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The European Union Emission Trading Scheme
The members of the
European Union (EU) agreed to jointly
fulfil their commitments to reduce greenhouse
gas emissions caused by human activity under
the
Kyoto Protocol. On 13 October 2003,
the European Parliament and Council published a directive
establishing a scheme for greenhouse gas
emission trading between the member states
and the
EU Emission Trading Scheme (ETS) was
launched on 1 January 2005. It is the
largest cap and
trade scheme in the world. The second
stage (or trading period) of this scheme commenced
on 1 January 2008. The second trading
period under the ETS coincides with the five-year
period—known as the 'first commitment
period'—in which the EU and member states
must meet their targets for limiting or reducing
emissions of greenhouse gases under the Kyoto
Protocol on climate change. A third stage
will commence from 2012.
The overall aim of the EU ETS is to reduce
greenhouse gas emissions in an economically
efficient manner. Currently, the scheme
has the following features:
- Each participating country produced
a national emissions permits allocation
plan.
-
The total EU emissions cap is an
amalgamation of the separate national
plans as approved by the European Commission.
-
Once a national emissions plan had
been decided upon, individual facilities
within each county were allocated
a number of emission permits. Each permit
represented a tonne of carbon dioxide
(CO2) (these
permits were also known as European
Emission Allowances or EUAs).
-
During the second and subsequent
trading periods, unused emissions permits
may be 'banked' by their holders and
used during following trading periods.
This is a significant change from the
first trading period.
-
At least 90 per cent of the
emission allowances were distributed
free of charge during the second trading
period. The remaining 10 per cent
of permits may be auctioned. The proportion
of permits auctioned will increase in
the third and subsequent trading periods.
-
As emissions occur the emitter is
required to surrender the relevant number
of emission permits to cover those emissions.
This occurs each December.
-
A country can partly meet its emissions
targets by the limited use of emissions
offsets (but not from forestry).
-
There is limited acceptance of emissions
credits generated by the Kyoto Protocol
Clean Development and Joint Implementation
Mechanisms.
-
A fine of €100 per tonne
of CO2 made over
the prescribed limits is payable to
the Commission.
-
Reporting, enforcement and compliance
are undertaken by participating states
during the second trading period. A
central administrator verifies the operation
of the EU ETS.
-
Initially, the scheme covered only
about 50 per cent of the projected
CO2 emissions,
but not other greenhouse gases such
as methane. However, the directive establishing
the scheme clearly includes the six
main Kyoto Protocol greenhouse gases
and contemplates the addition of other
gases as the scheme develops.
-
The scheme covers a wide range of
power generation and metals/minerals
processing facilities (but not aluminium,
yet). However, the first trading period
did not cover the transport, construction,
waste processing and farm sectors and
some industrial plants.
-
The aviation sector will be included
in the scheme with ongoing consideration
of including the general transport sector.
-
Norway, Iceland and Liechtenstein
will join the scheme.
The first trading period of the EU Emission
Trading Scheme had as its overall objective
the creation of the critical mass for a liquid
and well-functioning carbon market. The first
trading period was always intended to be a
'learning by doing' phase for all the parties
involved. The first trading period led to
the following:
-
A European CO2
market was firmly established.
-
There was an over-supply of permits
compared to actual emissions.
-
A volatile emissions permit price
in 2005–06 and a ridiculously low
permit price in 2007.
-
A small reduction in emissions during
2005 and 2006, but a small rise in emissions
during 2007.
-
Emissions reductions from unexpected
sources, such as using hard black coal
in previously brown coal fired power stations.
-
Emissions trading became a firm part
of European industry and business planning.
-
There was minimal impact on industrial
competitiveness during the first trading
period. However, this was over a time
of buoyant economic conditions and with
a limited application of emissions trading.
-
Some sectors made windfall profits
during the first trading period.
There are a number
of lessons for the design of an Australian
ETS from the experience of the EU ETS during
its first trading period, such as:
-
The EU ETS further entrenched
cap and trade schemes as the preferred
way to control emissions.
-
The scarcity of emissions permits
in such schemes must be maintained.
-
There is no substitute for accurate
verifiable emissions data for the efficient
operation of such schemes.
-
Emission permits must be allocated
on a consistent basis, preferably by a
central administrator or by a market based
mechanism such as auctioning.
-
Unused emission permits must be able
to be 'banked' for later use.
-
The best may be the enemy of the good.
The EU ETS was still able to achieve a
reduction in emissions, even with a comparatively
low emissions price and many economic
sectors not covered by the scheme. This
suggests that an ETS need not be perfectly
designed to produce worthwhile outcomes
and to gather relevant experience in operating
such a scheme.
Further reading:
A. Denny Ellerman and P. Joskow,
The European Union's Emissions Trading
System in Perspective, Pew Centre
on Climate Change, May 2008.
L. Nielson,
The European Emissions Trading System—Lessons
for Australia, Research paper,
no. 3, 2007–08, Parliamentary Library,
Canberra, 20 August 2008.
16 February, 2010
Comments to: web.library@aph.gov.au
Last reviewed
16 February, 2010
by the Parliamentary Library Web Manager
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