ for super efficient A+ and A++ appliances; the programme was based on dynamic requirements i.e. one year later in 2003, only the super-efficient appliances were eligible for rebates), and other promotional activities such as: wall insulation.
The programme aimed at achieving a permanent transformation of the market and at inducing investors to buy energy-efficient products. Grants for the purchase of the energy efficient appliance were offered, lowering the cost of the product to the consumer and making consumers aware that it was cost-effective for them to select energy-efficient appliances when they bought one.
These financial incentives were funded by an energy tax (Regulating Energy Tax; Regulerende Energie Belasting REB), of which 15 % was channelled back to the consumer through EPR rebates paid out by the energy companies. This so called “ecotax” on electricity and gas was in principle paid by the consumer to the state, but the energy companies collected it. The energy companies subtracted the energy rebate payments under the EPR scheme plus an addition of 10 to 20 % for their efforts in communicating and administering the programme from their ecotax debt to the state budget.
This programme achieved, as an example, that 94.4% of the market of washing machines were class A and higher i.e. the highest penetration in Europe at that time. The same was true for the super-efficient refrigerators and freezers, even a year after the programme ended in 2003.
Savings of at least 300 GWh/year and 0.3 million tons of CO2 were realized with the EPR programme (including the measures for insulation of buildings). The programme gave net economic benefits to the consumers who participated, but had slightly negative economic results for society. This overall result, however, includes costly measures such as solar energy and may also be due to free-rider effects: these were intentionally high, since the government wanted to ensure giving back a share of the increased energy tax to consumers.
The United States launched a similar programme called "Cash for Appliances". It was managed on a state level and funded by a federal stimulus package that provided every state with equal funding. However, demand varied from state to state leading to inadequate allocation of funds. In contrast to that, the Dutch policy paid for itself because of increased taxes (GreenBiz.com).
Similarly, in Italy the “Fiscal incentives for energy savings in the household sector” programme gave a tax incentive of up to €200 for purchases of A+ refrigerators or freezers (MURE 2011, p.2). Hungary provided a maximum incentive of 60,000 HUF (€190) for new A-labelled appliances and a maximum of 70,000 HUF (€222) for new refrigerators with either an A+ or A++ label (MURE NA, 1). For 2012, the government of Bulgaria plans to provide funds in the form of credits to Bulgarians if they purchase energy efficient appliances (MURE 2011 a, p.1).
Energy efficiency policy is part of an environmental policy with a tradition of 25 years in the Netherlands. In 1990 voluntary agreements were established between the distribution companies and the government. Another focus were eco taxes to take into consideration economical and ecological interests.
The distribution companies had to draft plans that were compiled to form the Environmental Action Plan (MAP) for the energy distribution sector. The distribution companies were allowed to recover the costs of energy efficiency activities through a charge on the electricity price. The upper limit for this charge was 2.1% of the revenues. Between 1991 and 1997, and following an expenditure of €600 million, 42.9 TWh of energy and 14.3 million tons of CO2 were saved. The MAP scheme ended in 2000.
Furthermore, a tax on the CO2 emissions from energy use for households and small and medium sized enterprises (SME) was created in 1997 for an average household (ap. 330 kWh/year this tax amounts to €230/year). In association with this tax, a new mechanism was created to reduce CO2 emissions. 15% of the tax was used for energy efficiency improvements.
The next table illustrates the market share of A-labelled appliances in the Netherlands in 1999 in comparison to the European Union. Before the implementation of the EPR, the Dutch market share of efficient appliances was already higher than EU average due to the MAP scheme. In 1999, 26% of the refrigerator market was A labelled (in comparison: market share in the EU: 12%).
The EPR was introduced in 2000, against these political and economic backgrounds.
1999 | 2000 | 2001 | ||
Refrigerators | Netherlands European Union | 26% 12% | 55% 19% | 67% 27% |
Freezers | Netherlands European Union | 29% 12% | 55% 16% | 69% |
Washing machines | Netherlands European Union | 40% 15% | 71% 26% | 88% 45% |
Dishwashers | Netherlands European Union | 27% | 55% | 73% |
Source: Belastingdienst 2002, adapted from GfK data
The programme aimed at achieving a permanent market transformation of the market and to create favourable conditions for investors to buy an energy-efficient product. Through financial measures, grants for the purchase of the energy efficient appliance can be given, lowering the cost of the product to the consumer and making consumers aware that it is cost-effective for them to select energy-efficient appliances when they buy one.
It is a national policy implemented in co-operation with energy companies
Both buildings and appliances were covered by the EPR, with a focus on appliances.
The list of the technologies addressed includes for example: refrigerators and freezers, dishwashers, washing and drying machines (e.g. in 2002: €50 for each appliance with an energy label class A, €100 for super efficient appliances: Energy+ fridges and freezers and AAA class washing machines, €160 to 205 for tumbler dryers); LCD monitors and TV; floor ground or wall insulation (from €2.5 to 12 per square metre); heat reflecting glass (from €20 to 30per square metre); high efficiency condensing boilers; low temperature heating systems; lighting systems control
Firstly, the EPR was supported by a wide scale information campaign including national campaigns on television and in national newspapers, advertisements in shops, promotions targeting installers, and websites such as www.energielabel.nl. The programme covered buildings too (in addition to the appliance specific measures). The EPR implemented inter alia grants for investment and an energy audit for buildings (especially on heating issues). These measures were also financed by the EPR.
Furthermore, the programme was in accordance with the EU Energy labelling scheme and the Energy+ campaign. If a customer decided to buy an efficient appliance, the energy label provided information, as to whether funding was possible or not. The same mechanism was offered by the Energy+ campaign for refrigerators and freezers. The Energy+ labelled appliance offered information about the financial options. Energy+ was an initiative by the European Commission, national energy agencies, and scientific institutes in Europe to promote the development and use of highly energy-efficient appliances (www.energy-plus.org). To participate in the Energy+ scheme e.g. refrigerators and freezers had to be at least 25 percent more efficient than basic energy class A models.
This interaction of the EPR with the EU energy label and Energy+ was a planned interaction. The EU energy label classes were an easy means to define eligibility for the grants and hence for appliance buyers to recognize the energy-efficient models eligible for the rebate. The Energy+ requirements were seen as preparation of the new label classes A+ and A++ and the EPR was thus used to support an early market offer and demand of A+ and A++ models through linking its grants to Energy+ requirements.
The well-known EU energy labelling scheme was an important pre-condition for the implementation of the EPR.
Agencies or other actors responsible for implementation
The energy companies were in charge of implementing the programme: paying out the grants, doing the communication, collecting the documents etc.
An independent state body monitored the programme. This body checked accounts in detail, visited some actual customers who had signed a paper on having received grants etc.
Funding
The policy was based on a dedicated funding scheme. The tax was channelled back to consumers who bought energy-efficient appliances.
Funds came from the Regulating Energy Tax (REB – Regulerende Energie Belasting), which is paid by consumers to the state and collected by energy companies. This tax was channelled back to the consumer through the utility companies i.e. electricity distribution companies, which are close to the consumers. They were requested to handle every application by the consumer within six weeks and provide immediate feedback. The customers had the possibility to get a rebate paid out by the energy companies for specific energy efficiency measures. The companies were allowed to recover the administrative, advertisement and other related costs by deducting "overheads", planned to be typically 5 to 10% of the costs, but actually more like 20 %. The energy efficiency technologies and requirements targets were defined by NOVEM and discussed with the industry and other market parties, before being proposed to the government for approval. An independent authority reviewed the operations (accounting, visiting customers). The criteria for calculating the rebates were based on a monetization of the avoided greenhouse gas emissions at €45 /ton of CO2. In order to avoid too high administrative costs, the minimum rebate was €45.
An ex-post evaluation was carried out by an independent group, hired for the purpose.
The next figure illustrates the EPR process.
Co-operation of countries
The EPR benefitted from the EU Energy label: the label classification made it easy for consumers to identify the A-labelled appliances that were eligible for the rebate. The EPR later also created synergies with the European campaign Energy+ to categorise the products with an even higher energy efficiency than A.
Quantified target
The programme had no concrete quantified target but the government specified an overall target for energy savings.
Between 1998 and 2000, the Dutch government aimed at reducing energy consumption by 2%/year.
The EPR is also part of the activities under the Kyoto Protocol to reduce CO2 emissions, especially in the residential sector. The aim was to avoid annual emissions of 2.3 million tons of CO2 by 2010.
Actors responsible for design
Ministries in charge of environment, economic affairs, finance (Central Administration): decision makers
NOVEM (energy agency, organized as subordinated public entity): responsible for proposals for concrete measures
Actors responsible for implementation
Ministries in charge of environment, economic affairs, finance (Central Administration): supervision
Energy companies: inform end-users and investors, disburse the bonus
Monitoring
Energy companies received 5-10% of the sum for advertisement and administrative costs. In return, they had to document the implementation and the costs. An independent authority reviewed the operations (checks on accounts in detail, visiting some actual customers who had signed a paper on having received grants etc.)
Evaluation
Ex-post evaluations are available:
Kemna, René (2002): Evaluation of the Netherlands energy efficiency subsidy scheme EPR, Belastingdienst-Centrum voor process- en productonwikkeling.
Joosen, Suzanne, Harmeling, Mirjam, Blok, Kornelis (Ecofys): Evaluatie van het Klimaatbeleid in de Gebouwde Omgeving 1995-2002, 2004.
Economic benefits were calculated as well.
A positive effect on the overall economics of the country is the state unemployment payments avoided in the appliance retail sector, which suffered from overcapacity.
In 2003, the budget for the EPR was €76 million but the investors received €175 million for new appliances. The necessary budget was underestimated due to the great demand that no-one expected. That is why the programme ended in 2003 without a recast.
In November 2001, almost two years after the start of the EPR, one third of Dutch households had applied for the EPR rebates. Of this, around two thirds concerned domestic appliances. The introduction of the EPR has led to an enormous growth of the supply of A-labelled appliances.
The market share of A-labelled washing machines grew from 40 to 88% over the 1999-2001 period. For refrigerators this was from 26 to 67%. The proportion of A labelled appliances doubled. Prices decreased (up to 25%). The increase in appliances is most likely due to the EPR and has led to a situation where retailers very often advise their customers to buy an A-labelled appliance as the best on offer.
The table below illustrates the achieved market shares of A-rated appliances in comparison to the average for the EU.
According to estimates by Wuppertal Institute, energy savings for household appliances of 300 GWh/year plus 500 GWh/year in heating energy for buildings and 0.3 million tons of CO2 were realized with the EPR programme (including the market transformation effect and other side effects).
Joosen et al. calculated a CO2 reduction from 2000 until 2002 of about 0.2 million tons and primary energy savings of 3-4 PJ in 2002 (differences are caused by different side effect calculations e.g. free-rider and market transformation effects).
1999 | 2000 | 2001 | ||
Refrigerators | Netherlands European Union | 26% 12% | 55% 19% | 67% 27% |
Freezers | Netherlands European Union | 29% 12% | 55% 16% | 69% |
Washing machines | Netherlands European Union | 40% 15% | 71% 26% | 88% 45% |
Dishwashers | Netherlands European Union | 27% | 55% | 73% |
Source: Belastingdienst 2002, adapted from GfK data
In total, about 15% of the ecotax was used for the energy credit scheme. The amount of funds available to the citizens for 2000 and 2001 were €158 million of which 97% was actually spent. The additional implementation costs (including information and awareness campaigns) by the utility companies were 20% of this expenditure (ca. €41 million). 42% was used to increase the demand for energy-efficient domestic appliances.
The 1999-2000 sales of A-labelled refrigerators, freezers, washing machines and dishwashers increased by 116%, 95%, 95% and 117% respectively. In the second year (2000-2001) sales increases, of a then already larger number, were 22%, 35%, 28% and 32%. The increase in sales has also produced a decrease in the prices of white goods. This effect is illustrated in the table below.
Other important measurable side effects of the EPR were increases in VAT and taxes on profit, and avoided unemployment benefits. They were calculated for the case of washing machines:With an estimated unemployment payment of €15000 per year, these yields avoided unemployment payments of ca. €2.3 million. It should be noted that elsewhere in the EU, where the machines are manufactured, further jobs have been secured.
1999 Euro | 2000 Euro | 2001 Euro | ||
Refrigerators | Energy+ A label not A label | 372,67 504,75 426,23 | 367,75 477,54 447,42 | 371,86 480,90 500,45 |
Freezers | A label not A label | 396,37 332,50 | 391,22 322,57 | 385,65 340,42 |
Washing machines | A label not A label | 814,45 490,17 | 678,50 497,61 | 674,55 476,32 |
Dishwashers | A label not A label | 794,92 645,64 | 695,94 672,72 | 740,99 647,90 |
Between 2000 and 2002, the total budget was €416 million, Of this, €86 million were used for administration by energy companies.
Joosen et al. (2004) estimated a cost of conserved energy of between 4 and 8 Eurocent/kWh for the programme costs (rebates plus administration). Due to the rebates, the actions were on average cost-effective for the consumers who took action. However, by including the investment instead of the rebates, the EPR was not totally cost-effective for society according to these results. This average, however, also includes costly solar thermal and photovoltaic installations. Furthermore, it is partly due to the fact that a high number of beneficiaries and also free-riders were intended by policymakers in order to return some of the energy tax back to consumers. However, the evaluation study (Joosen et al., 2004) may have assumed too high free-rider shares by taking the market share levels that were achieved by 2001/2002 as an effect of the programme, or at least partly, as the baseline (and hence as free riders) (Thomas 2007).
In November 2001, almost two years after the start of the EPR, one third of Dutch households had applied for the EPR rebates. Of this, around two thirds concerned domestic appliances. The introduction of the EPR has led to an enormous growth of the supply of A-labelled appliances.
The market share of A-labelled washing machines grew from 40 to 88% over the 1999-2001 period. For refrigerators this was from 26 to 67%. The proportion of A labelled appliances doubled. Prices decreased (up to 25%). The increase in appliances is most likely due to the EPR and has led to a situation where retailers very often advise their customers to buy an A-labelled appliance as the best on offer.
The table below illustrates the achieved market shares of A-rated appliances in comparison to the average for the EU.
According to estimates by Wuppertal Institute, energy savings for household appliances of 300 GWh/year plus 500 GWh/year in heating energy for buildings and 0.3 million tons of CO2 were realized with the EPR programme (including the market transformation effect and other side effects).
Joosen et al. calculated a CO2 reduction from 2000 until 2002 of about 0.2 million tons and primary energy savings of 3-4 PJ in 2002 (differences are caused by different side effect calculations e.g. free-rider and market transformation effects).
1999 | 2000 | 2001 | ||
Refrigerators | Netherlands European Union | 26% 12% | 55% 19% | 67% 27% |
Freezers | Netherlands European Union | 29% 12% | 55% 16% | 69% |
Washing machines | Netherlands European Union | 40% 15% | 71% 26% | 88% 45% |
Dishwashers | Netherlands European Union | 27% | 55% | 73% |
Source: Belastingdienst 2002, adapted from GfK data
makes energy efficiency in buildings and appliances transparent. For investors, policy-makers and actors involved in implementation and consultancy. Learn more ...
© 2023 | Built by the Wuppertal Institute for Climate, Environment and Energy | All rights reserved. | Imprint | Privacy Policy