Analysis
The implications for households of environmental tax reform (ETR) in Europe
☆
Paul Ekins
a,
⁎, Hector Pollitt
b
, Jennifer Barton
b
, Daniel Blobel
c
a
UCL Energy Institute, University College London, Central House, 14 Upper Woburn Place, London WC1H 0NN, United Kingdom
b
Cambridge Econometrics, United Kingdom
c
Ecologic, Germany
abstract article info
Article history:
Received 4 January 2011
Received in revised form 3 August 2011
Accepted 7 August 2011
Available online 9 September 2011
Keywords:
Environmental tax reform
Distributional impacts
European Union
Econometric modelling
The paper discusses the distributional implications of environmental tax reform (ETR) for households, and
presents new results from modelling the impacts of a major ETR for the European Union. The distributional
effects arise from the new environmental taxes, any tax reductions made as part of the ETR, the wider
macroeconomic impacts from the ETR, any special provisions in the ETR, and the environmental benefits from
the ETR. The paper's literature review makes clear that while the impacts from taxes on the household use of
energy are very often regressive, transport taxes tend not to be, although the impacts differ between urban
and rural households. Moreover, the net distributional impact is often less regressive, or not at all, once the
wider distributional effects are taken into account. Residual regressive effects can in principle be removed by
further adjustments in the tax or benefits system. The modelling results suggest that an ETR in Europe will
actually increase real incomes across the EU as a whole, and will not be generally regressive, although the
results differ by country and for different socio-economic groups. The political acceptability of ETR may
depend on the worst effects on these groups being mitigated in some way.
© 2011 Elsevier B.V. All rights reserved.
1. Introduction
The European Environment Agency has defined environmental tax
reform (ETR) as “a reform of the national tax system where there is a
shift of the burden of taxes from conventional taxes such as labour to
environmentally damaging activities, such as resource use or
pollution” (EEA 2005, p.84). ETR is therefore a particular kind of
policy instrument, which seeks to apply revenue-raising economic
instruments (which may be taxes or auctioned permits in an
emissions trading scheme) to resource use and pollution, in order to
increase the efficiency of resource use (resource productivity) and
improve the environment, and reduce other taxes such that the policy
is revenue neutral overall. ETR is therefore a tax shift, rather than a tax
increase, whereby taxation is shifted from ‘goods’ such as labour (e.g.
income taxes, social security contributions) or capital (e.g. corpora-
tion taxes) to ‘bads’ (pollution, resource depletion). ETR was
implemented on a relatively small scale in a number of North
European countries in the 1990s and early 2000s, with broadly
positive environmental and economic results (Anderson and Ekins
2009).
In the European Commission's Impact Assessment Guidelines (EC,
2009), equity issues such as social inclusion and the protection of
particular groups are clearly labelled as impacts that should be
considered ahead of any proposed change in policy or regulation. In
particular, Table 2 (p. 35) asks the question:
Does the option affect specific groups of individuals (for example the
most vulnerable, or the most at risk of poverty, children, women,
elderly, the disabled, unemployed or ethnic, linguistic and religious
minorities, asylum seekers), firms or other organisations or localities
more than others?
The literature review in Section 2 of this paper shows that such
considerations are relevant to ETR, because there is substantial evidence
that increases in environmental taxes can be regressive, meaning that
they fall disproportionately on low-income and rural households,
because these groups spend a relatively high proportion of their income
on domestic heating. This can affect the political feasibility of an ETR
package, so that policy makers considering ETR need to understand the
impacts of the package on the distribution of income across individuals
and households and, if necessary, implement measures that will reduce
or eliminate the regressivity. There is therefore an important research
question in this area, which is addressed by this paper: what would be the
distributional implications of a major ETR in Europe, and how might any
negative distributional outcomes be mitigated?
The research question was addressed by the use of a macro-
econometric model to help gain an understanding of the impacts of a
broad-based ETR on the distribution of income across individuals and
Ecological Economics 70 (2011) 2472–2485
☆ Note: This paper derives from a report from a recent project on ETR commissioned
by the European Environment Agency. Tax reform in Europe over the next decades:
implications for the environment, for eco-innovation and for household distribution’,
European Environment Agency, Copenhagen, forthcoming.
⁎ Corresponding author. Tel.: + 44 20 3108 5990; fax: + 44 20 3108 5986.
E-mail address: p.ekins@ucl.ac.uk (P. Ekins).
URL: http://www.ucl.ac.uk/energy (P. Ekins).
0921-8009/$ – see front matter © 2011 Elsevier B.V. All rights reserved.
doi:10.1016/j.ecolecon.2011.08.004
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Ecological Economics
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