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International Labour Organization European Union International Institute for Labour Studies Green policies in the EU: A review EC-IILS JOINT DISCUSSION PAPER SERIES No. 14

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Page 1: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

InternationalLabourOrganization

European Union

InternationalInstitute forLabour Studies

Green policies inthe EU: A review

EC-IILS JOINT DISCUSSION PAPER SERIES No. 14

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GREEN POLICIES IN THE EU: A REVIEW

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GREEN POLICIES IN THE EU: A REVIEW

INTERNATIONAL LABOUR ORGANIZATION INTERNATIONAL INSTITUTE FOR LABOUR STUDIES

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Abstract

This paper is part of a series of discussion papers that have been prepared by the International Institute for Labour Studies (IILS) within the framework of the joint project “Addressing European labour market and social challenges for a sustainable globalization”, which has been carried out by the European Commission (EC) and the International Labour Organization (ILO). The discussion paper series provides background information and in-depth analysis for two concluding synthesis reports that summarize the main findings of the project. This paper relates to the second part of the project “Preparing European labour markets to adapt to the long-run challenge of ensuring the joint social and environmental sustainability of globalization” and the concluding synthesis report “Towards a Greener Economy: The Social Dimensions”. The main purpose of this discussion paper is to examine the variety of green policies that EU Member States have implemented to address environmental sustainability. The paper starts with presenting available green policy instruments, such as regulations, tax instruments, the EU emission trading system, research and development (R&D) and public investment. It further discusses how these instruments are adopted in different EU Member States. Furthermore, existing green labour market policies in the EU are examined and the policy gaps are discussed.

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TABLE OF CONTENTS

Main Findings ................................................................................................................................................ 1

A. Green Policy Instruments for the Environment ........................................................................... 2

B. Regulations .......................................................................................................................................... 4

C. Tax Instruments ............................................................................................................................. 5

1. Energy and Mineral Oil Taxes ......................................................................................................... 6

2. Transport Taxes.................................................................................................................................. 8

3. Taxes on Emissions and Air Pollution ......................................................................................... 10

4. Tax Deductions and Other Special Provisions ........................................................................... 11

Trends in Taxation .................................................................................................................................... 14

5. Subsidies ............................................................................................................................................ 17

D. The European Union Emission Trading System (EU ETS) ................................................ 17

1. The first trading period of the National Allocation Plans (2005-2007) .................................. 18

2. The second trading period of the National Allocation Plans (2008-2012) ............................. 18

3. The third trading period without National Allocation Plans (from 2013 onwards) .............. 19

E. Research and Development ............................................................................................................ 21

F. Public Investment ............................................................................................................................ 24

G. Green Labour Market Policies .................................................................................................. 25

References .................................................................................................................................................. 28

Appendix 1 ................................................................................................................................................. 29

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List of figures Figure 1: Environmental tax revenues by EU Member States and type of tax, 2009, % of GDP ... 15 List of tables Table 1: Major policy instruments in the EU .............................................................................................. 4 Table 2: Fiscal policy instruments for sustainable transport ..................................................................... 9 Table 3: Common taxes in the EU ............................................................................................................. 11 Table 4: Energy efficiency measures ........................................................................................................... 12 Table 5: Environmental tax revenue in the EU Member States, 2008-2009 ........................................ 16 List of boxes Box 1: Energy efficiency policies in the EU ................................................................................................ 6 Box 2: Renewable energy feed-in tariffs ..................................................................................................... 13 Box 3: Business opportunities through green technology ....................................................................... 21 Box 4: Public–private partnerships ............................................................................................................. 23 Box 5: Education and Outreach .................................................................................................................. 25

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GREEN POLICIES IN THE EU: A REVIEW

Main Findings

• Environmental taxes and charges are the most widely used market-based instruments for green policies in the EU with governments imposing taxes on transport, emissions and air pollution, energy and mineral oil.

• Subsidies and tax credits have been granted to enhance energy efficiency in a variety of areas, including buildings, transport and households. Renewable feed-in tariffs (FITs) were also introduced in the renewable energy sector. These taxes and credits have raised supplies of clean energy and reduced emission of greenhouse gases (GHGs).

• The EU Emissions Trading System (EU ETS) is the first and largest international scheme that aims to combat climate change and cost-effectively reduce industrial GHG emissions.

• In order to promote environmentally friendly energy generation and decrease emissions, the governments of the EU Member States launched various climate change programs and funds. Renewable sectors are expanded by investing more in low-carbon energy production such as wind, solar, geothermal, hydro and nuclear power. Major EU Member Statesannounced Public-Private Research Partnerships (PPRP) to fund a wide range of renewable energy investments.

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• Governments of EU Member States are promoting energy efficiency and the use of renewable energy in the renovation and construction of buildings. Governments have also conducted surveys and feasibility studies while launching educational programs.

• The only evidence of green labour market policies is from countries that used tax revenue to finance reductions in distortionary labour taxes. Other quantitative or qualitative green labour market policies are not yet widespread in EUMember States.

A. Green Policy Instruments for the Environment

Green policies are all measures and instruments implemented by the government or other governmental institutions that have the purpose and the potential to reduce CO2 emissions. Reducing CO2 emissions cannot be limited to a few industries like the energy sector for example. A broad-based approach to encourage behavioural adjustments throughout the entire economy is needed since the consumption of fossil based energy resources can be decreased in many parts of the economy. The primary goal of policy instruments is to reduce the damage to the environment at minimum economic cost.

A variety of policies can encourage the structural change toward a low-carbon economy. INST-EC Discussion Paper No. 12 provides an in-depth discussion of the various tools available for EU policymakers. These tools include:

i. Regulations ii. Tax Instruments iii. Emission Trading Systems (Certificates and Licenses) iv. Research and Development v. Public Investment

While all of the instruments are relevant to the EU context, the first three options—regulations, tax instruments and trading systems—are identified in the literature as the main approaches to cope with global climate change (see Uzawa (2003) and Bertram (1992)). Indeed, the EU has relied heavily on tax instruments and trading schemes in addressing climate change, especially because these tools effectively assign a price to carbon — a favoured approach among economists. Some countries have engaged in more comprehensive tax approaches under Environmental Tax Reforms (ETR) in the 1990s. A detailed discussion of ETR in Europe can be found in the INST-EC Discussion Paper No. 13.

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In order to promote energy saving and reduce CO2 emissions, the governments of EU Member States have used various measures, such as taxes, subsidies, fees, laws and R&D investment programs. A detailed listing of green policies enacted in EU Member States is provided in the tables in Appendix 1. While many of these policies may not have originally aimed to address global climate change, they are still relevant in the context of this paper. Essentially, the observed policy instruments act to internalize the costs of environmental externalities through a variety of means that will be elaborated below. The majority of EU policies have focused, in some way, on the combustion of fossil fuels, which is the main source of CO2 emissions.

It is clear that certain countries in the EU have taken a more active role in implementing green policies. From the data in the green instrument tables in Appendix 11, the following countries stand out: Belgium, Czech Republic, France, Italy, the Netherlands, Spain, Sweden and the UK. These countries have each implemented over 30 green policies. Italy, the Netherlands and the UK were all around 50 policies, topping the list of countries included in this paper.

Section 2 discusses regulations on restriction of emissions by emphasizing emissions standards and recently introduced legislation on a CO2 labeling scheme for cars. Section 3 presents tax instruments, including an analysis of the various types of tax deductions, other special provisions and subsidies employed across the EU. Section 4 discusses the EU ETS. Section 5 details various R&D policies, including public-private partnerships. Section 6 discusses public investment, particularly in creating incentives for innovation and infrastructure development. Finally, Section 7 briefly discusses the limited amount of green labour market policies in the EU.

In Table 1, the major policy instruments adopted by the EU member states are illustrated. Taxes/duty, fees and subsidies are classified by types and purpose. Detailed analysis of each tools are followed in the further subsections of the paper.

1 Data in the tables is derived from the IEA’s Policies and Measures Databases and the OECD/EEA Database on instruments used for environmental policy and natural resources management).

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B. Regulations

Currently, the use of emission-restricting regulations is not widely prevalent across EU Member States, which have opted for more market-based approaches to the climate-change problem. Nevertheless, regulations have been used, in particular, to address emissions from vehicles and transport. For instance, emissions standards have existed since the 1970s and currently target four groups of emissions: nitrogen oxides, hydrocarbons, carbon monoxide and particulate matter.2 While emissions standards are a common feature of environmental policies in many advanced economies, the EU has only recently begun to address the issue of CO2 emissions from vehicles. Recent legislation has set the timeline for the implementation of new standards in this area.

Legislation was adopted in 2009 and set emission performance standards for new passenger cars, aiming to cap average emissions from these vehicles at 120 gCO2/km. Furthermore, the standards seek to reduce the fleet average for all cars in the EU by 19 2 Recent emissions standards for vehicles include Euro 4 (2009), Euro 5(2010) and Euro 6 (2014). None of these standards has addressed CO2 emissions. These standards are set at the EU level and compliance is left to member countries.

TAX/DUTY

Transportation- Vehicle registration/

usage/purchase (e.g. France ) -Import duty (e.g. Romania)-Weight based (e.g. Germany)-Emissions based (e.g. Ireland

and Spain)-Sticker tax on use of new/old cars (e.g. Finland)

-Vehicle insurance (e.g. Austria and the United Kingdom)-Air transport (e.g Bulgaria)

CO2 emissions, air pollution (e.g. Estonia , Denmark and Poland)

Energy production, consumption (e.g. the Netherlands and the United Kingdom)

Mineral oil production, sales, consumption (e.g. Denmark, Greece and Luxembourg)

FEE/CHARGE

Road tax for use of highways, alpine roads, and on heavy goods vehicle (e.g. Czech Republic and Slovak Republic)

User fee on parking (e.g . Austria and Finland)

Fee on CO2 emissions (e.g. Denmark and Estonia)

Air pollution fee on small/ medium/major stationary sources (e.g. Poland and Slovenia)

Environmental sanction fee for violations of the environmental code (e.g. Sweden)

SUBSIDY

Energy efficiency, clean energy including biofuels, biomass (e.g. Lithuania and Spain)

Environmentally friendly equipment (e.g. Hungary and Italy)

Transportation-Clean vehicles (e.g. Cyprus and Sweden)-Purchase of eco-friendly vehicles such as bicycles ( e.g. Begium and Italy)

-Energy labelling scheme (e.g. Finland and the Netherlands)

-Scrapping payment(e.g. Austria and France)

Ecological buildings (e.g. Czech Republic, Germany, the United Kingdom)

Feed-in tariffs (e.g. Germany, Italy and Luxembourg)

Table 1: Major policy instruments in the EU

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per cent by 2012 with a limit-value curve that will allow heavier cars to emit more than lighter cars, while maintaining the fleet average. Standards will be gradually phased in to allow for a smoother adjustment, starting in 2012 with 65 per cent of each manufacturer’s newly registered cars in compliance with the standard, 75 per cent in 2013, 80 per cent in 2014 and 100 per cent after 2015. Manufacturers will be required to pay a premium if they fail to meet the standard requirements.

In December 2010, the EU also made progress on forming regulations for CO2 emissions from vans, as a consensus was finally reached on the regulation text. Regulations on vans seek to cut CO2 emissions by 14 per cent (to 175 gCO2/km) by 2017. The regulations are modeled after those for new passenger vehicles and will be phased in with a cut in emissions of 28 per cent intended by 2020 (to 147 gCO2/km). Again, a limit-value curve is employed to set emissions limits by mass of vehicles and aiming to create a fleet average of 175 gCO2/km. Premium payments will also be required of manufacturers that do not comply with emissions restrictions. Additional incentives to manufacturers are also included. For instance, super credits, which allow manufacturers to count extremely low-emitting vans (below 50g/km) as more than one vehicle, will be offered on a phased-out schedule. And, manufacturers will be able to pool together to meet emissions targets collaboratively.

Recently passed legislation introduced a CO2 labeling scheme for cars in an effort to better inform consumer choices. Labels will provide information on fuel efficiency and CO2 emissions at the point of sale. Finally, legislation has also required a reduction in the GHG intensity of fuels by 10 per cent by 2020, with phasing-in of requirements. Again, fuel suppliers also have the option to pool together to meet standards.

C. Tax Instruments

Environmental taxes and charges are the most widely applied market-based instruments EU governments have imposed taxes on transport, emissions and air pollution, energy and mineral oil. Subsidies and tax credits have been granted to enhance energy efficiency in a variety of areas, including buildings, transport and households. Renewable feed-in tariffs (FITs) were also introduced in the renewable energy sector. Implementation of FITs is discussed in detail in the section on tax deductions and other special provisions. These taxes and credits have raised supplies of clean energy.

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1. Energy and Mineral Oil Taxes

Taxing energy and mineral oil as a means to raise tax revenue has a long tradition in EU Member States. Several EU Member States had already introduced energy taxes on the consumption of natural gas, coal, electricity and other oils since the 1950s. In the 1990’s, several EU Member States started introducing fuel taxes that included both, energy and mineral oil taxes, for environmental purposes. Later on, countries also started imposing specialized taxes on the energy and the oil sector.

The fuel excise tax imposed by Bulgaria in 1991 and revised later in 2006 includes both mineral oil and energy. Fuel is differentiated in three ways: by type, including petrol, diesel, gas oil, kerosene, LPG, heavy fuel oil, natural gas coal and coke, by electricity and by its use, such as whether it is used for heating or a propellant or for industrial or commercial purposes.

Denmark introduced duties on energy based on their purpose of usage since early 1980s, while duties on coal, electricity, and natural gas were imposed in 1995. The rest of the EU Member Statesstarted implementing taxes on energy products from early 1990s; Poland in 1990 and Austria in 1996. The Netherlands introduced separate taxes on energy, including a coal tax in 1992, and an energy tax and mineral tax in 1996. Italy has excised duties on consumption of all sources of energy since 1993. And, Romania and Slovenia imposed a fuel excise tax in late 1990s. Slovenia also introduced energy efficiency tax in 2010.

Italy has imposed an additional tax on electricity in towns and provinces since 1988. The electricity tax for manufacturing and transportation mode was levied in Germany as a result of their green tax reform in April 1999. Spain has levied electricity tax on production, distribution and importation since 1998.

Box 1: Energy efficiency policies in the EU

The EU has adopted the “20-20-20” plan, which sets climate and energy targets of cutting GHGs by 20 per cent by 2020 compared with 1990 levels, achieving 20 per cent of primary energy from renewable resources and improving energy efficiency by 20 per cent by 2020. As part of the strategy, many governments in the EU have imposed taxes on usage of electricity, mineral oils, roads and vehicles, which vary based on weight, purpose and emissions (see table 3). European countries have also designed a wide range of taxes including a tax on plastic bags in Ireland, the nutrient surplus charge in the Netherlands and waste disposal and batteries taxes in Denmark (see EEA (2005)). The plan also includes conducting surveys and feasibility studies while launching educational programs to provide information concerning renewable energy, energy efficiency and pollution.

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Non-fossil fuel obligation and climate change taxes were imposed on consumption of natural gas, coal and electricity in the UK since 2001. A number of countries like Sweden revised their energy taxes including, the electricity tax and energy and CO2 tax on fuels in 2010 that were introduced in the early 1990s. Some of the EU Member States like Czech Republic and Slovak Republic levied electricity, natural gas and solid fuels taxes in late 2000s.

Since the 1950s, some EU Member States have imposed taxes on petrol. For example, Denmark imposed a duty on petrol in 1950 and on mineral oil products in 1977. The rest of the EU started implementing different taxes on oil and petrol from the early 1990s. The Netherlands levied a separate petrol tax and a mineral oil tax in 1990 and in 1996. Italy imposed a special regional tax on oil and petrol in 1990 and also excised duty on petrol from 1993. While the original purpose of mineral oil taxes was to raise revenues, they can today be regarded as climate change policies and indeed several EU Member Statesraised mineral oil taxes in the course of their environmental tax reforms. Germany, for instance, raised the taxation on mineral oils in 1999. In Spain, a tax on mineral oils was extended to include retail sales of unleaded petrol, diesel, kerosene and others.

Many countries made revisions to their mineral oil taxes in 2010. Sweden revised its CO2 tax on petrol and diesel, which was first introduced in 1991. Duties on hydrocarbon oils like petrol, diesel and biodiesel were also changed in the UK.

Several countries introduced new energy and mineral oil taxes in the course of environmental tax reforms (ETR’s), thereby attempting to apply a more comprehensive tax policy approach. New green taxes are adopted while restructuring existing taxes and charges. Targeting renewable energy and energy-efficiency has been a main policy goal of ETR’s of EU Member States. Some of the methods in the greening of taxation are as follows:

• Tax on fuels and electricity introduced by Finland in 1990 and parking fines

• Duty on coal was excised in Denmark in 1982, fee on petrol is charged in 1992, duty on natural gas in 1995 and passenger car petrol in 1997, CO2 tax on fuels in 1998

• The Netherlands levied a petrol tax in 1990 and on coal in 1992, and started a comprehensive CO2 reduction plan in 1998 supporting the environmental projects and research by different tax incentives and subsidies

• France imposed a tax on natural gas in 1986, the reconstruction of environmental taxes and charges since 1999 and tax rebate on environmentally friendly house equipment in 2001

• Germany’s introduction of electricity tax and an increase of tax on mineral oils in 1999

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• Italy levied additional tax on electricity consumption in 1988, special tax on oil in 1990, excised duty on petrol and energy products in 1993,charge on air pollution in 1997, tax for registration of vehicles in 1999

• Sweden introduced a number of subsidies in the environmental and energy research such as investment subsidy for renewable energy in 1991, support for climate investment in 2003. Additionally, excised energy, CO2 taxes on petrol and electricity.

• An increase of fuel duty and climate change levy in the UK.

To reduce fossil fuel consumption, the German government has undertaken a three stage eco-tax reform on gasoline and heating fuel since 1999. In the beginning, the tax was raised by DM 0.06 per litre on gasoline, DM 0.04 per litre on heating fuel, DM 0.032 per kWh on natural gas, and DM 0.02 per kWh on electricity. Between 2000 and 2003, the yearly tax was increased by DM 0.06 per litre on gasoline and DM 0.005 per kWh on electricity. But after 2003, the eco-tax still remained at its 2003 level. At the same time, exemptions were granted to alleviate the tax burden. The manufacturing industry, for example, paid 20 per cent of the tax on electricity, heating oil and gas. And, oil and gas for power generation were not taxed.

The recent energy tax reform in Denmark created a green tax system that promotes renewable energy and targets reduction of CO2 emissions and gross energy consumption. In March 2009, the Danish Parliament agreed to launch the energy tax reform by cutting taxes on work and raising taxes on energy, climate and transportation by about EUR 1.1 billion.

2. Transport Taxes

EU Member States have imposed different types of vehicle-related taxes based on weight, purpose and emissions. Finland was one of the first countries to introduce a vehicle-related tax, with a tax on passenger cars and vans in 1958 (updated in 2009), and also a tax on registered cars in 1967 (updated in 2004). Most of the European countries, like Austria, Hungary, Latvia and the Netherlands, started levying vehicle-related taxes starting in the early 1990s.

In countries like Spain, until late 2007, the passenger car registration tax was linked to the cylinder capacity of the vehicle but from 2008, the registration tax was imposed according to car CO2 emissions/fuel consumption.

Since the early 1990s, many countries, like Ireland, introduced CO2 emission based vehicle taxes. Recently, France introduced CO2 emissions reduction measures, including a tax on company cars and a bonus/tax for registration of motor vehicles with low/high emission in 2008). In 2010, France imposed an annual tax on motor vehicles with large CO2 emissions (more than 245 g/km). Denmark has collected fees from heavy goods vehicles since the late 1990s.

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Table 2: Fiscal policy instruments for sustainable transport

Fuel tax - Gasoline/diesel tax (e.g. Poland) - Carbon tax (e.g. Sweden)

Vehicle tax - Annual vehicle attribute taxes and fees (EU) - Tax and fee reductions or exemptions for new clean, fuel

efficient cars (e.g. Denmark, Germany, the Netherlands) - Scrapping subsidies (e.g. Italy) - Annual fees for CO2 and smog externalities (e.g. Denmark,

the UK) - Import duty (e.g. Romania, Bulgaria and Lithuania)

Fee/tax on air plane - Emission landing charges (e.g. Sweden) - Tax on air transport (e.g. Austria, Bulgaria)

Road fees/tax - Congestion pricing (e.g. the UK) - Highway/Electronic road, road toll (e.g. Austria, Germany,

Czech Republic) - Road tax (e.g. Bulgaria, Slovak Republic)

User fee - Parking fees (e.g. Austria, Finland) - In-lieu fees for parking (e.g. Germany)

New vehicle incentives - “feebate”: variable purchase tax with fuel consumption (e.g. Austria)

Vehicle insurance - Fines for lack of mandatory insurance (e.g. the UK, Denmark) - Insurance-specific auto tax (e.g. France, Austria) - Pay-as-you drive and pay-as-you pump insurance (e.g. the

UK) Fleet vehicle incentives - Incentives for clean, fuel-efficient company cars (e.g. the UK)

Source: UNEP, OECD, IEA

In recent years, Germany implemented a weight and emission-based tax and charged a fee on heavy goods vehicle road toll since 2005. In the Netherlands, subsidies for low-emission vehicles are linked to vehicle labelling. In Romania, fees are levied on foreign registered vehicles that exceed standard dimensions. Portugal has implemented a municipal tax, truck tax and also a circulation tax on vehicles that transport goods, passenger cars and motor cycles.

Other kinds of vehicle-related taxes have included a sticker tax on the use of new and old cars and a diesel tax both introduced in Finland in 2004. Import duties on vehicles were also imposed in Romania, Bulgaria and Lithuania in the early 1990s. Additionally, air transport is taxed in countries like Austria and Bulgaria.

As for road transport, Austria has collected taxes on the use of lorries and trailers on roads since 1981. Austria and the Czech Republic also introduced fees for the use of highways in the second half of the 1990s. Czech Republic has charged additional road taxes on passenger cars since 1993 and electronic road toll fees since 2007.

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3. Taxes on Emissions and Air Pollution

In a number of EU Member States, CO2 emissions-related instruments have included air pollution fees and air emissions charges. The first CO2 tax was imposed in Finland in 1990, followed by countries like Denmark, Finland, Germany, the Netherlands, Poland, Slovenia, Sweden and the UK. Since 2000, Estonia started charge a fee on CO2 emissions.

The Czech Republic was one of the first countries to charge air pollution fees. The pollution fees on major sources were introduced in 1967, and were extended to medium and small stationary sources in 1991. The Slovak Republic introduced similar pollution fees on small sources in 1967 and on medium and large stationary sources in 1992.

Poland and Lithuania have been charging several air pollution fees since 1990. Italy started charging tax on air pollution since 1997 and Latvia since 1995. Air pollution non-compliance fees have been charged in Bulgaria since 1993, but in Romania and Latvia from 2000 and 2001 respectively. The Netherlands started providing subsidies for CO2 reduction since 1998, cutting the transport CO2 emissions, carbon credits and subsidy projects on CO2 re-use through underground storage in 2002. In Hungary, an air load tax and air pollution tax were levied in 2001 and 2004.

Spain introduced various taxes on air pollution starting with the tax on emissions to air in 1996. After providing tax deduction for environmental instruments since 1997, Spain introduced separate emissions and pollutants taxes including, a tax on activities that cause environmental harm in 2001; separate taxes on air pollution and on environmental damages caused by CO2 and SO2 emissions were introduced in 2006.

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Table 3: Common taxes in the EU

Fuel Tax/Fuel Excise Tax

e. g. Bulgaria, the Netherlands, Romania, Slovenia, Cyprus, Lithuania, Estonia, Finland, Latvia

Energy Tax

e. g. the Netherlands, Italy, Sweden, the UK, Austria, Slovenia

Mineral oil tax

e. g. Denmark, the Netherlands, France, Germany, Italy, the UK, Spain, Austria, Greece, Ireland, Luxembourg, Slovak Republic

Electricity

e. g. Germany, Denmark, Spain, Italy, Sweden, Czech Republic, Slovak Republic, Luxembourg, Malta, the UK, Finland

Coal

e. g. Denmark, the Netherlands, Denmark, Slovak Republic, Czech Republic

Natural Gas

e. g. Denmark, France, Czech Republic, Italy, Slovak Republic

Heating

e.g. Luxembourg

Petrol

e. g. Denmark, the Netherlands, Italy, Sweden, the UK

Diesel

e. g. the UK, Sweden, Ireland, Finland

Source: OECD, IEA

4. Tax Deductions and Other Special Provisions

Special tax provisions are widely used in EU Member States, particularly to increase the energy efficiency in environmentally friendly house equipment, buildings, vehicles and heating systems. Among the tools utilized are subsidies, grants, tax credits, tax deductions and exemptions.

Some EU Member States, like the Netherlands, launched tax incentive instruments to promote environmental initiatives. The Dutch government set up the Green Funds Scheme in 1995 to provide environmental tax credits to investors and loans to environmental projects through "green banks". Spain revised its 1997 tax deduction for environmental investments, such as renewable energy, air and water quality in 2006.

Tax credits encourage the production and sale of renewables because they reduce production costs, relative to the costs of producing substitutes like petrol and diesel fuel. Thus, Italy introduced tax credits for biomass heating systems in 2001, subsidies for the support of eco-friendly activities in 2004 and subsidies for energy efficiency in 2007. Lithuania has used tax exemptions for bio-fuels since 2000. In the UK, the first and second rounds of Bio-Energy Infrastructure Scheme were launched in 2003 and 2008 to provide grants to stimulate the use of small-scale biomass supplier fuel for heating and electricity generation. In Poland, rationalization of heat consumption in the household sector was introduced in 1998. France’s 2009 Finance Law was targeted to support

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renewable energy and increase financing for energy efficiency investments. The law provides consumption tax reduction on a variety of bio-fuels, ranging from EUR 15 to EUR 21 in 2009, EUR 11 to EUR 18 in 2011, and EUR 8 to EUR 14 in 2012.

Allowances for environmentally friendly vehicles and grants for the promotion of alternative energy sources have been provided in Cyprus since 2000 and 2003. In 2005, France revised the 2001 tax rebate on environmentally friendly house equipments. Recently, Hungary granted subsidies under the light bulb change programme. In its support for public transportation, Italy provided a personal income tax allowance in 2008 and subsidy for purchase of eco-friendly vehicles such as bicycles in 2009.

Table 4: Energy efficiency measures

Clean Vehicles

e.g. France, Italy, Cyprus, Denmark, Sweden, Germany, the UK, Sweden, the Netherlands, Spain, Hungary

Equipments

e.g. France, Italy, Germany, Hungary, the Netherlands, Spain, Belgium, Denmark

Buildings

e.g. France, Denmark, Germany, Finland, the Netherlands, Spain, Belgium, Denmark, Ireland, Lithuania, Czech Republic, Hungary, Portugal

Feed-in tariffs

e.g. France, the UK, Germany, Bulgaria Italy, Spain, Hungary, Luxembourg

Renewables/ Clean energy subsidy

e.g. France, Slovenia, Spain

- Biofuels e.g. Lithuania, France, Italy, Spain

- Biomass e.g. Poland, Italy, the UK, Sweden, the Netherlands

Source: OECD, IEA

In recent years, governments of EU Member States, particularly France and Germany, have started promoting energy efficiency and the use of renewable energy in the renovation and construction of buildings by taking initiatives such as setting a new norm for the public and private buildings and providing zero-interest loans. For example, through the environmental policy called the Grenelle de l’Environnement, the French government aims to cut the energy consumption of existing buildings by at least 38 per cent by 2020. Additionally, in 2012 the government is planning to reduce the existing public buildings’ energy consumption by 40 per cent and GHG emissions by 50 per cent. The norm for new offices and public buildings will be 50 kWh/m/year starting in 2010. The government established agreements with the banking and construction sectors to provide zero-interest loans to owners to improve the energy efficiency of their buildings (see Barbier (2009)).

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Box 2: Renewable energy feed-in tariffs

FITs promote market development of renewable energy technologies, such as solar-wind or geothermal-generated electricity. FITs offer producers of renewable energy long-term purchase contracts on favourable prices, usually at least the cost of production. Investments in renewable energy provide then a stable and calculable return. Producers of energy can be companies but also house owners who install solar panels on their roofs and can sell excess energy at a guaranteed price. In the long run, advanced technology and economies of scale are expected to decrease production cost so that renewable energy sources become competitive with their fossil-fuel-based counterparts. FITs are one of the most effective policy instruments in terms of overcoming cost barriers.

Through effective implementation of FIT law, several European countries like Germany (solar energy) and Denmark (wind energy) have successfully developed a renewable energy industry. Benefits of FIT include reduction of CO2 emissions, secured domestic energy supply, promotion of technological innovation, fair market conditions for renewable technologies and creation of jobs. The first Feed-In Law in Germany in 1990 supported producers of electricity from small hydro stations and wind energy installations. Since that time, the adoption of the Energy Supply Industry Act in 1998 and the Erneuerbare-Energien-Gesetz (EEG) (further amended in 2004), or the 2000 Renewable Energy Sources Act, indicated a commitment to raising the share of renewable energy in total electricity supply in Germany to 12.5 per cent by 2010, and to at least 20 per cent by 2020.

Other EU countries like France, the UK, Italy, Spain and Bulgaria have introduced FITs for different types of renewable energy since the beginning of 2000. The French government offered a series of new FITs in the biogas and mechanisation, wind power, photovoltaic, hydro, solar and geothermal sectors since 2001. The FITs for most technologies in France were superseded by subsequent regulations and further new tariffs were introduced in the area of hydropower (2007), biomass (2009) and solar PV (2010).

In April 2010, the UK government provided FITs for small-scale low-carbon electricity produced from a wide range of renewable energy technologies including bio-energy, hydropower, solar photovoltaic and wind. Italy stimulated the production of electricity from solar thermodynamic plants, connected to the electricity grid and plants had to be equipped with thermal accumulation systems relative to the intensities of industries within the economy.

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Trends in Taxation

As discussed in the tax instruments section, most of the taxes are imposed on energy. Figure 1 shows environmental tax revenue independently for EU Member States, and as a percentage of total tax revenue, for 2008 and 2009. The data shows that on average, environmental taxes account for 7.1 per cent of total taxes, with revenue ranging from EUR 1 to 40 million and 4.4 to 11.9 per cent of total tax revenue. This indicates that wide variation of tax policies and revenues exist among EU Member States. For example, in Denmark and the Netherlands, green taxes account for over 10 per cent of total tax revenue, in comparison to Belgium and France, where environmental taxes are less than 5 per cent of total tax revenue. Moreover, Figure 1 also reveals little growth, if any, in environmental tax revenue. There is only a 0.34 average per cent growth in environmental tax revenue between 2008 and 2009, with most EU Member States actually experiencing a decline in revenue. Such a decline in revenue amongst the majority of Member States can ultimately denote, however, that environmental taxes serve a more significant purpose than a tax instrument; environmental taxes are changing the consumption habits of communities by creating a price differential between environmentally-friendly and environmentally hazardous products. Decreased tax revenues reveal that green taxes are acting as an efficient disincentive in reducing the consumption and use of environmentally dangerous goods and limited natural resources.3 Exclusions exist for Latvia, Lithuania and Slovenia, which all witnessed markedly high increases in environmental tax revenue. Several countries have already raised environmental taxes substantially. These taxes can become an essential part of governments' budgets but the trends are declining. As examined in the INST-EC Discussion Paper No. 13, on average, environmental tax revenue in the EU has amounted to 2.5 per cent to 3 per cent of GDP, with a declining trend. Environmental taxes account for between 7 and to 8.25 per cent of total tax revenue on average, also with a declining trend. Table 5 shows the environmental tax-to-GDP ratio by Member State and the composition of environmental tax revenue, through taxes on energy, transport-fuel and pollution. Energy taxes are taxations on both transport and stationary use of energy products, such as electricity, natural gas and coal.4 The high share of taxes from transport fuels is almost exclusively from minimum excise taxes on petroleum. Lower taxes often exist for transport and use of fuels for heating and businesses, with Member States motivated by social rather than environmental concerns.5 Last, pollution taxes are taxations on hydrocarbons and other pollutants as an instrument in the EU’s reduction of CO2 emissions.

3 “Taxation Trends in the European Union: Data for the EU Member States, Iceland and Norway.” Part II, Environment. Eurostat, European Commission. 2010. (154). 4 “Taxation Trends in the European Union.” (152). 5 “Taxation Trends in the European Union.” (154).

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As seen in the table, energy taxes are by far the most significant form of environmental taxes, representing around three quarters of environmental tax receipts. Following taxes on energy usage, transport taxes comprise on average, slightly less than one quarter of environmental tax revenue.6 Moreover, despite minor exceptions, the green tax revenue for most Member States falls within 2 to 3 per cent of GDP. Only 4 countries – Denmark, Malta, the Netherlands and Slovenia – have environmental tax revenues that exceed 3.5 per cent of GDP. In the case of Denmark, increases in transport and pollution taxes, remarkably higher than other EU Member States, account for the elevated tax-to- GDP ratio. Figure 1: Environmental tax revenues by EU Member States and type of tax, 2009, % of GDP

6 “Taxation Trends in the European Union.” (150).

0

0.5

1

1.5

2

2.5

3

3.5

4

4.5

5

BE BG CZ DK DE EE IE EL ES FR IT CY LV LT LU HU MT NL AT PL PT RO SI SK FI SE UK

Environmental Tax-Energy as % of GDP Environmental Tax-Transport as % of GDP

Environmental Tax-Pollution as % of GDPSource: Eurostat

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Table 5: Environmental tax revenue in the EU Member States, 2008-2009

2008 2009 Environmental

tax revenue (in EUR millions)

Environmental tax as % of total

tax revenue

Environmental tax revenue (in EUR

millions)

Environmental tax revenue as % of total tax

BE 6.790,6 4.4 6.874,1 4.66

BG 1.218,89 10.6 1.060,5 10.48

CZ 3.627,66 6.8 3.418,01 7.23

DK 13.329,06 11.9 10.662,62 9.97

DE 54.538 5.7 54.164 5.69

EE 379,25 7.3 413 8.31

IE 4.506,83 8.3 3.781,2 8.39

EL 4.561 6.0 4.611 6.52

ES 17.840 4.9 17.163 5.35

FR 40.061 4.9 39.927 5.04

IT 38.130,84 5.7 39.864,54 6.08

CY 542,3 8.0 490,1 8.23

LV 451,17 6.7 429,33 8.69

LT 533,95 5.5 543,22 6.98

LU 986,15 7.0 931,4 6.61

HU 2.853,33 6.7 2.436,09 6.64

MT 200,51 10.2 194,89 9.77

NL 23.140 9.9 22.764 10.42

AT 6.795,09 5.6 6.658,16 5.69

PL 9.486,9 7.5 7.944,34 8.05

PT 4.406,32 7.2 4.202,98 8.07

RO 2.486,23 6.3 2.213,99 6.99

SI 1.119,53 8.1 1.260,83 9.47

SK 1.317,32 6.8 1.225,48 6.76

FI 4.992 6.3 4.553 6.17

SE 8.934,3 5.8 8.212,71 6.02

UK 43.768,75 6.5 40.603,37 7.44

EU Average

24.189

7.1

79.455

7.397

Source: Eurostat

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5. Subsidies

Subsidies have been a popular tool in the EU. Countries like Slovak Republic have provided subsidies for environmental purpose since 1991. In Italy, the motor vehicle scrapping subsidy was introduced in 2007. In the Netherlands, subsidies were provided for the generation of electricity, which included biomass installation and offshore wind generation.

In particular, the use of low-emission vehicles is supported through subsidies. The Power Shift Programme, launched in the UK in 1996, offers grants to buyers of clean-fuelled vehicles, including vehicles running on natural gas, liquefied petroleum gas and electricity (see EEA (2005)). Also, grants are offered to British operators of commercial vehicles and public operators. The French government has promoted clean-fuel alternatives to other petroleum products in both private and public transport vehicles by subsidizing and reducing taxes on electric and natural gas powered vehicles since 1999. In this sense, a bonus was provided for the acquisition of clean vehicles in 2007.

D. The European Union Emission Trading System (EU ETS)

As defined by the European Commission (EC), the EU ETS is the first and largest international scheme that aims to combat climate change and reduce industrial GHG emissions cost-effectively. By allowing participating companies to trade emission allowances, the EU ETS assists EU Member States in fulfilling their commitments to reduce GHG emissions at least cost. From 2005 to 2009, the global carbon market grew to a total value of USD 144 billion, of which the EU ETS accounts for USD 123 billion (see Robins et al. (2009)).

The EU ETS was launched in 2005, with a first trading phase from 2005 to 2007 and a second phase from 2008 to 2012. It covers over 10,000 installations in the energy and industrial sectors that generate almost half of the EU's total CO2 emissions and 40 per cent of its total GHG emissions. On 1 January 2008, the EU-27 Member States under the ETS were joined by Norway, Iceland and Liechtenstein. According to a July 2008 amendment to the EU ETS Directive, the aviation sector will be added to the system starting in 2012.

The EU ETS allows participants to buy and sell allowances within the trading limit determined by the ETS. The holder of an allowance has the right to emit one tonne of CO2 or equivalent amount of another GHG. The ETS covers the CO2 emissions in the power sector, including all fossil fuel generators over 20 MW, iron and steel manufacturing, oil refining, cement, glass, ceramics and paper and pulp production. After 2005, member states were permitted to “opt in” smaller installations within these sectors,

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and under the second phase from 2008-2012, new sectors were added and include non-CO2 GHG emissions. From 2005 to 2007, member states could apply to "opt-out" specified installations, but after 2008 all eligible installations were required to be covered under ETS.

In the first and second trading periods under the scheme, Member States had to draw up National Allocation Plans (NAPs), which determine the total quantity of GHG emission allowances that the companies in EU Member States are granted. Each Member State had to decide the total quantity of allowances for the trading period and allocate the allowances among the installations covered by ETS. For the third trading period starting in 2013, the allocation will be set directly at the EU level, suspending the use of national allocation plans.

1. The first trading period of the National Allocation Plans (2005-2007)

Each Member State prepared and published their first NAPs by 31 March 2004 and 1 May 2004 (for 10 Member States that joined the EU in 2004). The allocations granted to installations were required to be within the framework of the Kyoto Protocol. The following plans were accepted by the Commission:

• In 2004, Austria, Denmark, Germany, Ireland, the Netherlands, Slovenia, Sweden, the UK, Belgium, Estonia, Finland, France, Latvia, Luxembourg, Portugal, and the Slovak Republic, Cyprus, Hungary, Lithuania, Malta and Spain

• In 2005, Poland, the Czech Republic, Italy and Greece

The NAPs for the first trading period successfully established the free trading of emission allowances within the EU by developing the core infrastructure of a dynamic carbon market. Due to the adoption of emission projections, however, excessive allocation of allowances occurred in some Member States and sectors.

2. The second trading period of the National Allocation Plans (2008-2012)

While NAPs of the first trading period were time-consuming and complex, and not sufficiently transparent, NAPs in the second period were much simpler. The second trading period is crucial because it coincides with the first commitment period of the Kyoto Protocol. The NAPs were prepared and published by 30 June 2006 and during this period, the EU Member States have to achieve their targets to limit or reduce GHG emissions. All second period NAPs are approved by the EC and while member States individually meet their Kyoto commitments, the second period EU cap is about 13 per cent lower than the first period cap and 6 per cent lower than comparable 2005 emissions

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(see Ellerman & Joshkow (2008)). The total cap, quota and allocation of emissions to energy and industrial facilities vary according to countries.

From 2008-2012, Italy committed to cut CO2 emissions by 13.65 million tonnes with a total cap of 201.63 million tonnes. The annual emissions quota for new industrial plants is, on average, 16.93 million tonnes. The share of emissions that can be offset by credits created in developing nations is 15 per cent of the total amount, except for fuel-fired power plants (up to 19.3 per cent).

In Denmark’s second NAP, a total of 125 million CO2 emission allowances were allocated. On 13 March 2003, a new climate change strategy was adopted that identified tools to achieve Denmark's Kyoto target of 21 per cent GHG emission reductions in the period 2008-2012.

In Greece's NAP, 69.1 million tonnes of CO2 emissions per year were allocated, with the expected result in a 16.6 per cent reduction in GHG emissions for 152 industrial enterprises. The whole emission rights are allocated free of charge and totals to 345.6 million tonnes of CO2. About 4.8 per cent of the total emissions rights, or 16.7 million tonnes of CO2, will be spent on new plants in 2008-2012.

Due to widening differences in national methods for allocating allowances to installations, it is difficult to ensure fair competition in the internal market. Therefore, the EC has supported improvements in the harmonization and refinement of these methods and also encouraged access to credits from emission-reduction projects outside the EU. Moreover, the conditions for linking the EU ETS to ETS elsewhere should be provided, and the monitoring, verification and reporting requirements need to be enhanced.7

3. The third trading period without National Allocation Plans (from 2013 onwards)

For the third trading period, allowances will be allocated through harmonized rules and there will be a single EU-wide cap. The main allocation method will be the auctioning of carbon allowances. The EC summarized the following major changes8:

• Derogation of the rule “no allowances are to be allocated free of charge to electricity generators” is allowed temporarily (or is optional) to some Member States as of 2013. The amount of free allowances to power plants is limited to 70 per cent of carbon dioxide emissions in phase 1 and declines in the following years. Moreover, free allocation in phase 3 is only provided to power plants.

7 Refer to the EC’s Climate Action site: http://ec.europa.eu/clima/policies/ets/index_en.htm 8 Summary of the main changes is stated on the above website of the EC’s Climate Action

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• Detailed explanations of criteria are used to determine the sectors or sub-sectors exposed to a significant risk of carbon leakage. Installations of all exposed industries for 100 per cent free allowances if international agreement is reached and the most efficient technology is used.

• Member States may compensate certain installations for CO2 costs passed on in electricity prices if the CO2 costs might otherwise expose them to the risk of carbon leakage.

• The level of auctioning of allowances for non-exposed industry will be raised in a linear manner: 70 per cent by 2020 and reaching 100 per cent by 2027.

• 10 per cent of the allowances for auctioning will be redistributed to Member States with low per capita income from those with high per capita income. Also, 2 per cent of auctioned allowances are added to support Member States, which in 2005 had achieved a reduction of at least 20 per cent in GHG emissions compared with the reference year set by the Kyoto Protocol.

• The share of auctioning revenues that is used in solving climate change issues within the EU as well as in developing countries is increased from 20 per cent to 50 per cent.

• New sectors and new entrants will be able to use credits but the total amount must not exceed 50 per cent of the reduction between 2008 and 2020.

• 300 million allowances from new entrants reserve will be used to support up to 12 carbon capture and storage demonstration projects and projects on innovative renewable energy technologies.

• The opting out of small combustion installations is extended to all small installations, the emission threshold is raised from 10,000 to 25,000 tonnes of CO2 per year, and the capacity threshold for combustion installations is raised from 25MW to 35MW.

In order to achieve the GHGs reduction target, the cap on carbon will be tightened by 1.7 per cent a year from 2013, and 60 per cent of allowances will be auctioned compared with current rate of 3 per cent.

By putting a price on carbon emissions, emissions from installations in the scheme are falling, which shows how the EU ETS could effectively trade the GHG emissions. Progressive changes including the auctioning of allowances will be introduced in 2013. The successful implementation of the EU ETS has encouraged other countries to adopt compatible cap and trade schemes.

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E. Research and Development

An effective strategy to reduce CO2 emissions and promote environmental sustainability must combine market-based instruments with direct public intervention such as regulations, public investment and increased promotion of R&D. The R&D activities of private enterprises, which are promoted by both tax and price incentives, alone are insufficient –governments have to support adequate R&D activities and make green investments in order to boost and accelerate the green transition.

Several European countries have contributed substantial amounts of funds to research programs on renewable and environmentally friendly energy generation since 1970s. In recent years, government expenditure on environmental R&D has risen rapidly, taking the form of investments, subsidies and tax credits. Denmark has implemented the Energy Development and Demonstration Program since 1976 and subsidized many new energy and electricity efficiency related research and development since the end of 1999.

Sweden has invested in energy research, renewable energy and climate change since 1991 and has subsidized activities on introducing renewable energy, as was done with wind power in 2004. Lithuania started implementing an energy efficiency and housing project and set up an Environmental Investment Fund in 1996. In the Netherlands, research on environment and technology has been supported by subsidizing the climate indifferent energy, reduction of GHG and management of waste since the late 1990s.

Box 3: Business opportunities through green technology

The world’s low-carbon energy and efficiency technologies market is forecasted to grow from USD 740 billion in 2009 to USD 1.5-2.7 trillion in 2020, most likely tripling to USD 2.2 trillion or at least doubling in the worst case scenario. During this period the fastest growing sector will be electric vehicles, expanding more than 20 times to reach USD 473 billion (see HSBC (2010)).

The HSBC expects that the EU will meet its renewable energy targets, but not its energy efficiency targets (see Robins et al. (2010)). It foresees limited growth in clean energy in the U.S. and expects current clean energy targets to be exceeded in China. At present, the EU has the largest share of the low-carbon market (33 per cent), which includes low-carbon energy production and energy efficiency, followed by the U.S. (21 per cent) and China (17 per cent). But as indicated in the HSBC conviction scenario, the share of the EU is expected to fall to 27 per cent because of an increasing market share of China (24 per cent) (see Robins et al. (2010)).

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Governments are providing grants and subsidies in the research and development of sustainable development, environmental education, renewable energy sources and protection of air and water though special funds and programs, such as the State Environmental Fund of the Czech Republic (SEFCR). The Austrian Climate and Energy Fund, established in 2007 with a budget of EUR 500 million, also promoted R&D on sustainable energy technologies and technology deployment and diffusion.

Denmark created the Energy Development and Demonstration Program in 1976 and has also actively subsidized the research and development in the environmentally friendly electricity generation and efficient use of electricity since the late 1990s. Additionally, subsidies were granted to the support of ecological buildings and to the development of new energy technologies in 2007.

France is supporting the clean energy development by providing subsidy for multiple renewable energy sources under programs such as Renewable Energy Market Development Program (1999). Additionally, government crediting and loan guarantees are provided for energy efficiency and renewable energy investment since 2001.

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Box 4: Public–private partnerships

Although public investment plays an important role in green R&D, private corporations and consumers are still encouraged to finance the climate economy. In recent years, major EU countries have announced Public-Private Research Partnerships (PPRP) to fund a wide range of climate change and renewable energy investments.

For example, the Renewable Energy and Energy Efficiency Partnership (REEEP) was established in 2002 and is funded by the governments of Australia, Austria, Canada, Germany, Ireland, Italy, the Netherlands, New Zealand, Norway, Spain, the UK, the U.S. and the EC. In addition to governments and governmental organizations, several non-governmental organizations like the North American Insulation Manufacturers Association (NAIMA) and business organizations like the National Australia Bank are involved as donors. This partnership targets clean energy by providing policy and regulatory initiatives and facilitating financing for energy projects.

France is one of the major countries that rely on partnerships to encourage private funding in climate change projects. The Renewable Energy and Energy Efficiency Partnership (REEEP) and National Strategy for Research and Development in the Field of Energy were established in 2002 and in 2007. Through the Hydropower Revival Plan of July 2008, the French government intends to increase the capacity and efficiency of hydropower and by 2020, raise the final energy consumption to 23 per cent. The plan involves large-scale public investment in hydropower dams as part of le Grenelle de l'Environnement and will ensure high water quality. The renewable process of the plan encourages the participation of private sector.

According to the International Energy Agency (IEA), on 25 April 2006, France established PPRP to support climate change policy and decrease the use of petroleum products.1 The Agency for Industrial Innovation is providing public funding for three major programs including a 88 million euro programme to improve energy efficiency in buildings, a 96 million euro project for a "green chemistry" initiative, and a 62 million euro initiative to create energy-efficient subway cars.

In February 2009, the French government launched the fourth PREDIT programme which first started in 1990. This program’s priority is energy and environment and the largest share of the 145 million euro budget is allocated to the reduction of CO2 emissions, improvement of data on pollution and coordination of research into very energy-efficient, low- or zero-carbon dioxide emitting vehicles.

In 2010, the UK government announced its plan to establish a private and public funded commercial Green Investment Bank (GIB) that would include a public investment of up to 1 billion pounds. The GIB’s main role is to facilitate the delivery of the UK’s emission reduction targets as set by the Climate Change Act 2008. By helping to overcome barriers that constrain investments, the GIB could lead to a substantial increase in investments in low-carbon technologies and infrastructure in the UK (see UK GIBC (2010)).

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F. Public Investment

Public investment is one of the tools that can help to facilitate the reduction in GHG emissions. Governments can either increase total public investment, or – perhaps more practically, given the strained public budgets in many countries – shift public investments from “brown” capital to “green” capital. In order to promote environmentally friendly energy generation and decrease emissions, the governments of the EU Member States have launched various climate change programs and funds. Most of the EU Member States have also expanded their renewable sectors by investing more in the low-carbon energy production such as wind, solar, geothermal, hydro and nuclear power. In Germany, for example, the operators of renewable energy plants have been able to sell green electricity on the market since 1996. German authorities accepted extra costs caused by green tariffs and also started purchasing green power.

According to IEA, around 80 per cent of the GHG emissions originate in energy production and consumption.9 Thus, governments have drawn measures to increase energy efficiency, reduce GHG emissions and achieve the indicative target. Some of these plans include Italy's Provisions on GHG Emissions Reduction (1998), Denmark's Climate Change Strategy (2003), the Netherlands’ Energy Efficiency Action Plan (2007), Austria’s New Energy 2020 program (2008), the UK’s Low Carbon Transition Plan (2009) and Finland's Long-term Climate and Energy Strategy (2008). The Austrian Climate and Energy Fund of 2007 also increased energy efficiency and reduced CO2 emissions in transport.

In order to reduce energy consumption in the transport sectors, governments took additional measures in the framework of national programmes and plans by increasing investment in public transportation and road construction, updating HGV-toll and reforming vehicle tax on a CO2 basis. These measures were undertaken by the German government through the Transport Initiative of 2001, Future Investment Programme (2008) and the National Energy Efficiency Action Plan (2007) and the Integrated Energy and Climate Change Programme (2007).

The UK is subsidizing the Green Technology Challenge and the England Rural Development Programme by investing in infrastructure and public transportation since 2002. The Carbon Trust provides an interest-free loans scheme for small or medium-sized enterprises for acquiring and installing energy efficient technologies.

A major challenge to greater public investment is budget constraints induced by the economic crisis. The need for fiscal prudence has severely reduced the capacity of governments to appropriate funds for “green” goals. Yet, public investments play a strong

9 See http://www.iea.org/textbase/pm/?mode=re&id=4247&action=detail.

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role in influencing the market and encouraging the private sector towards a green transition, and play a complementary role to larger market-based mechanisms. Besides public investments, private investments should be promoted through incentives or standards of three major instruments like regulations, taxes, and cap and trade.

G. Green Labour Market Policies

As defined in the INST-EC Discussion Paper No. 10, green labour market policies are those that intend to increase the level of employment or improve working conditions within an economy that is transitioning towards a green economy. Labour market policies play a significant role in addressing challenges specific to the green transition and provide opportunities to smooth the necessary structural changes. Implementation of the right policy mix can lead to positive net employment effects from the green transition. However, specific labour market policies that are targeted at facilitating the green transition from the labour market side are not widely observed throughout the EU.

In fact, the only evidence of green labour market policies is from countries that used tax revenue to finance reductions in distortionary labour taxes, largely in search of the double dividend. Refer to the INST-EC Discussion Paper No. 13 for a detailed discussion of tax

Box 5: Education and Outreach

Governments conducted surveys and feasibility studies while launching educational programs to provide information concerning renewable energy, energy efficiency and pollution. Environmental and ecological websites are launched to reduce household carbon emissions. The French government also set up an information network with five hundred people operating on energy efficiency "Points Info Energie" in 2000 and Ecological Consumption Website in 2008, to reduce individual CO2 emissions. Additionally, in France, surveys, Diagnostics and related studies were done under the “Disposition Général des Aides à la Décision” since 2000 in order to identify possible solutions to resource mismanagement..

The klima:aktiv programme in Austria (2004-2012) targets energy efficiency and increased the use of renewable energy in all sectors of the economy by providing direct grant, information and advice. In Germany, a joint project, "Partnership for climate protection, energy efficiency and innovation", is implemented to support company visits by members of the chambers which will provide energy consulting services. This project is initiated by the Federal Ministry of Economics and Technology (BMWi) and the Federal Ministry for the Environment, Nature Conservation and the Nuclear Safety (BMU) together with the Association of German Chambers of Industry and Commerce (DIHK).

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revenue recycling and its influence on the labour market. The case of Germany, included in that report, is pertinent to this section. Germany used revenue from energy and petroleum taxes to subsidize social security contributions levied on labour, which had the effect of reducing the effective wage cost.

Several studies detailed in the report indicated that this revenue recycling resulted in slightly positive employment effects as well as a small reduction in emissions, although different findings were observed across various studies. In a research project commissioned by the German Federal Environmental Agency (UBA), Markus & Görlach (2005) show that ecological tax reform created 250,000 jobs, particularly in labour-intensive sectors during 1999-2003. Thus, it is safe to assume that at a minimum, no cumulative negative effects on employment resulted from German policy.

In other countries, green policies have included a consideration of the labour market. For example, in July 2009, the British government set out the long-term strategy to cut the nation's carbon emissions by 2020 - 18 per cent from 2008 levels under the UK Low Carbon Transition Plan. Besides the emission reduction, the plan also targets energy supplies and creation of jobs. The plan includes five major sectors: power and heavy industry; transport; homes and communities, workplaces and jobs; farming, land and waste. In Denmark, the Parliament agreed to launch the energy tax reform in March 2009, by cutting taxes on labour and raising taxes on energy, climate and transportation by about EUR 1.1 billion.

Other quantitative or qualitative green labour market policies have not yet been implemented in EU Member States. Given the sectoral employment shifts that are to be expected from a green transition (see INST-EC Discussion Paper No. 16), several green labour market policies might be necessary in the future.

Relevant questions in this regard include the early identification of future skills and needs and corresponding adjustment of education systems. Some industries10 (e.g. renewable energy sector) are driving the structural change. New technologies are applied in these industries and workers need to be trained especially in the natural and engineering sciences. Other skills, in declining industries, may not be needed in the future. Thus, skills mismatches may occur during the transition and adequate labour market policies need to be available.

Such mismatches of labour demand and labour supply can also have geographical reasons. For example, the mining industry is often concentrated in certain regions of a country. A decline of the coal and oil industry can therefore cause disproportionally high effects in those regions that result in regional unemployment. Emerging industries which demand additional labour might be located in different geographical regions. For example, wind mill parks are often erected in coastal areas or even in the sea, possibly far away from the

10 In particular enterprises which fall into Category I and Category III of the employment matrix in INST-EC Discussion Paper No. 10.

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mining industry where labour might be released. A possible regional mismatch of labour supply and labour demand must be adequately addressed by governments, e.g. by offering mobility assistance like tax deductions for moving costs.

Other green labour market policies can refer to changing wage shares in high vs. low-carbon industries as well as other effects on income distribution. The effects of a green transition on gender issues needs to be determined and appropriate policy responses must be identified.

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References

Bertram, G., 1992. Tradeable Emission Permits and the Control of Greenhouse Gases. Journal of Development Studies, (23), 423-446.

Coase, R.H., 1960. The problem of social cost. Journal of Law and Economics, (3), 1-44.

EC’s Climate Action, Emissions Trading System http://ec.europa.eu/clima/policies/ets/index_en.htm

EEA, 2005. Market-based instruments for environmental policy in Europe, Copenhagen: European Environment Agency (EEA).

Ellerman, A.D. & Joshkow, P.L., 2008. The European Union's Emissions Trading System in perspective, Pew Center on Global Climate Change.

International Energy Agency, IEA, Policies and Measures: Climate change http://www.iea.org/textbase/pm/?mode=cc

Markus, K. & Görlach, B., 2005. Effects of Germany’s Ecological Tax Reforms on the Environment, Employment and Technological Innovation, Berlin: Ecologic Institute.

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Robins, N. et al., 2010. Sizing the climate economy: We forecast the low-carbon energy market will trible to USD2.2trn by 2020, London: HSBC Global Research.

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Page 37: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

Green policies in the EU: A review

29

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Page 38: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

30

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Green policies in the EU: A review

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2002

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BELG

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32

Nam

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Type

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emis

sion

redu

ctio

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ojec

ts.

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BELG

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Sour

ce: O

ECD

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Green policies in the EU: A review

33

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Page 42: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

34

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Page 43: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

Green policies in the EU: A review

35

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Page 44: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

36

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Page 45: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

Green policies in the EU: A review

37

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Page 46: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

38

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: OEC

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Page 47: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

Green policies in the EU: A review

39

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: OEC

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40

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Page 49: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

Green policies in the EU: A review

41

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: OEC

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Page 50: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

42

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: OEC

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Green policies in the EU: A review

43

Nam

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Page 52: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

44

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Page 53: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

Green policies in the EU: A review

45

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Page 54: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

46

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Green policies in the EU: A review

47

Nam

e o

f In

stru

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nt

Typ

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Ye

ar o

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Re

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THE

NET

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LAN

DS

Page 56: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

48

Na

me

of

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h;

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lic

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or

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en

t B

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OE

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Page 57: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

Green policies in the EU: A review

49

Nam

e of

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ergy

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50

Nam

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Type

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Green policies in the EU: A review

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SP

AIN

Page 61: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

Green policies in the EU: A review

53

Na

me

of

Inst

rum

en

tT

yp

e o

f In

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me

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ar

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od

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Ins

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19

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SW

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Page 62: Green policies in the EU: A revie...Green policies in the EU: A review 3 In order to promote energy saving and reduce 2 emissions, the governments of EU CO Member States have used

54

Nam

e o

f In

stru

me

nt

Typ

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f In

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ar o

f In

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ind

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l Co

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mp

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n a

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for

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: OEC

D/I

EA

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Green policies in the EU: A review

55

Nam

e o

f In

stru

me

nt

Typ

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f In

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me

nt

Ye

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du

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ch

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ne

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at

the

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UN

ITED

KIN

GD

OM

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56

Nam

e o

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Ye

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vera

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nd

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nti

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07

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ltip

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ab

le E

ne

rgy

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ult

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cto

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oli

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sea

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un

cils

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erg

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ua

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du

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HG

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lp

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pa

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vest

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10

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wil

l be

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to

en

sure

th

e U

K m

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s e

mis

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rge

ts, s

ecu

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its

en

erg

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pp

lie

s fo

r, m

axi

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pp

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bs,

ski

lls

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vest

me

nt

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d e

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re fa

ir t

o p

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he

m

ost

vu

lne

rab

le in

so

cie

ty.

Cli

ma

te C

ha

nge

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Re

gula

tory

Inst

rum

en

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Pro

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Tra

da

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P

erm

its

20

08

To

imp

rove

ca

rbo

n m

an

age

me

nt,

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lp t

he

tra

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ard

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d

de

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nst

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str

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ad

ers

hip

.

UN

ITED

KIN

GD

OM

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Green policies in the EU: A review

57

Nam

e of

Inst

rum

ent

Type

of I

nstr

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tYe

ar o

f In

trod

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onLa

st R

evis

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ect

Act o

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2 ad

vice

line

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atio

n an

d O

utre

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2007

Prov

ides

the

UK

have

acc

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to a

'one

-sto

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op' s

ervi

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hel

p m

ake

thei

r hom

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usta

inab

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omes

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utre

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Re

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Inst

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; 20

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Volu

ntar

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n th

e Ph

ase

Out

of I

ncan

desc

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Bu

lbs

Volu

ntar

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Car

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Build

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for G

reen

er B

uild

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atio

n an

d O

utre

ach

2005

The

Swed

ish

and

UK

gove

rnm

ents

hav

e la

unch

ed a

join

t ini

tiat

ive

to s

hare

bes

t pr

acti

ces

in s

usta

inab

le b

uild

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arch

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rgy

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me

(RCE

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& D

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geth

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n on

e fr

amew

ork

all t

he R

esea

rch

Coun

cil a

ctiv

itie

s on

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rgy

rese

arch

and

trai

ning

. Cl

imat

e Ch

ange

Pro

gram

me

2006

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ic In

vest

men

t, R

D &

D,

Polic

y Pr

oces

ses;

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ulat

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rum

ents

; Tra

dabl

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rmit

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cent

ives

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sidy

2006

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ckle

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ge, i

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sev

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y

Sour

ce: O

ECD

/IEA

UN

ITED

KIN

GD

OM