A Review of Carbon and Energy Taxes in EU

Carbon and energy taxes have been frequently advocated by economists and international organisations as a policy instrument for reducing carbon dioxide emissions. In the practice of environmental policies an increasing number of Western European countries have implemented taxes based on the carbon or energy content of the energy products (Sweden, Norway, The Netherlands, Denmark, Finland, Austria, Germany and Italy). Several other countries, like Switzerland, France and the United Kingdom, are currently discussing proposals for their implementation. In the meantime, carbon or energy taxes proposals in some other countries have failed, sometimes quite disastrously (e.g. in the United States).

Taxes on Energy Products in Some Selected Countries, in Purchasing Power Parity

Country

Petrol (gasoline) unleaded

Diesel

Diesel/Gas Oil
(industrial use)

Coal
(industrial use)

Natural Gas
(industrial use)

 

$PPP / 1000 l

$PPP / ton CO2

$PPP / 1000 l

$PPP / ton CO2

$PPP / 1000 l

$PPP / ton CO2

$PPP / 1000 kg

$PPP / ton CO2

$PPP / 1000 m3

$PPP / ton CO2

Denmark

395

164

272

95

206

(197 - 180)

72

(69 - 63)a

163

(153 - 136)

67

(63 - 56)

28

(21 - 6)

15

(11 - 3)

Finland

558

232

324

113

55

19

33

14

28

15

France

590

245

370

129

78

27

0

0

1

1

Germany

495

205

313

109

40

14

0

0

33

17

Netherlands

583

242

336

117

102

36

11

5

55

29

Norway

520

216

403

140

46

(23)

16

(8) b

46

19

93

49

Spain

490

203

356

124

104

36

0

0

8

4

Sweden

456

189

295

103

183

64

(19) c

126

52

(19)

105

56

(22)

Switzerland

356

148

372

129

1

1

0

0

0

0

UK

630

261

645

224

40

14

0

0

0

0

USAd

101

42

116

40

na

na

na

na

na

na

Japane

320

133

124

43

4

1

na

na

23
(8)

12
(4)

source: Baranzini, Goldenberg and Speck, 2000.

na: not available.
a Tax rate is for light processes and heavy processes.
b Tax rate is for gas oil used in the pulp and paper industry.
c Tax rate is for energy products used in the manufacturing industry and greenhouse horticulture sector.
d Figures for USA: 1996 (source OECD/IEA: Energy Prices and Taxes. Paris, 1997).
e Figures for Japan: 1996 for petrol and diesel; 1995: gas oil; 1994 natural gas (source OECD/IEA: Energy Prices and Taxes. Paris, 1997). Japan has a general petroleum excise tax on all crude oil refined in Japan: rate was 1996 2040 yen/1000 l - 12.1 $PPP/1000 l (this figure is not included in the above table).
Tax rates for European countries are for 1998 in national currencies and then converted with 1997 purchasing power parities (PPP) 1997 (PPP source: OECD Main Economic Indicators July 1998, Paris)

In countries where carbon/energy taxes have been implemented, several issues are generally considered in the course of developing overall tax policies. Often, carbon/energy taxes:

Taxes on energy products and the derived ‘implicit’ carbon taxes vary significantly between countries (see table on energy taxes on page 8), and thus the average price of a ton of carbon is relatively different from country to country. This is one of the main problems to implement internationally coordinated carbon taxes.

Data in the table also shows that there are large differences between the taxation levied on different energy products. Some fuels, like petrol and diesel, are heavily taxed. The main reason is that those energy products possess low demand elasticities, and thus taxing them is an easy way to collect fiscal revenues. With respect to the carbon content of energy products, it should also be noted that, in almost all countries (except Sweden and Denmark), coal has a particularly low implicit carbon tax. In fact, coal is even still heavily subsidised in countries like Germany and Spain. More in general, fossil fuels with higher carbon content often have lower implicit carbon taxes than those with lower carbon content. Therefore, with respect to the objective of reducing carbon emissions, a reform of the energy tax structure should accompany the eventual introduction of carbon taxes.

Empirical studies evaluating the environmental effectiveness of implemented carbon taxes are rather limited so far. The lack of appropriate studies can be ascribed to the fact that there are several methodological difficulties and complexities in doing such evaluation studies. The few evaluation studies demonstrate that carbon taxes are an effective instrument in reducing CO2 emissions.

An evaluation study of the Swedish CO2 tax carried out by the Swedish Environmental Protection Agency (SEPA) concludes that the CO2 tax "… has helped to reduce emissions of carbon dioxide in line with Swedish environmental policy" (SEPA 1997, p.52). The Danish Ministry of Finance estimated the effect of the carbon/energy tax regime a 4.7% reduction in CO2 emissions from 1988 levels in the year 2000.

Detailed information of environmental related taxes and charges and of energy taxes implemented in the EU Member States plus Norway and Switzerland can also be found in European Commission 1999.

Baranzini, Goldenberg, and Speck. "A Future for Carbon Taxes" in Ecological Economics. Forthcoming, March 2000.

European Commission. "Database of Environmental Taxes in the European Member States plus Norway and Switzerland - Evaluation of Environmental Effects of Environmental Taxes," Office for Official Publications of the European Communities, 1999. The database can also be downloaded from the homepage of DGXI http://europa.eu.int/comm/dg11/enveco/index.htm.

Swedish Environmental Protection Agency (SEPA) "Environmental Taxes in Sweden - Economic Instruments of Environmental Policy." Report 4745. Stockholm. 1997.

Ekins, P. and S. Speck. Competitiveness and Exemption from Environmental Taxes in Europe. "Environmental and Resource Economics." Vol.13. pp.369-396. 1999.


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