An Overview of Greenhouse Gas (GHG) Control Policies in Various Countries


An Overview of Greenhouse Gas (GHG)
Control Policies in Various Countries

Jane A. Leggett
Specialist in Energy and Environmental Policy
Richard K. Lattanzio
Analyst in Environmental Policy
Carl Ek
Specialist in International Relations
Larry Parker
Specialist in Energy and Environmental Policy
December 30, 2009
Congressional Research Service
7-5700
www.crs.gov
R40936
CRS Report for Congress
P
repared for Members and Committees of Congress

An Overview of Greenhouse Gas (GHG) Control Policies in Various Countries

Summary
As Congress considers legislation to address climate change, and follows negotiations toward a
new international agreement to reduce greenhouse gas (GHG) emissions, the question of the
comparability of actions across countries frequently arises. Concerns are raised about what the
appropriate sharing of efforts should be among countries, as well as the potential trade
implications if countries undertake different levels of GHG reductions and, therefore, incur
varying cost impacts on trade-sensitive sectors. This report summarizes the GHG control policies
in effect or under consideration in the European Union (EU) and various other large countries,
and offers a brief set of initial observations. It gives particular emphasis to how particular trade-
sensitive sectors may be treated in the context of each national program.
All countries examined have in place, or are developing, some enforceable policies that serve to
reduce GHG emissions. Most are at some stage of making their programs more stringent. The
wealthiest countries have all taken on GHG limitation or reduction targets under the Kyoto
Protocol. Some of the emerging economies have voluntarily stated GHG targets, though none
have yet accepted legally binding obligations in an international agreement. The forms of targets,
and their stringencies, vary widely across countries.
The scope of specific GHGs and economic sectors covered by national (or sub-national)
reduction measures is generally, but not completely, similar. All have policies that affect carbon
dioxide emissions; most have some measures that cover the additional five gases covered under
the Kyoto Protocol (methane, nitrous oxide, sulfur hexafluoride, perfluorocarbons, and
hydrofluorocarbons).
The programs and measures used vary across countries. Even when some measures have similar
names (e.g., voluntary programs and voluntary action plans), the measures may differ in
important ways that may influence their effectiveness and impacts on trade competiveness.
Within sectors of a country, emission rates and control requirements may vary widely. A country
may have some facilities with emission rates (or energy intensities) comparable to the best
globally, even if the country’s sectoral average as a whole has, for example, a significantly higher
energy intensity than the global average.
This report presents an overview of GHG control policies within individual countries. It does not
present a rigorous assessment of the comparability of GHG control policies across countries or
within specific sectors. The criteria for assessing comparability internationally are not widely
agreed, and could encompass a range of considerations, not all quantitatively measurable.

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An Overview of Greenhouse Gas (GHG) Control Policies in Various Countries

Contents
Synthesis Observations ............................................................................................................... 1
European Union .......................................................................................................................... 3
France......................................................................................................................................... 9
Germany................................................................................................................................... 11
United Kingdom ....................................................................................................................... 13
Australia ................................................................................................................................... 16
Brazil........................................................................................................................................ 19
Canada...................................................................................................................................... 23
China ........................................................................................................................................ 25
India ......................................................................................................................................... 29
Japan ........................................................................................................................................ 33
Korea........................................................................................................................................ 38
Mexico ..................................................................................................................................... 40
Russian Federation.................................................................................................................... 42
United States............................................................................................................................. 47

Figures
Figure 1. Japanese Regulations or Exemptions Specific to Trade-Sensitive Sectors.................... 36
Figure 2. Russian Total Primary Energy Supply, 1990 and 2006 ................................................ 43
Figure A-1. Comparison of International Fuel Economy and GHG Standards ............................ 51
Figure A-2. Standardized Comparison of Select Vehicle Efficiency Standards
Internationally........................................................................................................................ 52

Tables
Table 1. Average Required Fuel Economies under Proposed Standards ...................................... 48

Appendixes
Appendix. Comparison of Vehicle Efficiency Standards Internationally (as of Mid-2009).......... 51

Contacts
Author Contact Information ...................................................................................................... 52

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An Overview of Greenhouse Gas (GHG) Control Policies in Various Countries

his report summarizes the greenhouse gas (GHG) control policies in effect or under
consideration in a number of large countries, and offers a brief set of initial observations.
T This overview allows preliminary comparison across countries. Because of congressional
interest in the comparability of countries’ actions, and in the potential trade ramifications of
differential policies, these country fact sheets give emphasis to how particular trade-sensitive
sectors may be treated in the context of each national program. Where specific industries are not
listed in a country’s fact sheet, no further information was found.
The European Union’s policies are presented first, followed by any additional rules or policies
under consideration in several of the largest EU Member States (i.e., France, Germany, the United
Kingdom). A number of additional large-emitting countries follow in alphabetical order. Finally,
the Appendix provides a comparison of early 2009 vehicle efficiency standards across countries,
which may be a useful reference for a sector that emits a large portion of global GHG emissions.
Synthesis Observations
• All countries examined have in place, or are developing, some enforceable
policies that serve to reduce greenhouse gas (GHG) emissions. Most are at some
stage of making their programs more stringent.
• The scope of specific GHGs and economic sectors covered by national (or sub-
national) reduction measures is generally, but not completely, similar. All have
policies that affect carbon dioxide (CO2) emissions; most have some measures
that cover the additional five gases covered under the Kyoto Protocol, including
methane (CH4), nitrous oxide (N2O), sulfur hexafluoride (SF6), perfluorocarbons
(PFC), and hydrofluorocarbons (HFC).
• The programs and measures used vary across countries. Even when some
measures have similar names (e.g., voluntary programs and voluntary action
plans), the measures may differ in important ways that may influence their
effectiveness and impacts on trade competiveness. For example, many countries
support “voluntary programs” or “voluntary action plans.” Some of these
voluntary efforts may provide technical assistance with few requirements from
participants; other programs may include formal emission reduction targets,
reporting, and governmental pressure to achieve targets.
• Within economic sectors of a country, emission rates and control requirements
may vary widely. A country may have some facilities with emission rates (or
energy intensities) comparable to the best globally, even if the country’s sector as
a whole has, for example, an energy intensity significantly higher than the global
average for that sector. Such discrepancies often occur in emerging economies
wherein an older, less-efficient industrial sector is being replaced by new
infrastructure.
• Most of the programs include provisions to assist or exempt trade-sensitive
sectors, but the definition of what is trade-sensitive, and the approaches to
assisting or protecting the sectors, vary widely. “Trade-sensitivity” is a
continuing phenomenon. Companies become more or less competitive on an
international market according to a host of factors, including productivity, market
demand, resource costs, labor costs, exchange rates, and the like. The addition of
a carbon control regime to this competitive dynamic has raised concerns that, in
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An Overview of Greenhouse Gas (GHG) Control Policies in Various Countries

the absence of similar policies among competing nations, trade-exposed
industries that must control their emissions, or face increased costs passed-
through by suppliers, may be less competitive and may lose global market share
to competitors in countries lacking comparable carbon policies.1 These concerns
have led many countries to consider specific provisions for exposed sectors.
• Assessing the comparability of GHG control policies across countries and in
specific sectors could be difficult, and the results could be subject to debate. How
well alternative policy directions and methods could stand up under possible
challenges against border adjustments under the World Trade Organization
(WTO) may merit further investigation. However, consideration of specific
methods to assess comparability, and their implications, is beyond the scope of
this report.

1 For a further discussion on trade-sensitivity issues, see CRS Report R40100, “Carbon Leakage” and Trade: Issues
and Approaches
, by Larry Parker and John Blodgett; and CRS Report R40914, Climate Change: EU and Proposed
U.S. Approaches to Carbon Leakage and WTO Implications
, by Larry Parker and Jeanne J. Grimmett.
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European Union2
1. Overall GHG emission target, if any, and timing:
Under the Kyoto Protocol, the European Union (EU) agreed to reduce GHG emissions of its 15
Member states in 1997 (EU-15) in aggregate by 8% below 1990 levels during the first
commitment period of 2008-2012. (There is no collective target for the EU-27, the current 27
Member states of the EU.) In 2007 and 2008, EU-15 GHG emissions were approximately 5% and
6%, respectively, below 1990 levels. In November 2009, The European Commission projected
that the EU-15 will surpass its obligation to reduce GHG emissions under the Kyoto Protocol.3
The EU-15 will have reduced their domestic GHG emissions to about 7% below 1990 levels
during 2008-2012. Plans by EU-15 Member states to acquire international credits through the
Kyoto Protocol’s three market-based mechanisms would provide another 2.2% GHG reduction,
while acquisitions by operators in the EU Emission Trading Systems may provide an additional
1.4% GHG reduction, and enhancement of carbon removals by sinks may offer another 1.0%.
With additional policies and measures, the Commission projects that the EU-15 may be around
13% below 1990 levels in 2008-2015.
For the post-Kyoto period (beyond 2012), the European Council adopted on April 23, 2009, the
“20-20-20” Policy”—a climate and energy package to require by 2020:
• a 20% reduction in GHG emissions from 1990 levels,
• a 20% share of renewable energy in the European Union’s final consumption
figures (including a 10% share in each Member State’s transport sector), and
• a 20% reduction in energy consumption.4
The legislation also committed to scale up the GHG emission reduction target to 30% if other
developed countries make comparable efforts under a new international agreement. The purpose
is to limit the global temperature rise to no more than 2˚Celsius above preindustrial levels.
2. Principal Policy Instrument(s):
a. Expansion of current European Union Emissions Trading System (EU ETS).5
b. Effort-sharing relationships among Member States to reduce emissions in sectors not covered
by the EU ETS. It will be left to Member States to define and implement policies in such sectors,
although a number of EU-wide measures in areas such as efficiency standards, passenger car
emission standards, and a landfill directive for waste disposal will contribute. The European

2 This section was prepared by Richard K. Lattanzio, Analyst in Environmental Policy (7-1754), with input from Larry
Parker, Specialist in Energy and Environmental Policy (7-7238) and Jane A. Leggett, Specialist in Environmental and
Energy Policy (7-9525).
3 http://europa.eu/rapid/pressReleasesAction.do?reference=IP/09/1703&format=HTML&aged=0&language=EN&
guiLanguage=en.
4 See {COM(2008) 13 final}; {COM(2008) 16 final}; {COM(2008) 17 final}; {COM(2008) 18 final}; {COM(2008)
19 final} at http://ec.europa.eu/environment/climat/emission/pdf/com_2008_16_en.pdf.
5 (2003/87/EC); see http://europa.eu/rapid/pressReleasesAction.do?reference=IP/09/628&format=HTML&aged=0&
language=EN&guiLanguage=en. Also see CRS Report RL34150, Climate Change and the EU Emissions Trading
Scheme (ETS): Kyoto and Beyond
, by Larry Parker.
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Community infringement procedures and mechanisms for corrective action under the effort-
sharing decision are to be put in place to monitor progress.6
c. Regulations stipulating mandatory national targets for the overall shares of energy from
renewable sources in gross final consumption of energy, taking into account differing starting
points for each Member.7 It will be left to Member States to determine renewable share allocation
among sectors.
At the national level, several EU Member states also impose carbon emission fees to some
degree. Carbon fees exist in Denmark, Finland, and Sweden. French President Sarkozy had
announced carbon taxes to begin on January 1, 2010, on French households and motor fuels,
though their introduction has been delayed by an adverse constitutional ruling. Spain and Ireland
reportedly have also signaled that they may consider domestic carbon fees in addition to EU and
other national policies.8 In addition, on October 5, 2009, an EU Taxation Commissioner revealed
that in early 2010 the European Commission plans to propose an expansion of existing energy
taxation in order to charge CO2 emission fees as well.9 The new carbon tax would cover sectors
not under the EU ETS (see below), such as agriculture, households, and transport. The proposal
explicitly is intended to help the EU achieve compliance with its law to reduce GHG emissions to
20% below 1990 levels by 2020. All taxation proposals, to pass into law, require unanimous
agreement of the 27 EU Member states, which may be difficult to achieve, and the assent of the
European Parliament.
3. Covered Gases and Sectors:
The only greenhouse gas covered under the original 2003 EU ETS was CO2. The expanded EU
ETS to take effect in 2013 will add N2O emissions from nitric, adipic, and glyoxalic acid
production, and PFC emissions from the aluminum sector. Gases not stipulated in the EU ETS,
but defined as “greenhouse gases” in Annex II of DIRECTIVE 2003/87/EC include CH4, HFC,
and SF6. These gases will be controlled under guidelines for sectors not covered by the EU ETS.
Sectors originally covered in the 2003 EU ETS were: power and combustion installations
(exceeding 20 megawatts (MW)); petroleum refineries; coke ovens; metal ore production
installations; iron and steel production installations (exceeding 2.5 tons of product per hour);

6 Each Member State is responsible for the implementation of Community law (adoption of implementing measures
before a specified deadline, conformity and correct application) within its own legal system. Under the Treaties (Article
226 of the EC Treaty; Article 141 of the Euratom Treaty), the Commission of the European Communities is responsible
for ensuring that Community law is correctly applied. Consequently, where a Member State fails to comply with
Community law, the Commission has powers of its own (action for non-compliance) to try to bring the infringement to
an end and, where necessary, may refer the case to the European Court of Justice. For additional information, see
http://ec.europa.eu/community_law/infringements/infringements_en.htm
7 Directive 2009/28/EC of the European Parliament and of the Council of 23 April 2009.
8 See, for example, Andres Cala, Europe Warming to Carbon Tax, Energy Tribune. “Spain and Ireland, which until
recently were considered unlikely candidates to follow suit because of their high unemployment rates, are also
weighing adding similar levies next year. Ireland’s Finance Minister, Brian Lenihan, said recently that the government
would not raise taxes to finance next year’s budget, with the single exception of a carbon tax.... Spain’s Prime Minister
Jose Luis Rodriguez Zapatero, which has announced a fiscal reform to raise more money to control a rampant deficit,
called the carbon tax an ‘interesting’ proposal and added carbon taxes will inevitably be applied by most countries.” 23
Sept. 2009. http://www.energytribune.com/articles.cfm?aid=2354
9 http://news.bna.com/deln/DELNWB/split_display.adp?fedfid=15354499&vname=dennotallissues&fn=15354499&
jd=a0c0y8h5r1&split=0; http://www.reuters.com/article/GCA-GreenBusiness/idUSTRE59544A20091006.
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factories for cement (exceeding 50 tons per day), glass (exceeding 20 tons per day); ceramics
including tiles, bricks, stoneware, porcelain (exceeding 75 tons per day); and production of pulp,
paper and board (exceeding 20 tons per day). The expanded EU ETS will increase the scope of
covered sectors beginning in 2013 to include primary and secondary aluminum production
facilities; ferrous, ferro-alloy, and non-ferrous metal production facilities; mineral wool and
gypsum plants; ammonia, petro-chemical and chemical plants including carbon black organics,
nitric acid, adipic acid, glyoxal, organic chemicals (exceeding 100 tons per day), hydrogen
(exceeding 25 tons per day), soda ash, and sodium bicarbonate. Additionally, certain categories of
aviation will be incorporated into the ETS involving commercial flights departing or arriving in a
territory of a Member State.10 In the EU ETS, Member states decide a National Allocation Plan
(NAP), subject to review by the EU, to give emission allowances to individual plants. In the first
pilot trading period, some Member states allocated more emission allowances than needed to
companies, so that revisions to the scheme in Phase III, beginning in 2013, have been adopted to
avoid over-allocation, including increasing rates of auctioning allowances.
Sectors not covered by the EU ETS but covered by adopted legislation include transport, housing,
agriculture, and waste (see the following discussion).
4. Allocation of GHG reductions to various sectors:
The European Union’s programs call for a 21% reduction in EU ETS sector emissions compared
to 2005 and a 10% reduction in non-EU ETS sector emissions compared to 2005. This is
expected to achieve an overall reduction of 14% compared with 2005, which is equivalent to a
reduction of 20% compared with 1990. The EU ETS covers electricity generation and the main
energy-intensive industries—power stations, refineries, iron and steel, cement and lime, paper,
food and drink, glass, ceramics, engineering, and vehicles. Initially, countries allocate allowances
to covered sectors, but limited auctioning of permits is planned for the future (e.g., maximum
10% of allowances are auctioned in Phase II).
Phase III ETS: Emissions from sectors covered in the EU ETS will be cut 21% from 2005 levels
by 2020. A single EU-wide cap on emissions will be set for EU ETS covered sectors. Allowances
will be allocated on the basis of rules harmonized across Member states. The tentative annual cap
figure will begin at 1,974 million tons CO2 in 2013 and decrease annually. The total number of
allowances (one allowance equals permission to emit one ton) in 2013 will begin at the average
total quantity issued for the 2008-2012 period and will decrease annually at a rate of 1.74%. Free
allocation of emission allowances will be progressively replaced by auctioning allowances by
2020. Auctioning will begin in 2013 at 20% and gradually rise to 70% in 2020 and to 100% in
2027. Power producers must acquire all allowances at auction in order to prevent windfall profits
(following experience under the pilot trading period). Member States that are highly dependent on
fossil fuels and/or States insufficiently connected to the grid (these include Bulgaria, Cyprus,
Czech Republic, Estonia, Hungary, Latvia, Lithuania, Malta, Poland and Romania) are allowed to
apply for a derogation procedure of reduced auctioning rates for power production of 30% in
2013, gradually rising to 100% in 2020, as long as producers invest in clean technologies to the
market value of the permits. Furthermore, less affluent states (the 10 above plus Greece and
Portugal) will receive an increased amount of emission permits to auction amounting to 12%
more than their actual share to assist in revenue generation. Each Member state will be allowed to

10 See CRS Report R40090, Aviation and Climate Change, by James E. McCarthy.
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determine use of revenue with a suggested investment of 50% toward clean technologies and
pollution abatement.
Non-ETS: Sectors not covered by the EU ETS are transport, housing, agriculture and waste. The
2009 Directive proposes to cut emission in these sectors by 10% EU-wide from 2005 levels by
2020. Targets will be mandated according to each Member states’ relative wealth (based on GDP
per capita and economic growth prospects) with figures ranging from -20% to +20%. Targets are
binding on Member states and are enforceable through the usual EU infringement procedure.11 If
a country exceeds its annual objective, it must implement corrective measures, and will be
penalized via a deduction from the following year’s CO2 allowance. Several flexibility measures
are available including the possibility of trading emission cuts across countries; carrying forward
(“banking”) extra emission reductions; and using a limited amount of credit from developing
countries (through an offsets mechanism similar to the Kyoto Protocol’s Clean Development
Mechanism).
The transportation sector has legally binding standards for CO2 emissions from new passenger
cars to apply as of 2012 in order the meet the 20% emission reduction by 2020.12 Reductions are
required to achieve 120 grams carbon dioxide per kilometer (CO2/km) for 65% of fleet in 2012,
75% in 2013, 80% in 2014 and 100% starting in 2015. A target of 95 grams CO2/km is set for
2020. Enforcement is set through financial penalties against the car manufacturers depending on
how far their fleet exceeds the targets.13
A renewable energy mandate sets mandatory national targets for each Member state in accordance
with each country’s different starting points. The purpose of mandates is to provide certainties for
investment. Each country will report to the European Council by June 2010 regarding how each
Member has allocated the renewable target among transport, electricity, heating and cooling
sectors. A 10% target for renewable energy in the transportation sector is set at the same level for
all countries.
5. Any regulations or exemptions specific to trade-sensitive sectors:
The climate and energy package in the 2009 Directive provides that the risk of “carbon leakage”14
may be reduced by allotting free carbon allowances to businesses exposed to “significant risk of
carbon leakage” (SRCL) by the cost of compliance with the EU ETS. (The European
Commission must adopt a list of sectors deemed exposed to a significant risk of carbon leakage
no later than December 31, 2009. A draft list was proposed in September 2009, discussed below.)
However, any free allowances will not be decided until 2011. The list may be revised before
2014, based on reanalysis of trade figures, and identification of countries that make firm
commitments to reduce their GHG emissions.

11 http://www.consilium.europa.eu/uedocs/cms_data/docs/pressdata/en/misc/107136.pdf.
12 Directive 2009/33/EC of the European Parliament and of the Council of 23 April 2009.
13 http://www.consilium.europa.eu/uedocs/cms_data/docs/pressdata/en/misc/107136.pdf.
14 If one or more countries requires carbon controls that add to production costs in businesses that compete
internationally, it is possible for “carbon leakage” to occur if production in the controlled countries declines because
purchasers instead buy increased supply from uncontrolled producers in other countries. Though emissions may decline
from the controlled facilities, they may increase at uncontrolled facilities, thereby leading to “carbon leakage.” This
would offset the benefits of the emission controls.
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If international negotiations on climate change in Copenhagen do not lead to a comprehensive
international agreement, several criteria permit an EU ETS-covered industrial sector to allege
SRCL:
• if the industry can demonstrate that purchasing permits increases its costs (more
than 5% of gross value added) and faces international competition (non-EU trade
intensity above 10%), or
• if the industry can demonstrate that purchasing permits significantly increases its
costs (more than 30% of gross value added), or
• if the industry faces international competition (non-EU trade intensity above
30%), then it can qualify for the free allocation of allowances.
Free allocation of permits typically will not be at 100% of needs for SRCL facilities, however.
Free allowances will be adjusted according to Community-wide ex-ante benchmarks so as to
ensure incentives for GHG reduction. The benchmarks will be set at the average performance of
the 10% most GHG emissions-efficient installations in a sector in 2007-2008. Only the most
efficient businesses in a sector, therefore, have a chance to receive all of their allowances free. If a
business emits more than this benchmark allocation, it will need to acquire allowances up to its
actual emissions.
As of September 2009, EU analysis assessed the industries and productions potentially exposed to
carbon leakage risks. Assuming that 100% of allowances were auctioned (which will not occur
initially), the analysis concluded that 146 sectors (out of 258) and five additional product
categories meet the EU’s criteria for being exposed to SRCL.15 Outside of these sectors, 13
subsectors and products may be exposed to risk: food processing industries; industrial gases; non-
metallic mineral products; glass fibers (filament glass fibers); and, colors and similar preparations
for ceramics/glass etc.16 The EU analysis estimates that the listed sectors now constitute about
75% of GHG emissions covered by the EU ETS.
An alternative approach to issues of competitiveness in trade sensitive sectors put forward by the
European Commission is the integration of importers into the EU ETS. Under an integrated
emission trading regime, foreign producers would purchase emission certificates for their imports
according to the emissions produced. In a speech in London on January 21, 2008, the President of
the European Commission, Jose Manuel Barroso, said: “I think we should also be ready to ...
require importers to obtain allowances alongside European competitors, as long as such a system
is compatible with WTO requirements.” Beyond these measures, French President Nicolas
Sarkozy, with possible interest from German Chancellor Angela Merkel, has indicated interest in
potentially charging carbon levies against imports from countries that do not meet stringent
environmental standards. (See fact sheet on France. See also the Appendix, comparing EU
efficiency standards for motor vehicles with those of other countries.)
On December 22, 2009, E.U. environment ministers—including those from then-E.U. President
Sweden and incoming-E.U. President Spain—were stated as saying that the 27-nation bloc would

15 Of the 146 sectors, 117 have trade intensity > 30%; 27 have both estimated CO2 costs >5% and trade intensity >
10%; and two sectors have CO2 cost above 30% and trade intensity < 10%. Hans Bergman, “Sectors Deemed to be
Exposed to a Significant Risk of Carbon Leakage—Outcome of the Assessment” presentation to Working Group 3
Meeting, 18 September 2009.
16 http://ec.europa.eu/environment/climat/emission/carbon_en.htm.
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consider imposing carbon tariffs and other border sanctions in the wake of perceived failures at
the Copenhagen climate conference. No details were stated, but Teresa Ribera, Spain’s Secretary
of State for Climate Change, reportedly said that Spain plans to convene special meetings for the
E.U. environmental ministers in the upcoming months to discuss the “strategic line” the European
Union should take in promoting an international environmental agenda.
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France17
(Policies and statements if substantially different from the European Commission)
1. Overall GHG emission target, if any, and timing:
Under the Kyoto Protocol, France’s share of the EU target is not to exceed the 1990 level during
the period 2008-2012.
France has a stated long-term national GHG emissions target of 75% below the 1990 level by
2050. A law is planned to reduce energy consumption of existing buildings by 38% by 2020.
2. Principal Policy Instrument(s): (See “EU ETS.”)
Beyond instruments of the European Union, policy considerations have ranged from a freeze on
the building of new highways and airports, to a vast plan to shift freight traffic from road to rail,
to a commitment to slash pesticide use by half within 10 years by Europe’s biggest farm producer.
Tramway and TGV high-speed train networks are to be extended, and drivers encouraged to buy
cleaner cars through bonuses and penalties. In October 2007, French President Nicolas Sarkozy
called for a plan to institute a national “carbon tax” on global-warming pollutants. The Sarkozy-
proposed carbon tax was rejected by France’s Constitutional Council in December 2009;
however, the party said the measure would be redrafted for passage in 2010 (see below).
3. Covered Gases and Sectors: (See “European Union.”) The administration’s proposed carbon
tax would apply to households and motor fuels but not to large businesses and power generators,
as they are not covered by the EU ETS.
4. Allocation of GHG reductions to various sectors:
About half of French industry’s GHG emissions are covered by the EU ETS, including large
emission sources in the power generation, iron, steel, glass, cement, pottery and brick sectors.
In September 2009, President Nicolas Sarkozy stated that the proposed carbon tax would begin in
January 2010. Because Sarkozy’s party holds a majority in its parliament, expectations are that
the new carbon levy will be enacted into law. Initially set at 17 Euros (US$25)18 per ton of
emitted CO2, the tax on the use of oil, natural gas and coal would nudge up the cost of a liter of
gasoline by US$0.06 (US$0.23 a gallon). It would apply to households as well as enterprises, but
not to the heavy industries and power companies in France that are covered by the EU’s
emissions trading scheme (see the EU ETS under “European Union”). Revenues from the new tax
would be returned to taxpayers through cuts in income tax and other taxes. France’s Le Monde
newspaper says the tax will cover 70% of the country’s carbon emissions (e.g., from vehicles) and
bring in about 4.3 billion Euros (US$6.4 billion) of revenue annually. Sweden, Denmark, Finland,
Norway and Switzerland already impose similar taxes, although Sweden’s is levied at a much
higher emission fee (108 Euros/ton of CO2, or US$161/ton).

17 This section was prepared by Richard K. Lattanzio, Analyst in Environmental Policy (7-1754).
18 Live market currency exchange rate for November 19, 2009, is listed as 1 Euro equivalent to 1.49 US$
(http://www.xe.com/). Currency rates are subject to fluctuation.
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On December 28, 2009, France’s Constitutional Council rejected the carbon tax because the bill
reportedly contained too many exceptions for polluters, broke with past practices, and produced
an unfair tax burden on individual consumers. The French Council was stated as saying that the
tax was flawed because it would have raised the cost of vehicle and home heating fuel without
commensurate increases on other sources of emissions. The Sarkozy administration promised an
amended bill back to council ministers by January 20, 2010. To address objections, a new bill
would need to subject corporate industry to the tax, a requirement opposed by French companies
already concerned with decreasing competitiveness. France continues to back efforts to introduce
an E.U.-wide carbon tax and a border tax at E.U. frontiers as ways to allay industry concerns (see
below).
5. Any regulations or exemptions specific to trade-sensitive sectors:
French President Nicolas Sarkozy has promoted a European levy on carbon-intensive imports
from countries outside the Kyoto Protocol. The United States could be subject to such proposed
fees should it not adopt legally enforceable GHG controls domestically. The Economist has said,
“That leads some to suspect that his ultimate objective is to create a pretext for
protectionism.”19,20
In addition, President Sarkozy, along with German Chancellor Angela Merkel, has called for the
United Nations to support “appropriate adjustment measures” to be levied against countries that
do not join or implement an international agreement being negotiated for agreement in
Copenhagen in December 2009.21
Motor Vehicles: A law is planned to cut GHG emissions from transport by 20% by 2020; it
would include a goal of 7% bio-fuels by 2010 and EU emissions limit for new cars—130g/km—
to be phased in from 2012.

19 Economist, Sept. 17 2009. http://www.economist.com/world/europe/displaystory.cfm?story_id=14460346.
20 In the international negotiations held in Copenhagen in December 2010, France (nor the EU) agreed with the United
States, Australia, and China to reaffirm a principle not to hide trade protectionism behind climate change policy
measures, according to a New York Times article. http://www.nytimes.com/2009/12/16/business/global/16trade.html?
fta=y.
21 http://news.yahoo.com/s/afp/20090918/sc_afp/francegermanyclimateenvironmentuneu.
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Germany22
(Policies and statements if substantially different from the European Commission)
1. Overall GHG emission target, if any, and timing:
Under the Kyoto Protocol, Germany’s share of the EU target is to reduce GHG emissions to 21%
below 1990 levels during the period 2008-2012. (Germany was able to take on such a deep target
because of its reunification with East Germany, taking on East Germany’s high emissions
baseline and reducing emissions by closing and improving many inefficient installations.)
The German government approved a new package of climate change measures in June 2008 that
are a legal transposition of the EU’s Integrated Climate Change and Energy Programme.23 The
German measures aim at a CO2 emission reduction of 40% by 2020 compared to 1990 levels. The
legislative package focuses on the transport and construction sectors.
2. Principal Policy Instrument(s): (See “EU ETS.”)
The Integrated Climate Change and Energy Programme: In 2007, the German government,
working from the general guidelines of European policy decisions, implemented a concrete
program of measures at the national level. Through 29 measures, the program addresses a wide
range of matters, including combined heat and power generation, the expansion of renewable
energies in the power sector, carbon capture and sequestration (CCS) technologies, smart
metering, clean power station technologies, the introduction of modern energy management
systems, support programs for climate protection and energy efficiency (apart from buildings),
energy efficient products, provisions on the feed-in of biogas to natural gas grids, an energy
savings ordinance, a modernization program to reduce CO2 emissions from buildings, energy
efficient modernization of social infrastructure, the Renewable Energies Heat Act program for the
energy efficient modernization of federal buildings, a carbon dioxide strategy for passenger cars,
the expansion of the bio-fuels market, reform of vehicle tax on the basis of carbon dioxide,
energy labeling of passenger cars, the reduction of emissions of fluorinated greenhouse gases,
procurement of energy efficient products and services, energy research and innovation, increased
electric mobility, international projects on climate protection and energy efficiency, reporting on
energy and climate policy by German embassies and consulates, and a transatlantic climate and
technology initiative. In June 2008, the program was enacted with a package of measures to
double electricity generated by combined heat and power technology (CHP) to 25%. The share of
renewable electricity will also be increased to 20%, especially through subsidizing off-shore wind
farm development. At the same time the package has set a target of producing half of Germany’s
electricity from renewable energy sources or super-efficient plants by 2020. The package aims for
an 11% reduction in electricity consumption by 2020.
Loans for energy efficiency and CO2 reduction measures in the domestic sector have been
available as an economic recovery measure.

22 This section was prepared by Richard K. Lattanzio, Analyst in Environmental Policy (7-1754).
23 http://www.bmu.de/english/climate/doc/39945.php.
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3. Covered Gases and Sectors: (See “European Union.”)
4. Allocation of GHG reductions to various sectors: (See “European Union.”)
5. Any regulations or exemptions specific to trade-sensitive sectors:
Germany wants to give companies in globally traded sectors bigger EU allowance quotas in the
EU ETS to soften the cost impact of Europe’s climate change policy.
Germany has been a vocal opponent of auctioning emissions allowances, although the EU has
decided to move forward with limited auctioning. As examples of Germany’s past stance, in
January 2008, Environment Minister Sigmar Gabriel critiqued the European Commission’s plan
to commence auctioning emissions permits that are currently distributed for free, stating that “The
European Union cannot ignore the question of how to preserve the international competitiveness
of industries that consume lots of energy,” such as cement, steel and chemicals, all key sectors of
the Germany economy.24 Sectors “which have reached their average for reductions of carbon
dioxide emissions must be able to obtain free emission rights to be able to remain in Europe,”
claiming that many European industries could be forced to relocate elsewhere in order to maintain
competitive prices in international markets. German Economy Minister Michael Glos has also
criticized the plan to auction emission rights.25 Gabriel also condemned the weakness of the
commission’s project in terms of developing renewable energies, which he said threatened
national support for such energies. Gabriel nonetheless reiterated German opposition to EU plans
to reduce new car emissions to 120 grams of CO2/km by 2012 without distinguishing by the class
of vehicle (German car makers produce many powerful automobiles which emit high levels of
CO2).

24 See article at http://afp.google.com/article/ALeqM5jRYO-p98IjJ1mzuQxZoS4LODTsMg.
25 See article at http://www.eubusiness.com/news-eu/1200576720.98.
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United Kingdom26
(Policies and statements if substantially different from the European Commission)
1. Overall GHG emission target, if any, and timing:
Under the Kyoto Protocol, the United Kingdom’s (UK) share of the EU target is to reduce GHG
emissions to 12.5% below 1990 levels during the period 2008-2012.
Climate Change Act of 2008 introduced a legally binding long-term target to cut emissions by at
least 80% by 2050 and at least 34% by 2020 compared to 1990 levels.27 Major provisions of the
act include the setting of legally binding targets, the establishment of a carbon budgeting system,
and the creation of a Committee on Climate Change. The carbon budgeting system establishes
caps on GHG emissions over five-year periods, with three budget periods being set at a time,
charting progress to 2050. The act also requires that the government amend the act to include
emissions from shipping and aviation by December 31, 2012. The act states that a reduction of
power sector emissions by 40% should be achievable by 2020.
Goal to reduce CO2 emissions from new houses to zero by 2016.
2. Principal Policy Instrument(s): (See “EU ETS.”)
The Carbon Budgeting System is outlined in the 2008 Climate Change Act. In it, the Secretary of
State is authorized to set an amount for the net UK carbon account (the “carbon budget”) for
successive periods of five years each (“budgetary periods”), beginning with the period 2008-
2012.
The Carbon Reduction Commitment (CRC)28 applies to non-energy intensive sectors not covered
by the EU ETS. It will apply a mandatory emissions cap and trading program to cut carbon
emissions from large commercial and public sector organizations (including supermarkets, hotel
chains, government departments, large local authority buildings using more than 6,000 megawatt
hours (MWh) of electricity through mandatory half hourly meters) by 1.1 million tons of carbon
per year by 2020. Allowances in the CRC system would be sold by auction. The revenue raised
from the sale of Carbon Reduction Commitment allowances are to be recycled back into the
scheme through bonuses and penalties meant to stimulate organizations to reduce their levels of
emissions. Any bonus or penalty administered to an organization are to be based on their ranked
position on performance in three metrics (gross emissions, growth, and early compliance
actions).29
The Carbon Emissions Reduction Target (CERT) came into effect on April 1, 2008, and will run
until 2011 as an obligation on energy suppliers to achieve targets for promoting reductions in
carbon emissions in the household sector. As reported by the Energy Savings Trust, an

26 This section was prepared by Richard K. Lattanzio, Analyst in Environmental Policy (7-1754).
27 http://www.opsi.gov.uk/acts/acts2008/ukpga_20080027_en_2#pt1-pb2-l1g4
28 For this and other policy descriptions, see the Department of Energy and Climate Change website:
http://www.decc.gov.uk/en/content/cms/publications/lc_trans_plan/lc_trans_plan.aspx
29 http://www.carbonreductioncommitment.info/carbon-reduction-commitment
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independent UK-based non-governmental organization, “it was originally estimated that CERT
would stimulate approximately £2.8 billion (US$4.7 billion)30 of investment by energy suppliers
in carbon reduction measures. In September 2008, the Government announced that the level of
funding available from the energy suppliers would be increased by £560 million” (US$893
million). The investment would increase the program’s lifetime carbon savings to 185 million
tons (Mt) CO2 (31 Mt CO2 more than under the original CERT target of 154 Mt CO2). 31
The Renewable Energy Strategy: The Department of Energy and Climate Change (DECC) details
how the UK plans to hit its target of getting 15% of energy (electricity, heat and transport) from
renewable sources by 2020. In order to achieve the target, 30% of electricity must come from
renewable energy sources, including nuclear power (a five-fold increase from today’s rate of
~5%), 12% of heat must be generated by renewables, and 10% of transport energy must be from
renewables. The main instrument to achieve these targets for renewable (and nuclear) electricity
generation are “Non-Fossil Fuel Obligations” (NFFO), begun in 1989, now Renewables
Obligations,” requiring operators of the distribution grid to purchase quotas of renewable and
nuclear electricity. The prices are subsidized by a Climate Change Levy.32
The Climate Change Levy was established in the UK under the Finance Act 2000 (2000 c:17): a
tax on most fuels, including natural gas, electricity (including nuclear) and solid fuels, but not on
vehicle or household users, nor renewable energy or cogeneration.33 Revenues are used to help
fund employment insurance, and to fund the Carbon Trust.34 In addition, energy-intensive
businesses qualify for a levy reduced by 80% if they signed voluntary Climate Change
Agreements to improve energy efficiency or reduce GHG emissions. Although the Climate
Change Levy initially was a fixed rate, the 2006 UK budget tied the rates to account for inflation
beginning in 2007.
3. Covered Gases and Sectors: (See “European Union.”)
4. Allocation of GHG reductions to various sectors
The EU ETS covers electricity generation and the main energy intensive industries—power
stations, refineries, iron and steel, cement and lime, paper, food and drink, glass, ceramics, and
engineering and vehicles. Overall, these account for around 50% of UK CO2 emissions. Non-
energy intensive, large-scale, commercial and public sectors are covered by the CRC policy
(amounting to 25% of the business sector). Household emissions are covered by the CERT
policy.35

30 Live market currency exchange rate for November 19, 2009, is listed as 1UK£ equivalent to 1.67 US$
(http://www.xe.com/). Currency rates are subject to fluctuation.
31 http://www.energysavingtrust.org.uk/Global-Data/Funding-Information/Carbon-Emissions-Reduction-Target-CERT.
32 http://www.publications.parliament.uk/pa/cm200708/cmselect/cmenvaud/590/59003.htm.
33 The Climate Change Levy revised and replaced a fossil fuel levy.
34 Maria Pender, “UK Climate Change Programme: Business and Public Sector Economic Agreements.”
35 http://www.berr.gov.uk/energy/environment/euets/index.html.
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5. Any regulations or exemptions specific to trade-sensitive sectors:
The UK’s “Low Carbon Industrial Strategy” states a vision that the nation “must create the
conditions for the UK to be—and be recognised as—the leading location in the world for growing
an innovative low carbon business and developing new low carbon products and services.”36 The
UK strategy appears oriented toward supporting identified opportunities in “green” businesses
and technologies, aiding them through:
• a Low Carbon Investment Fund, (with financing of £405 million—US$674
million);
• a business-led Technology Strategy Board;
• an Energy Technologies Institute (ETI), serving as a private/public partnership to
invest in development of low carbon energy technologies;
• R&D tax credits;
• a Carbon Trust to support development and deployment of new and emerging
low carbon technologies; and
• a UK “innovation infrastructure,” including intellectual property systems and
procedures, standards, and a National Measurement System.

36 DECC, Investing in a Low Carbon Britain, available at http://interactive.bis.gov.uk/lowcarbon/vision/.
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Australia37
1. Overall GHG emission target, if any, and timing:
Under the Kyoto Protocol, Australia accepted a target to limit its net GHG emission increase to
8% above 1990 levels. It has also proposed that, under a new international agreement, it would
take on a target to reduce its GHG emissions by 5% to 25% below 2000 levels by 2020, with the
more stringent commitment conditioned on whether “the world agrees to an ambitious global deal
to stabilise levels of CO2 equivalent in the atmosphere at 450 parts per million (ppm) or lower.”38
2. Principal Policy Instrument(s):
The Australian government proposed a Carbon Pollution Reduction Scheme (CPRS) to be phased
in beginning July 1, 2011. A one-year period would occur from 2011-12, during which carbon
emission permits would be sold at a fixed price Aus$10 per ton of carbon (US$9.20);39 these may
not be banked for use in later periods. The full cap-and-trade system would be in effect by 2012,
by which time all covered businesses must purchase carbon permits at market prices. The Senate
did not pass this proposal on its first or second readings in August and December 2009. Despite
addition of several exemptions and aid to selected industries, strong political opposition
(including the ousting of the Senate’s opposition leader who negotiated the compromise
provisions) in the Senate blocked passage of the measure. The Rudd Government has said it will
maintain its overall GHG goal of 25% below 2000 levels and will resubmit the proposal to the
Parliament again in February 2010. It has also indicated that, if the CPRS does not pass in
February, it will lead to “double dissolution” of the Parliament and a snap election, expected to
result in increased representation by Rudd’s allies.
The Australian program includes a Renewable Energy Target, and investment in carbon capture
and storage. Up to 5 percentage points of its offered 25% target for 2020 could be met by
purchase of international emission reduction credits using CPRS revenue, though no earlier than
2015. Eligible businesses also may receive government funding for energy efficiency
investments, available from a Aus$200 million (US$184 million) portion of a Climate Change
Action Fund.
In August, though the Australian Senate did not pass the carbon reduction proposal, it passed the
Renewable Energy Target (RET) into law40 that establishes a system of tradable Renewable
Energy Certificates (RECs). It requires that 20% of electricity come from renewable resources by
2020 (projected to require 45 gigawatt hours (GWh)). Currently, about 8% of Australia’s
electricity is generated with renewables. Among other provisions, the law provides Solar Credits,
allowing receipt of a multiple of 2-5 of RECs for qualified installations, that will subsidize the
capital costs of small-scale systems, such as household photovoltaic systems. The grants of RECs

37 This section was prepared by Jane A. Leggett, Specialist in Environmental and Energy Policy (7-9525).
38 http://www.environment.gov.au/minister/wong/2009/mr20090504.html.
39 Live market currency exchange rate for November 19, 2009, is listed as 1Aus$ equivalent to 0.92 US$
(http://www.xe.com/). Currency rates are subject to fluctuation.
40 Renewable Energy (Electricity) Amendment Act 2009, No. 78, 2009, C2009A00078; and Renewable Energy
(Electricity) (Charge) Amendment Act 2009, No. 79, 2009, C2009A00079. http://www.comlaw.gov.au/comlaw/
Legislation/Act1.nsf/0/94CB90B9EED48B69CA25762D001B6F5F?OpenDocument.
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will depend on the generation of energy, not the installed capacity (which, in some countries, has
not stimulated maximizing the use of installed capacity).
3. Covered Gases and Sectors:
As proposed, the CPRS would initially cover the six GHG of the Kyoto Protocol, and emissions
from stationary energy, transport, industrial processes, waste, forestry, and fugitive emissions
from oil and gas production.41 It is expected to cover 75% of Australia’s GHG emissions and
about 1000 entities (out of 7.6 million registered businesses in Australia).42 Agriculture was
exempted in order to secure passage of the bill.
4. Allocation of GHG reductions to various sectors:
Permits would be available in 2011 at a fixed price of Aus$10 per ton of carbon-equivalent
(US$8.60), after which all covered sources must purchase their permits through auction or the
market.
5. Any regulations or exemptions specific to trade-sensitive sectors:
News reports indicate that the Rudd Government’s legislative proposal has been modified to gain
legislative support for the measure, by exempting agriculture from the system, and increasing
financial incentives to electric power generators, coal mines, and food processors.43 The proposed
CPRS includes provisions to assist emissions-intensive, trade-exposed industries (EITE).
Eligibility for assistance would be determined by an assessment of all entities conducting a
specific activity. First, there would be quantitative and qualitative tests to assess the activity’s
trade exposure. Second, there would be assessments of greenhouse gas intensity based on the
average emissions per million dollars of revenue or emissions per million dollars of value added.
The baseline for the emission data would be 2006-2007 to 2007-2008, while the baseline for
revenue/value added data would be 2004-2005 to the first half of 2008-2009.
The government allocates free permits using an allocation baseline of emissions per unit of output
for each EITE activity. This baseline will provide the basis for eligibility at either the 90% or 60%
assistance rates. The proposal44 would set up two initial rates of assistance: (1) 90% allocation of
allowances for activity with emissions intensity of at least 2,000 tons of emissions per million
dollars revenue or 6,000 tons of emissions per million dollars of value added; (2) 60% allocation
of allowances for activity with emissions intensity between 1,000 tons of emissions per million
dollars revenue and 1,999 tons of emissions per million dollars revenue or between 3,000 tons
and 5,999 tons of emissions per million dollars of value-added. This assistance per unit of
production will be reduced by 1.3% annually.
The proposed CPRS would include a five-year Global Recession Buffer as part of an assistance
package to EITE. Industries eligible for 60% assistance would receive a “buffer” of 10% free

41 Australian Government, Carbon Pollution Reduction Scheme: Australia’s Low Pollution Future: White Paper
(December 2008).
42 http://www.climatechange.gov.au/whitepaper/summary/index.html.
43 Reuters, “UPDATE 1-Australia Govt Secures Carbon Deal with Opposition,” November 24, 2009,
http://in.reuters.com/articlePrint?articleId=INSYD51352320091123.
44 http://www.environment.gov.au/minister/wong/2009/mr20090504a.html.
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emission permits; industries eligible for 90% assistance would receive a 5% buffer of free
emission permits.
Reviews of the EITE scheme would occur every five years, and would consider a list of identified
issues, including whether the assisted firms are making progress toward world’s best practice
efficiencies, and whether “broadly comparable carbon constraints” are imposed in competing
economies. Any changes to the system would require five years’ advance notice.
The scope of consideration for assistance includes (1) direct emissions covered, (2) related cost
increases for electricity and steam use, and (3) related cost increases for upstream emissions from
natural gas and its components (e.g., methane and ethane) used as feedstock. The assistance
package would include direct emissions and some indirect emissions.
Two amendment bills to the Renewable Energy (Electricity) Act 2000 were passed on August 20,
2009, and received Royal Assent on September 8, 2009. The Renewable Energy Amendments
contain provisions to assist electricity-intensive industries and the coal industry. Under these
provisions, one or more emissions-intensive trade-exposed activities may be partially exempted
from its REC requirements. If resulting Partial Exemption Certificates are taken into account, it
would reduce the charge for falling short of RECs that would otherwise be payable.45 In this law,
the definition of “emissions-intensive trade-exposed activity” would be either defined by further
regulations, or by regulations under a Carbon Pollution Reduction Scheme Act 2009 if passed.
The methods for calculating the amounts of partial exemptions would be defined by regulations.

45 Renewable Energy (Electricity) Amendment Act 2009, Schedule 2.
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Brazil46
1. Overall GHG emission target, if any, and timing:
In November 2009, Dilma Rousseff, chief of staff for Brazilian President Luiz Inácio Lula da
Silva, was reported as saying that her country would take a proposal for voluntary GHG
emissions reductions of 36%-39% by 2020 to the Copenhagen summit.47 Brazil’s emissions
would drop to near 1994 levels if the top end of the pledge is met, representing about a 20% cut
from the 2.1 million tons emitted in 2005. The emission cuts would be based largely on reducing
deforestation rates, and would depend in large part on obtaining “sufficient” financing. President
Lula stated in December 2008 that Brazil would slow its rate of deforestation in the state of
Amazonas by 70% by 2017, compared to the average rate from 1996 to 2005. In September 2009,
the Brazilian government extended this target to an 80% reduction by 2020.48 Brazil has set a
target by 2010 for zero deforestation in its Atlantic Forest.
On December 28, 2009, President Lula signed into law the 39% reduction in emissions by 2020,
meeting the commitment made at the Copenhagen climate conference. The new law, however, is
subject to several decrees setting out responsibilities and regulations for the farming, industrial,
energy, and environmental sectors, and omits several vetoed provisions, including a reference to
“promoting the development of clean energy sources and the gradual phasing out of energy from
fossil fuels.” President Lula is expected to sign the decrees in January after consulting scientists
and other experts.49
2. Principal Policy Instrument(s):
In December 2008, Brazilian President Luiz Inácio Lula da Silva signed the National Climate
Change Plan (PNMC) into effect.50 Policy measures include:
• Stimulating energy efficiency through best practice, including the
implementation of an energy efficiency policy that targets a savings of 106
terawatt hours per year (TWh/y) by 2030; the substitution of renewable charcoal
for coal in manufacturing sectors; the replacement of one million old
refrigerators per year for 10 years; the deployment of solar power systems for
water heating; and the phasing out of the use of fire for the clearing and cutting
of sugarcane.
• Retaining a high renewable energy share in the electricity sector, including the
increase of the total electricity supply from cogeneration, mainly from sugarcane
bagasse, to 11.4% by 2030; the reduction of non-technical losses in electricity

46 This section was prepared by Richard K. Lattanzio, Analyst in Environmental Policy (7-1754).
47 See http://www.reuters.com/article/marketsNews/idUSN1347815120091113.
48 According to Brazil’s National Institute of Space Research (INPE), Brazil’s average rate of deforestation from 1996
to 2005 was 7,542 square miles annually, compared to averages of 6,574 annually from 1988 to 1995, and 4,974 from
2006 to 2008; http://www.mongabay.com/brazil.html. This target does not appear to include forests, including open
canopy forests, in other parts of Brazil, which may be cleared for agricultural production. Also, http://en.cop15.dk/
news/view+news?newsid=2351, http://www.cmcc.it:8008/cmcc/blog-en/brazil-sets-new-deforestation-target.
49 http://www.grist.org/article/2009-12-30-brazils-lula-signs-law-cutting-co2-emissions.
50 http://www.mma.gov.br/estruturas/208/_arquivos/national_plan_208.pdf.
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distribution at a rate of 1,000 GWh/y over the next 10 years; the addition of
34,460 MW capacity from new hydropower plants over the next 10 years; the
increase in electrical supply share from wind and sugarcane bagasse by 7,000
MW by 2010; and the expansion of the national solar photovoltaic industry and
its deployment in systems isolated from the grid.
• Increasing the share of bio-fuels in transport matrix, including the attempt to
encourage industry to achieve an annual substitution rate of 11% bio-fuels for
fossil sources over the next 10 years; and the institution of a 5% bio-fuel to diesel
mandate by 2010;
• Reducing deforestation rates and eliminating forest losses, increasing policing
against illegal logging and curtailing financing to illegal ranching.
• Continuing the policy measures of prior renewable energy regulations including
the 2004 Program of Incentives for Alternative Electricity Sources (PROFINA),
coordinated by the Ministry of Mining and Energy and Centrais Elétricas
Brasileiras (Eletrobras). The program contains new strategies for the
incorporation of renewable resources in Brazil’s energy matrix and strengthens
the country’s policy on diversification and development. On its inception,
PROFINA contracted 144 generation stations to benefit 19 states with a
combined capacity of 3,300 MW from wind, biomass, and small hydro sources
for a potential GHG reduction of 2.8 Mt CO2/year.
Many of Brazil’s mitigation strategies involve the reduction of deforestation rates in the Amazon.
The current administration has expanded protected areas in the Amazon and implemented new
environmental policies. More than 62 natural reserves have been established in the Amazon,
bringing the total area of the Brazilian Amazon protected by law to 280,000 square kilometers,
the fourth-largest percentage of protected area in relation to territory among all countries. In
addition to the aforementioned National Climate Change Plan, Brazil has enacted other laws that
address deforestation and sustainable development.
• The Public Forest Management Law encourages sustainable development, places
a moratorium on soybean plantings and cattle ranching in the Amazon, and
authorizes the creation of a plan to reduce the rate of Amazon deforestation by
half. Brazil plans to meet this goal by increasing federal patrols of forested areas,
replanting 21,000 square miles of forest, and financing sustainable development
projects in areas where the local economy depends on logging.
• The Action Plan for the Prevention and Control of Amazon Deforestation intends
to improve the monitoring of the deforestation process, from a regional to a local
scale; promotes the presence of public authorities in critical zones; confronts the
economic speculation problem involved in public lands; plans the appropriate
distribution of public lands according to social and ecological needs; and retains
commercial wood exploration while also promoting sustainable forest
management.
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• The Amazon Fund (a private fund) aims to combat deforestation and to promote
sustainable development in the Amazon. In 2008, Norway pledged $1 billion to
the fund through 2015, making it the first country to do so, stating that it would
donate as much as $130 million in 2009.51
The Brazilian government maintains that these efforts have been successful. It has recently been
reported that deforestation of the Amazon fell by the largest amount in more than 20 years,
dropping 45%, from nearly 5,000 square miles to some 2,700 square miles, in 2008, although
there normally is a great deal of year-to-year variability in deforestation rates.52 A continued
emphasis on enforcement coincides with legislation. The enactment of the Prevention of the Use
of Illegal Timber in the Building Industry Act, starting January 2009, asks for proof of the legal
origin of timber from building companies. As such, the government recovered 1.4 million cubic
meters of illegal wood and 700 people were put in prison.53
Observers note, however, that other factors contribute to the rate of deforestation beyond
governmental policy measures. Brazilian deforestation is strongly correlated to the economic
health of the country. Recent reductions are concurrent with the global economic downturn.
Falling commodity prices have stalled the expansion of ranching and agriculture into the Amazon.
While these trends have seemed favorable for emission reductions, some commentators still point
to what they consider continued deforestation practices by commercial and speculative interests,
misguided government policies, inappropriate World Bank projects, and commercial exploitation
of forest resources. Others see favorable taxation policies, combined with government subsidized
agriculture and colonization programs, as a continued encouragement for the destruction of the
Amazon. Still others emphasize the inherent difficulty in measuring, reporting and verifying any
GHG emission reductions in the Land Use, Land Use Change and Forestry (LULUCF) sector.
Finally, most stress the crucial commitment to local law enforcement policies to sustain any
regulatory reform that comes out of the federal government.
3. Covered Gases and Sectors:
Primarily CO2 in deforestation and other domestic agendas; however, U.N. Clean Development
Mechanism projects in Brazil include CH4 and N2O reductions.
4. Allocation of GHG reductions to various sectors:
Unlike other developed or developing countries, Brazil holds a unique endowment of natural
resources that affects its climate change portfolio in the power generation and transportation fuel
sectors. A low contribution of greenhouse gas emissions has been due to both market-driven and
governmental decisions to adopt renewable energy sources over the past few decades. The
markets for both hydroelectricity and sugarcane products (bagasse for thermal purposes and
ethanol for transportation fuel) have expanded 10-fold. During this period there was also an
important decrease in wood consumption in the residential and industrial sectors and an increase
in charcoal consumption in the industrial sector.

51 Brazil received $100 million of the pledge on March 25, 2009. The remainder is pending. See
http://inter.bndes.gov.br/english/news/not036_09.asp.
52 See http://www.eenews.net/Greenwire/2009/11/13/4.
53 http://www.redd-monitor.org/2009/01/23/brazils-national-plan-on-climate-change-and-the-amazon-fund-
%E2%80%9Cthis-plan-does-not-create-any-carbon-credits-or-right-to-emissions%E2%80%9D/.
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Taken together, however, the sectors of energy, industrial processes, solvents and waste treatment
contribute only 25% of total GHG emissions, estimated at approximately 1 billion tons. The rest
of Brazilian GHG emissions is tied to the LULUCF sector, and of that total, 90% corresponds to
the conversion of forests to other uses, especially agriculture and ranching. For this reason, most
of Brazil’s mitigation policies have concentrated on the forestry sector.
5. Any regulations or exemptions specific to trade-sensitive sectors:
Not specified.
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Canada54
1. Overall GHG emission target, if any:
In April 2007, then-Environment Minister John Baird announced that by 2020, Canada would
reduce its GHG emissions by 150 million tons, or 20%, from its 2006 level. Beyond this, the
government hopes to achieve a 60%-70% reduction by 2050.55 The Kyoto emission reduction
targets are scored from 1990 (with a few explicit exceptions); some analysts assert that, since
Canada’s GHG emissions rose 27% between 1990 and 2004, the government would be able to
demonstrate far greater progress if it were able to use 2006 as its base year in the Copenhagen
Agreement.56
2. Principal Policy Instrument(s):
The government’s most recent plan for regulating industrial air emissions was announced in
March 2008.57 However, observers note that it remains indefinite. Canada’s current Environment
Minister, Jim Prentice, is traveling around the country’s 10 provinces soliciting ideas on a cap-
and-trade system. There has reportedly been a great deal of pressure on the Minister to develop a
plan that will be compatible with whatever may be developed in the United States. For example,
the original 2007 Canadian plan called for an “intensity target” rather than a cap. Bilateral
discussions over a compatible cap-and-trade system are underway.58 The effort at cross-border
harmonization is likely due to the extensive economic integration between the two countries.
The government aims to complete its policy formulation and present its formal plan before the
December 2009 United Nations climate change Conference of the Parties in Copenhagen. Some
observers note that the government’s ambitions might be delayed or curtailed if a snap election is
called; however the prospect of such a vote is believed to be increasingly unlikely.59
Recognizing that the transportation sector is responsible for about 27% of GHG emissions, the
Canadian government is also set to issue mandatory auto emissions regulations—essentially
converting fuel efficiency into CO2 limits—and likely will seek to make its standards compatible
with those set by the U.S. Environmental Protection Agency. The Environment Ministry may also
issue modified regulations regarding usage of ethanol. These changes would be facilitated by
amendments to the Canadian Environmental Protection Act of 1999, which, among other things,

54 This section was prepared by Carl Ek, Specialist in International Relations (7-7286).
55 Canada’s New Government Announces Mandatory Industrial Targets to Tackle Climate Change and Reduce Air
Pollution. News release. Environment Canada website. April 27, 2007. http://www.ec.gc.ca/default.asp?lang=En&n=
714D9AAE-1&news=4F2292E9-3EFF-48D3-A7E4-CEFA05D70C21.
56 No Clear Environmental Champion; Canada and the United States Have Shown Varied Levels of Aggressiveness in
the Fight to Combat Climate Change. Globe and Mail. July 9, 2008. See also: Canada’s Greenhouse Emissions Soaring
Again: UN Report. Canwest News Service. April 21, 2009.
57 Government Delivers Details of Greenhouse Gas Regulatory Framework. News release. Environment Canada
website. March 10, 2008. http://www.ec.gc.ca/default.asp?lang=En&n=714D9AAE-1&news=B2B42466-B768-424C-
9A5B-6D59C2AE1C36.
58 Notes for an address by the Honourable Jim Prentice, P.C., Q.C., M.P. Minister of the Environment on Canada’s
climate change plan. Speech. Environment Canada website. June 4, 2009. http://www.ec.gc.ca/default.asp?lang=En&
n=6F2DE1CA-1&news=400A4566-DA85-4A0C-B9F4-BABE2DF555C7.
59 CRS discussion with Canadian government official, September 10, 2009.
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can be used to regulate tailpipe emissions and ethanol blending. Regulations have yet to be
published; the ministry likely will attempt to match and harmonize its emissions standards on a
continental basis.
The federal government can also use its spending power to control pollution. The government has
created a climate change “ecoTrust” fund from which the provinces may draw in order to pay for
programs to reduce their own GHG emissions. The last two federal budgets have also included
significant funding for carbon capture and storage, including a large-scale demonstration facility.
This could be one important aspect of the attempt to reduce emissions arising from some
provinces’ extensive use of coal as an energy source; it also could be used for oil sands.
3. Covered Gases and Sectors:
Although the details are still being negotiated, Canada’s regulations will likely cover the six gases
included in the Kyoto Protocol. In reducing GHG emissions in Canada, the government will
likely also attempt to co-reduce other pollutants such as sulfur dioxide, particulate matter, and
mercury. Specific sectors have yet to be determined.
4. Allocation of GHG reductions to various sectors:
The government has not yet determined the sectoral allocation of reductions, but it has calculated
that 35% of Canada’s GHG emissions arise from fossil fuel production, industrial processing and
manufacturing; 22% from services, residential, waste and agriculture; 16% from electricity and
heat generation; and 27% from transportation.60
5. Any regulations or exemptions specific to trade-sensitive sectors:
Canadian government officials maintain that exemptions—if any—and regulations are yet to
come, and that Environment Minister Prentice is still attempting to strike agreements with the
various provinces.

60 Notes For an Address by the Honourable Jim Prentice, P.C., Q.C., M.P. Minister of the Environment on New
Regulations To Limit Greenhouse Gas Emissions. Speech. Environment Canada website. April 1, 2009.
http://www.ec.gc.ca/default.asp?lang=En&n=6F2DE1CA-1&news=D8C4903B-B406-4B70-8A4A-EDEF99B71D38.
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China61
1. Overall GHG emission target, if any, and timing:
The 11th Five-Year Plan set compulsory energy and pollution targets for 2006-2010 that have
slowed growth of GHG emissions, and those energy targets appear likely to be reached or
surpassed by 2010. However, as China publishes neither its GHG emissions nor the effects of
policies on GHG trajectories, validating reports of progress is not possible. Chinese Premier Wen
Jiabao in November 2009 stated a national target to reduce GHG emissions by reducing carbon
intensity (emissions per unit of economic output) by 40%-45% by 2020 compared with 2005
levels.62 The State Council indicated that this carbon-intensity target will be made a “binding
goal” in China’s 12th Five-Year Plan, from 2011-2015, and long-term national social and
economic development plans.
One Chinese researcher has estimated that, if these Chinese economy doubles by 2020, the 40%-
45% target would hold GHG to approximately today’s emissions level.63 The Chinese climate
change website suggests that Chinese leaders are “mulling” GHG goals of improvement of
carbon intensity of 4%-5% annually over several decades, which could lead to an 85%-90%
reduction of carbon intensity by 2050 compared to the 2005 rate.64 (A percentage improvement
expressed as carbon intensity would be easier to achieve than the same percentage target
expressed as energy intensity, so this rate of annual improvement would be less than the annual
energy intensity improvement target in the current five-year plan.)
2. Principal Policy Instrument(s):
Edicts specify national, provincial, and plant-specific targets or actions. For example, one
national goal is to reduce energy consumption per unit of GDP by 20% from 2006-2010. Each
province was given a corresponding target in June 2006, and many local governments were
assigned energy conservation targets by the National Development and Reform Commission
(NDRC) in July 2006. Some of the key instruments the central government is using to meet its
targets for 2010 include:
• reducing or eliminating incentives for energy-intensive exports (e.g., export tax
rebates);
• implementing a program of “Large Substitute for Small,” closing half of small,
inefficient electric power plants by 2010, and banning new small plants;
• removing some subsidies from inefficient or polluting plants;

61 This section was prepared by Jane A. Leggett, Specialist in Environmental and Energy Policy (7-9525).
62 Xinhuanet, “China Announces Targets on Carbon Dioxide Emission Cuts,” November 26, 2009,
http://www.ccchina.gov.cn/en/NewsInfo.asp?NewsId=20831.
63 Xinhuanet, ibid.
64 http://www.ccchina.gov.cn/en/NewsInfo.asp?NewsId=20325. This article also points to a study indicating that an
83% reduction of carbon intensity by 2050 would cost about 2.3% of GDP, while a 90% reduction of carbon intensity
would cost about 7% of GDP. It is unclear whether this is a lost compared to the annual rate of GDP growth, or to
cumulative GDP growth in 2050.
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• setting 2010 energy consumption targets within the Top-1000 Enterprise Program
for each large enterprise (in total representing 33% of national energy use in
2004);
• requiring closure of small and inefficient industrial plants, sometimes with
compensatory payments;
• setting electricity dispatch rules to favor low-carbon generation, such as feed-in
tariffs for renewably produced electricity that can reach 25%-50% higher than
coal-based electricity prices;
• providing large subsidies to help finance some large capital investments in
efficient or low-emitting technologies;
• allowing energy prices to rise to international price levels in many cases, and
imposing (and reportedly beginning to collect) pollution fees;
• setting new vehicle efficiency standards at the Europe-IV level (tighter than
U.S.), and making payments to turn in and destroy older, polluting vehicles (like
“cash for clunkers”);
• raising investments in inter-city and intra-city rail; and
• tightening building efficiency codes by many municipalities, although
enforcement may be spotty.
High-level officials have indicated that the 12th Five-Year Plan will embody the -40% to -45%
carbon-intensity targets, and that several national laws will be amended in the near-term to
achieve GHG reductions. Carbon cap-and-trade “pilot” projects will be initiated in “some
designated areas and industries.”65 President Hu has summarized additional targets that likely
would help to restrain expected growth of GHG: a target to increase non-fossil fuel share of
primary energy consumption to 15% by 2020, and to increase forest coverage by 40 million
hectares and forest stock volume by 1.3 billion cubic meters by 2020 from 2005 levels. China
also requires strict fuel efficiency standards for vehicles.
Some have argued that China’s policies may be undermined by incomplete implementation, due
to sometimes vague statement of requirements, lack of enforcement resources, poor data,
conflicting priorities at the local level, and other factors. Though some argue that reporting and
enforcement of the targets and regulations have been irregular, there are indications that the
central government is working to improve such weaknesses, and to impose career penalties on
officials who do not meet their targets.66 The State Council stated in November 2009 that new
measures would be developed for auditing, monitoring, and assessing implementation of the
GHG plans. Others are cautious about the central government’s will and ability to gain full
implementation of national policies at the provincial and local levels.

65 Jing Li and Zhe Zhu, “Legislature Takes Urgent Action in Climate Change Fight,” China Daily, August 28, 2009,
http://www.chinadaily.com.cn/china/2009-08/28/content_8626140.htm.
66 See, for example, http://news.xinhuanet.com/english/2007-06/20/content_6269732.htm; http://www.chinacsr.com/en/
2009/06/18/5487-china-first-heavy-industries-fined-for-infringement-of-environmental-rules/; http://www.china.org.cn/
environment/2009-09/28/content_18619189.htm; and http://www.china.org.cn/government/news/2008-03/12/
content_12338958.htm.
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3. Covered Gases and Sectors:
Policies are mostly focused on energy reforms not GHG control, though they also reduce CO2 and
methane emissions. Some projects under the Kyoto Protocol’s Clean Development Mechanism
address many industrial gases (such as hydrofluorocarbons) as well. Sectors addressed include
energy, vehicle manufacturing, building, energy-intensive industries, forestry, etc. Agriculture
seems engaged only through development of bio-fuels.
4. Allocation of GHG reductions to various sectors:
Many sectors are covered through various programs. Targets and actions are set by enterprise, not
industry-wide.
5. Any regulations or exemptions specific to trade-sensitive sectors:
Many Chinese industry-specific policies seem aimed at eliminating the most energy-intensive and
inefficient facilities within a sector. Many of China’s exporting firms perform close to or at
international energy-intensities. In 2007, China removed or reduced export tax rebates for many
types of export products, including for energy-intensive, trade-sensitive industries. These
adjustments generally have the effect of reducing incentives to export. Examples of additional
programs are provided below.
Iron and Steel: The Chinese government has been emphasizing restructuring and improving the
overall production efficiency of the iron and steel industry, much of which is likely also to reduce
direct and indirect emissions. Closures are mandated in 2006-2010 of 100 million tons of iron
production capacity and 55 million tons of steel capacity using inefficient and old technologies.67
From 2006-2008, 61 million tons of iron and 43 million tons of steel capacity were closed,
according to government statistics.68 Mergers and acquisitions are being encouraged to increase
concentration and efficiency in the industry. The adjustment and revitalization plan also envisions
shifting the product composition of the sector’s production, as well as shifting to integrated
capacity.
Aluminum: Chinese requirements for energy savings and emissions reductions in its aluminum
industry have been estimated to achieve its target of reducing GHG from the industry by 25% by
the end of 2010.69 The central government mandated closures of inefficient aluminum smelting
capacity in 2006-2010. China’s Ministry of Finance announced it would levy a 15% export tariff
on non-alloy aluminum rods and poles, and eliminate the 5% import duty on electrolytic
aluminum and many other energy-intensive commodities, in order to “further restrict exports of
high energy-consuming and polluting resources products and encourage imports of raw
materials,” as well as to suppress China’s trade surplus.70
The Chinese government has removed preferential electricity rates for metal producers, so
manufacturers now pay market prices. The (U.S.-based) Aluminum Association also notes,

67 http://www.reportbuyer.com/industry_manufacturing/metals/steel/pollution_report_china_steel_industry.html.
68 http://news.xinhuanet.com/english/2009-08/25/content_11942981_1.htm.
69 Feng Gao et al., “Greenhouse gas emissions and reduction potential of primary aluminum production in China,”
Science in China Series E: Technological Sciences 52, no. 8 (2009): 2161-2166, doi:10.1007/s11431-009-0165-6.
70 http://experts.e-to-china.com/analysis/general_analysis/Taxation/2009/0728/58804.html.
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“Additionally, China has invested in alternative energy systems that will begin paying off in
2009, namely solar and hydroelectric power, which will reduce the cost of energy.”71 This is
likely also to reduce associated GHG emissions.
Cement: China set a target to reduce energy intensity in its cement industry by 20% in the 11th
Five-Year Plan (2006-2010), using plant closures and installing state-of-the-art technologies.
China’s cement production is about 50% of the global total. The central government mandated
closures of inefficient cement production capacity in 2006-2010, with closures of about 140
million tons of production capacity achieved from 2006-2008.72 One program is set to “design an
economically viable, environmentally friendly alternative fuel and raw materials co-processing
program, which will include conducting demonstrations in six Chinese plants, and developing,
documenting, and disseminating technical guidelines for co-processing.... [T]ools, training
materials, and results from the project will be disseminated to further enhance the capacity
building of the entire Chinese cement industry. An integrated national database on energy
efficiency and emissions for Chinese cement industry, using worldwide recognized
methodologies and tools, will also be established.”73
Motor Vehicles: New vehicle efficiency standards have been set at the Europe-IV level (stricter
than US standards). National policy and investment promotes rail rather than road transport.
China has enacted its version of the “Cash for Clunkers” program: from Aug 1, 2009, to June 30,
2010, consumers may receive 3,000-6,000 Yuan (US$440-875)74 per vehicle to replace “yellow
tag” passenger cars, vans, and trucks that exceed emission standards, or are 8-12 years old.
Previous changes in vehicle taxes, with higher rates for large cars and lower rates for small ones,
resulted in increased small car sales in 2008.
The total trade-in subsidy, mainly targeting light commercial vehicles, is likely to cost the
government around 5 billion Yuan.

71 http://www.aluminum.org/AM/Template.cfm?Section=Home&CONTENTID=27780&TEMPLATE=/CM/
ContentDisplay.cfm.
72 http://news.xinhuanet.com/english/2009-08/25/content_11942981_1.htm.
73 http://china.lbl.gov/news/chinese-cement-companies-reduce-their-carbon-footprint.
74 Live market currency exchange rate for November 19, 2009, is listed as 1 CNY = 0.146 US$ (http://www.xe.com/).
Currency rates are subject to fluctuation.
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India75
1. Overall GHG emission target, if any, and timing:
The Minister of State for Environment and Forests, Jairam Ramesh, announced on December 3,
2009, that India will reduce its GHG emissions intensity (emissions per unit of GDP) by 20%-
25% by 2020, compared to the 2005 level.76 (He reportedly said that India’s carbon intensity
decreased by 17.6% from 1990 to 2002.) Ramesh also committed to India’s Parliament that India
would accept neither legally binding targets nor peaking dates77 internationally.78,79 Earlier, the
government also pledged that 20% of India’s energy would come from renewable resources by
2020, and 15% of India’s annual GHG emissions would be taken up by forests by 203080 (up
from about 11% in 200581). The Indian government has pledged that its emissions per capita
would always remain below those of the now-industrialized countries (though expected
population increases are substantial).
2. Principal Policy Instrument(s):
Ramesh has indicated that the national Planning Commission has agreed that India’s 12th Five
Year Plan, from 2012-2017, will include a low-carbon growth strategy. He identified five
categories of measures:82
• mandatory fuel efficiency standards for all vehicles by December 2011;
• national building code guidance for energy efficiency, to recommend to local
governments to make mandatory;
• amendments to laws to reduce energy intensity of industrial activities;
• forest monitoring; and
• use of advanced technologies (super critical, ultra super critical, and coal
gasification) for half of all new coal-fired power plants.
In actions to date, India’s national government has relied almost exclusively on public
information, training of energy auditors, voluntary “declarations” of energy management policies

75 This section was prepared by Jane A. Leggett, Specialist in Environmental and Energy Policy (7-9525).
76 “India’s 2020 Target: Reduce Emission by 20-25%,” The Times of India, December 3, 2009, online edition,
http://timesofindia.indiatimes.com/india/Indias-2020-target-Reduce-emission-by-20-25/articleshow/5297073.cms.
77 A date by which its national emissions would peak and then begin to decline in absolute terms. Some proposals have
advocated peaking dates for developing countries of between 2015 and 2030.
78 T.K. Arun, “For a Binding Climate Target,” The Economic Times (India), December 4, 2009, sec. Op-Ed,
http://economictimes.indiatimes.com/opinion/columnists/t-k-arun/For-a-binding-climate-target/articleshow/
5298331.cms.
79 In the same speech to Parliament, Ramesh stated that India would not allow international review of GHG reduction
actions it takes without international financing, though the government “can consider” international review of actions
that are supported by international finance.
80 http://www.forbes.com/2009/09/23/jairam-ramesh-india-business-energy-climate-change.html.
81 http://www.thaindian.com/newsportal/india-news/indian-forests-absorb-11-of-annual-greenhouse-gas-emissions-
jairam-ramesh_100240011.html.
82 Times of India, December 3, 2009, op. cit.
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by businesses, and small financial awards as its principal instruments to promote energy
efficiency. In concept, Ramesh has said that India might enact a law directing the government to
set climate-related, but non-mandatory, targets, with reporting to and review by the Parliament.
He has indicated that the new law may be similar to the Fiscal Responsibility and Budget
Management law (FRBM), which directs the government to develop targets, and requires
reporting to the Parliament, as well as Parliamentary approval. The targets in the FRBM are
neither specified nor binding.
Prime Minister Manmohan Singh approved in August 2009 a national energy efficiency plan that
would require 714 energy-intensive industrial facilities in nine sectors, accounting for 40% of
India’s fossil fuel use, to meet energy efficiency targets. The energy efficiency plan is estimated
by 2015 to avoid about 5% of India’s projected fossil fuel use. The Prime Minister’s Office may
be contemplating setting up a new National Climate Change Mitigation Authority under the
Prime Minister’s authority.
Reportedly, the government has initiated greenhouse gas abatement plans in the past several
months, including reforestation. An existing voluntary set of efficiency standards is expected to
become mandatory by 2010. Stronger standards may be set for energy efficiency for certain
appliances and government buildings; an Energy Conservation Building Code (ECBC) for all
new government buildings; and monitoring of afforestation. Prime Minister Singh announced in
late August the intention of introducing an energy efficiency trading system to reduce India’s
energy consumption by 5% and its CO2 emissions by 100 million tons annually from projected
levels by 2015 (about 8% of current emissions).83 Two funds would be created with about $60
million of funding to provide partial loan guarantees and venture capital. Proposed targets may be
set by December 2010.
In 2008, the Prime Minister released a National Action Plan on Climate Change, containing eight
“national missions”: the National Solar Mission; National Mission for Enhanced Energy
Efficiency; National Mission on Sustainable Habitat; National Water Mission; National Mission
for Sustaining the Himalayan Ecosystem; National Mission for a Green India; National Mission
for Sustainable Agriculture; and National Mission on Strategic Knowledge for Climate Change.84
The most concrete measures aimed at increasing solar energy capacity. In November 2009, the
Indian Union Cabinet approved a Jawaharlal Nehru National Solar Mission (NSM) to increase
India’s solar electric capacity from 5 megawatts (MW) to 20 gigawatts (GW) by 2022 (slipping
back two years from the initial target date), at a cost of $19 billion.85 Some $900 million has been
approved for the initial phase, to install 1.1 GW of on-grid and 0.2 GW of off-grid solar capacity
by 2012. The NSM will offer financial incentives to investors, including tax breaks, and will
boost research. Several existing laws support renewable energy development, according to a
report from the Pew Center.
The Electricity Act (2003) encourages the development of renewable energy by mandating
that State Electricity Regulatory Commissions (SERCs) allow connectivity and sale of
electricity to any interested person and permit off-grid systems for rural areas. The National
Tariff Policy (2006) stipulates that SERCs must purchase a minimum percentage of power

83 See, for example, http://in.reuters.com/article/oilRpt/idINDEL15998520090907?pageNumber=1&
virtualBrandChannel=0.
84 http://www.indg.in/rural-energy/environment/national-action-plan-on-climate-change.
85 Ministry of New and Renewable Energy, “Statement of Dr. Farooq Abdullah on Jawaharial Nehru National Solar
Mission – ‘Solar India’” November 23, 3009.
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from renewable sources, with the specific shares to be determined by each SERC
individually. The states of Himachal Pradesh and Tamil Nadu have the highest quotas—20%
by 2010 and 10% by 2009, respectively. Under the Rural Electrification Policy (2006)
electrification of all villages must be completed by 2012.86
India established a program to replace 400 million incandescent light bulbs with efficient
compact fluorescents by 2012.
A fund supports the regeneration and sustainable management of forests. The initial capitalization
of the fund was proposed to be $2.5 billion, with an annual budget of about $1 billion.87
Although India has some pollution control standards in place, enforcement of standards has been
low.88 The current government is planning to establish a new National Environmental Authority,89
apparently to be modeled after the U.S. EPA.
3. Covered Gases and Sectors:
Most identified and proposed measures address CO2. The proposed system of “tradable energy
efficiency certificates” would apply to 714 energy intensive facilities in the following sectors:
fossil fuel-fired electricity generation; fertilizer production; cement; iron and steel; chlor-alkali
production; aluminum; rail transport; and textiles.
4. Allocation of GHG reductions to various sectors:
The Bureau of Energy Efficiency would assign energy efficiency improvement targets to the most
energy-intensive industrial plants, based on benchmark performance “bands.” Facilities in the
most efficient “band” would have a less stringent improvement target, while those in less efficient
“bands” would be required to make greater improvements. Facilities that perform better than the
targets would receive energy savings certificates (“ESCerts”) that could be sold to companies for
compliance with their targets or, potentially, banked to meet future requirements. Facilities that
fail to meet targets could be fined.
5. Any regulations or exemptions specific to trade-sensitive sectors:
Reportedly, Indian officials have suggested taxing imports based on the per capita carbon
emissions of the exporting country.90 This could have a large impact on the United States, as its
per capita emissions are higher than most countries. (Besides foods and fossil fuels, the United
States exports to India a wide variety of products, among which the largest in value are: civilian
aircraft and parts, steel and other metal products, synthetic fertilizers, chemicals, electronics and
industrial equipment, electronics, and gem diamonds.)91

86 Pew Center, “Climate Change Mitigation Measures in India,” International Brief 2, September 2008.
87 http://online.wsj.com/article/SB125018657071529801.html.
88 Among many sources: http://www.business-standard.com/india/news/23-thermal-plants-not-complyingemission-
norms/01/09/69289/on.
89 http://www.business-standard.com/india/news/govt-to-reduce-water-air-pollution/365976/.
90 http://www.dw-world.de/dw/article/0,,4707051,00.html.
91 U.S. Census Bureau, Foreign Trade Statistics, http://www.census.gov/foreign-trade/statistics/product/enduse/exports/
c5330.html.
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Motor Vehicles: In India, high taxes are levied on motor fuels: 52% on gasoline and 32% on
diesel in 2007. The Prime Minister’s office has directed the Bureau of Energy Efficiency to set
fuel efficiency labeling standards for vehicles under the Energy Conservation Act, to become
effective by 2011. However, after several years’ delay, these standards have not been set. As
planned, the standards would require labeling only by 2011, with mandatory performance to be
effective later. The Bureau of Energy Efficiency would certify the manufacturers’ labels.
Reportedly, some representatives of the automobile sector have demanded that the standards be
set on the basis of CO2 emissions and legally be put on India’s list of “local pollutants.”92

92 http://www.greencarcongress.com/2009/06/india-fe-20090603.html.
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Japan93
1. Overall GHG emission target, if any, and timing:
Under the Kyoto Protocol, Japan agreed to reduce its GHG emissions to 6% below 1990 levels in
the period 2008-2012. The Japanese Ministry of Environment has estimated that national GHG
emissions were about 1.9% above its 1990 Kyoto Protocol baseline or almost 8% above its
obligation, though this comparison does not account for sequestration or international GHG
credits. GHG emissions were 1,286 million tons in the Fiscal Year (FY) 2008-2009, about 6.2%
below the previous year, due largely to the economic recession.94
In mid-2008, then-Prime Minister Fukuda offered to reduce Japan’s GHG by 80% from 2008
levels by 2050, and by 8% below 1990 levels by 2020 (without using international credits).
Newly elected Prime Minister Yukio Hatoyama pledged Japan to a GHG target of 25% below
1990 levels by 2020, conditional on all major countries’ participation in a new international
accord. (The outgoing government’s proposed target was equivalent to 8% below 1990 levels. In
2008, Japan’s GHG emissions were almost 16% above its Kyoto Protocol target.)
Despite the lack of an internationally binding agreement at the Copenhagen climate conference,
Environment Minister Sakihito Ozawa and Minister of Economy, Trade, and Industry Masayuki
Naoshima reportedly reiterated the Hatoyama administration’s pledge of a 25% emission
reduction below 1990 levels by 2020 at a press conference on December 22, 2009. At least one
minister has noted that this pledge comes “with conditions” not specified.95
2. Principal Policy Instrument(s):
The Japanese Government formulated in 2005 the Kyoto Protocol Target Achievement Plan
(KPTAP) to promote measures to cope with global warming. The KPTAP lays out estimated
emissions and expected reductions by sector, and for several specific programs, in order for Japan
to meet its Kyoto Protocol target. The 2008 review and revision of the plan called for further
actions to close the gap between expected emissions and the Kyoto target, including more
stringent efficiency standards for equipment, vehicles, and small businesses. The government
plan concluded that it would be very difficult to constrain emission reductions associated with the
residential and commercial sectors, and therefore relied on expanding the Voluntary Action Plans
in the business sector to achieve 80% of the envisaged further GHG reductions.96 (See section on
covered gases and sectors, below.)
Since October 2008, Japan has established an integrated domestic GHG emissions market,
comprised of four components: (1) Japan’s Voluntary Emission Trading System (J-VETS) cap-
and-trade system, initiated in 2005 for voluntary trading of CO2 emissions from energy and
process emissions covering only industries that do NOT have in place a Voluntary Action
Program; (2) an Experimental Japanese Emissions Trading System, with emissions targets based

93 This section was prepared by Jane A. Leggett, Specialist in Environmental and Energy Policy (7-9525).
94 National Institute for Environmental Studies, http://www.nies.go.jp/whatsnew/2009/20091111/20091111-e.html.
95 BNA, “Japan Stands by Pledge to Cut Emissions 25 Percent by 2020; Industry Voices Dissent,” Daily Environment
Report
, 246 DEN A-3, December 29, 2009.
96 For a summary of the plan in English, see http://eneken.ieej.or.jp/data/en/data/pdf/443.pdf.
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on industry-specific Voluntary Action Programs; (3) Domestic Credit Scheme, to allow GHG
reduction credits (i.e., “offsets”) from small and medium-sized companies; and (4) Kyoto Credits,
available through any of the three Kyoto Protocol emissions trading mechanisms.
The new Hatoyama government has indicated it plans to create a mandatory GHG cap-and-trade
system, require “feed-in” tariffs as financial incentives for renewable energy generation, and may
consider a carbon tax.97 The Hatoyama campaign, on the other hand, pledged before the election
to eliminate highway tolls and a fuel tax of about 25 yen (US$0.28)98 per liter on gasoline by
April 2010, which could raise vehicle GHG emissions by as much as 20%.99
The Law Concerning the Promotion of Measures to Cope with Global Warming100 enacted in
1998, directed the national government to promote GHG emission reductions and to enhance
carbon sinks. It also directed local governments and business to take actions to limit emissions.
This basic authority also directs the central government to publish Japan’s GHG emissions.
The 5,000 largest businesses in Japan have been required to report their energy production and
consumption for more than a decade by the Law Concerning the Rational Use of Energy.101
Consequently, the foundation for calculating the energy-related CO2 emissions from each
industrial source is established.
The Act on Promotion of Global Warming Countermeasures and Act on Rational Use of Energy
establish authorities to promote energy efficiency in “energy-using” equipment, buildings,
factories, and machinery. These and related legislation require efficiency labeling, and allow for
low-interest financing, industrial improvement bonds, tax exemptions and other financial
incentives to promote efficiency. They also require efficiency measures by industrial facilities and
for appliances. The Energy Conservation Center of Japan (ECCJ) is a public-private partnership
for research and implementation of energy conservation programs (including Japan’s Energy Star
program, modeled after the US EPA’s), accreditation of energy managers, and information.
3. Covered Gases and Sectors:
Under Japan’s Kyoto Protocol Target Achievement Plan, industry is expected to reduce its GHG
emissions to 7% below 1990 levels during the Kyoto first commitment period (2008-2012). The
Keidanren Voluntary Action Plan102 on the Environment (VAP) covers 35 industries, include
energy, mining, construction, and at least some manufacturing sectors (e.g., production of
vehicles, electronics, steel, cement, etc.).

97 Various press reports, including http://search.japantimes.co.jp/cgi-bin/ed20090925a1.html.
98 Live market currency exchange rate for November 19, 2009, is listed as 1 JPY = 0.0112 USD (http://www.xe.com/).
Currency rates are subject to fluctuation.
99 http://www.planetark.com/enviro-news/item/54691.
100 Law No.117 of 1998.
101 22 June 1979, Law No. 49. Revised in 10 December 1983, 31 March 1993, 12 November 1993, 9 April 1997, and 5
June 1998.
102 Established by Nippon Keidanren, the Japan Business Federation. Negotiated environmental agreements in Japan
have been used in lieu of legally binding regulation since the 1990s, and are not comparable to “voluntary programs” in
the United States or some other countries. For example, they may require inspections and there are few reported
instances of non-compliance with set targets (Imura Hidefuri, “Building a Cooperative Relationship Between Industry
and Regulatory Authorities,” presented at OECD, Environmental Compliance Assurance: Trends and Good Practices
Paris, 17-18 November 2008.”
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4. Allocation of GHG reductions to various sectors:
The Keidanren VAPs include a non-binding target of reducing CO2 emissions in industry and
energy-converting sectors “below” their 1990 levels by 2010. In the Keidanren VAPs, different
industries’ metrics of performance and targets differ. In 2007, about 18 industries tightened their
voluntary targets, although some observers have criticized even the more stringent targets as
being no more than what was already being accomplished. Others argue that the voluntary targets
are costly compared to reductions expected in other countries, such as within the European
Union.
5. Any regulations or exemptions specific to trade-sensitive sectors: (See Figure 1.)
Motor Vehicles: The Japanese government provides tax benefits for “eco-friendly” vehicles and
exemptions from taxes for three years for “next-generation” vehicles.103 Beginning in April 2009,
subsidies have been offered to purchasers of eco-friendly vehicles (e.g., for cars: 100,000 yen, or
US$1100). These include a “cash-for-clunkers”-type program that offers higher subsidies to
owners who scrap vehicles 13 years or older and replace them with eco-friendly vehicles (e.g., for
cars: 250,000 yen, or US$2700). The subsidies extend as well to minivans, trucks and buses. One
industry official reported that, with the subsidies, “eco-friendly” vehicles accounted for almost
half of vehicle sales in Japan.104
Japan is reputed to have among the most stringent fuel economy standards for vehicles in the
world, at 46.9 miles per gallon by 2015 (see Appendix). These are expected to constrain new
passenger vehicle emissions of GHG.
Iron and Steel: To contribute to Japan’s Kyoto Protocol obligations, the Iron and Steel Federation
set a voluntary target for the sector of reducing CO2 emissions by 9% from its 1990-1991
(financial year) levels (200.6 million metric tons) during the period 2008-2012. Due largely to the
recession, the industry’s emissions were 178.2 million tons in 2008-2009, reflecting a 13%
reduction in steel output from the previous year. The industry reportedly also has purchased 56
million tons of GHG reduction credits for delivery during that period.105 The chairman of Japan’s
Iron and Steel Federation, Shoji Muneoka, has announced an industry reduction of 5 million
metric tons of CO2-equivalent GHG from their forecast level in 2020. The Federation’s business-
as-usual projection foresees crude steel production to rise from 2008-2020 by 13%, to 119.7
million metric tons.

103 http://www.jama-english.jp/asia/news/2009/vol36/index.html.
104 Ibid.
105 http://steelguru.com/news/international_news/MTIxMjIw/
Japan_steelmakers_to_receive_56_million_tonnes_of_CO2_offsets.html.
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Figure 1. Japanese Regulations or Exemptions Specific to Trade-Sensitive Sectors

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Note: Table copied from The Energy Conservation Center, Asia Energy Efficiency and Conservation
Collaboration Center, 2008. Available at http://www.asiaeec-col.eccj.or.jp/eng/e3104keidanren_plan.pdf.
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Korea106
1. Overall GHG emission target, if any, and timing:
On November 17, 2009, the South Korean cabinet approved a 4% GHG emission reduction target
by 2020 as a basis for its current and future climate change efforts. The goal is measured from a
2005 baseline and is equivalent to a 30% reduction from “business-as-usual.” The target is the
most ambitious of three options recommended by the country’s Presidential Committee on Green
Growth, which had urged South Korea to voluntarily participate in climate change efforts under a
midterm target of either an 8% increase, no change, or a 4% cut. President Lee Myung-bak said in
a statement released by his office that the decision was made “to facilitate the country’s paradigm
shift to low-carbon green growth.” He characterized the policy as a “voluntary, independent, and
domestic target for unilateral reduction,” driven by “environmental technology and renewable
energy development.”107
2. Principal Policy Instrument(s):
The November recommendation will empower a governmental committee to prepare industry-
specific quotas and implement support measures. Near-term reductions will focus on buildings
and transportation to give other industry sectors more time to adjust.
In addition to these recent measures, Korea’s policies have involved dialogue with industrial
organizations, voluntary plans by participating facilities to save energy and reduce CO2
emissions, and some non-regulatory emissions trading. The government has provided financial
incentives and technological assistance. Voluntary agreements cover plants that consume more
than 2,000 tons of oil equivalent annually.108 This process has resulted in some performance
benchmarking for industries, collaborative research, and participation in the Kyoto Protocol’s
Clean Development Mechanism.
South Korea recently said it plans to invest about 2% of its GDP annually in environment-related
and renewable energy industries over the next five years, for a total of US$84.5 billion. The
government said it would try to boost South Korea’s international market share of “green
technology” products to 8% by expanding research and development spending and strengthening
industries such as those that produce light-emitting diodes, solar batteries and hybrid cars.109 To
meet its pledge of a new, quantitative target, the government has indicated it may use GHG-
trading and tax incentives. It has also indicated that financial incentives would increase use of
hybrid cars, renewable and nuclear energy, light-emitting diode lighting, and smart grids.110

106 This section was prepared by Jane A. Leggett, Specialist in Environmental and Energy Policy (7-9525).
107 http://www.korea.net/News/News/newsView.asp?serial_no=20091118002&part=101&SearchDay=&page=1.
108 http://www.wwf.or.jp/activity/climate/lib/kyotoprotocol/20040928b.pdf.
109 Mufson, “Asian Nations Could Outpace U.S. in Developing Clean Energy,” The Washington Post,
http://www.washingtonpost.com/wp-dyn/content/article/2009/07/15/AR2009071503731.html.
110 Various press reports, including http://www.reuters.com/article/environmentNews/idUSTRE57308M20090804.
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3. Covered Gases and Sectors:
Sectors included in Korea’s “Industrial Organization for UNFCCC Task Force Team” are steel,
cement, electricity generation, paper, semi-conductor manufacturing, petrochemicals, oil refining,
and automobile manufacturing.
4. Allocation of GHG reductions to various sectors:
Not yet determined.
5. Any regulations or exemptions specific to trade-sensitive sectors:
Motor Vehicles: The automobile manufacturing association reached voluntary agreement with
the EU to meet CO2 emission standards of 140grams/km by 2008.111

111 http://www.wwf.or.jp/activity/climate/lib/kyotoprotocol/20040928b.pdf.
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Mexico112
1. Overall GHG emission target, if any, and timing:
Mexico voluntarily plans to cut national GHG emissions by 50 million tons per year beginning in
2012, constituting approximately 8% of Mexico’s net GHG emissions in 2008. The government
has established a non-binding goal to reduce GHG by 50% by 2050 (to 340 million tons of CO2)
below 2000 emissions. The pledge is contingent on availability of international technical and
financial support and on successful negotiation of an international agreement consistent with
stabilizing CO2-equivalent concentrations at 450 parts per million. Mexico foresees converging
by 2050 on global average emissions per capita at or below 2.8 tons of CO2 annually.
2. Principal Policy Instrument(s):
In 2007, the Government of Mexico set out a Strategy on Climate Change (NSCC) that identified
GHG mitigation opportunities, and vulnerability and adaptation policies. The ensuing Mexico
Climate Change Program (MCCP) sets 85 specific goals for mitigating GHG in four emission
categories and 12 subcategories. In December 2008, Mexican President Felipe Calderon
announced his intention to cap Mexican greenhouse gas emissions and allow GHG trading,
beginning with state-owned energy producers. Mexico envisions eventually being part of a
domestically regulated but internationally integrated North American GHG trading system.113
Mexico mainly promotes energy efficiency (including greater co-generation of heat and power by
industrial sources) and renewable energy production, along with prevention of further
deforestation, as its mitigation priorities. Principal instruments include Law for the Better Use of
Renewable Energy and the Financing of Energy Transition (2007 or 2008) provide a number of
legal energy reforms, including provisions that lay the groundwork for private investment in
renewable electricity generation. The Law for the Sustainable Use of Energy created a three-stage
program to 2050. It, inter alia, promotes renewable energy and energy efficiency. It also requires
energy efficiency in all federal, state and local governments.
3. Covered Gases and Sectors:
Six Kyoto Protocol gases. The cap-and-trade system under development is likely to cover energy
production (oil and gas, refining, electricity), metals, chemicals, textiles, and cement. Analysis is
underway to include a cap-and-trade program for vehicle fuel efficiencies as well.
4. Allocation of GHG reductions to various sectors:
Not yet determined.

112 This section was prepared by Jane A. Leggett, Specialist in Environmental and Energy Policy (7-9525).
113 North American Leaders’ Declaration on Climate Change and Clean Energy, August 10, 2009. Available at
http://pm.gc.ca/eng/media.asp?category=5&id=2724.
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5. Any regulations or exemptions specific to trade-sensitive sectors:
Motor Vehicles: The stringency of Mexico’s vehicle efficiency standards was increased in 2004
to a mix of U.S. and European standards for different classes of vehicles.
Oil and Gas Production, Refining and Distribution: PEMEX, Mexico’s state-owned petroleum
company, has operated an internal carbon cap-and-trade system since 1998.
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Russian Federation114
1. Overall GHG emission target, if any, and timing:
The Russian Federation (hereafter “Russia”) projects that its greenhouse gas (GHG) emissions in
the year 2010 will be 28% below the 1990 level, which is Russia’s GHG emissions cap (its
“Assigned Amount”) under the Kyoto Protocol.115 Though GDP in 2006 was 3% below the 1990
level, Russia’s GHG emissions were 34% below the 1990 level (inclusive of carbon uptake by
forests and other vegetation, net GHG emissions were 74% below the 1990 level). Some four-
fifths of the GHG reductions came from the energy sector. Russia’s GHG emissions are thus
below its Kyoto Protocol obligation, creating a large surplus of emission allowances (Assigned
Amount Units, or AAUs, in the terminology of the Protocol). Under the rules of the Kyoto
Protocol, Russia may sell its surplus AAUs to other Parties with GHG obligations.
A Presidential Decree116 on measures for increasing the energy and environmental efficiency of
the Russian economy was issued in 2008, setting a target to decrease the energy intensity of the
economy by at least 40% by 2020, compared to the 2007 level. The government has also set a
target to increase the share of renewable energy (excluding large hydroelectric production) in
electricity generation to 4.5% by 2020, and to use 95% of associated natural gas (produced with
oil) by 2014-2016.
In the Copenhagen negotiations, President Dmitry Medvedev has offered a GHG target for
Russia’s emissions of 22%-25% below 1990 levels by 2020.117 With policies and measures in
place, the Russian government has projected that its GHG emissions in 2010, 2015, and 2020 will
be reductions of 28%, 21%, and 13%, respectively, of its 1990 emissions level. Other experts
project them to be 10%-37% below 1990 levels in 2020 with current policies and economic
outlooks.118
Although Russian leaders agreed in the G8 summit meeting of July 2008 to consider an 80%
reduction from 1990 levels of GHG emissions from developed countries by 2050, Russia leaders
agreed only to a 50% reduction target for Russia.
2. Principal Policy Instrument(s):
Many observers contend that climate change has not attracted the interest of high level leaders in
Russia and that, consequently, “[t]he government hardly has any official climate strategy, and

114 This section was prepared by Jane A. Leggett, Specialist in Environmental and Energy Policy (7-9525).
115 United Nations Framework Convention on Climate Change, Report of the Centralized In-Depth Review of the
Fourth National Communication of the Russian Federation
(Bonn, August 31, 2009), http://unfccc.int/documentation/
documents/advanced_search/items/3594.php?rec=j&priref=600005423.
116 Decree 889, June 4, 2008.
117 http://www.reuters.com/article/idUSTRE5AH2IE20091118?feedType=RSS&feedName=environmentNews&
utm_source=feedburner&utm_medium=feed&utm_campaign=
Feed%253A+reuters%252Fenvironment+%2528News+%252F+US+%252F+Environment%2529.
118 See Table 5 in Aleksandra Novikova, Anna Korppoo, and Maria Sharmina, Russian Pledge vs. Business-As-Usual:
Impelementing Energy Efficiency Policies Can Curb Carbon Emissions
(The Finnish Institute of International Affairs,
December 4, 2009), http://www.upi-fiia.fi/en/publication/97/.
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little progress is occurring.”119 These claims persist in spite of apparent changes in the Russian
leadership’s diplomatic approach to the issue (e.g., an announcement of a climate “doctrine”
accepting that GHG emissions would pose risks and would require actions to reduce
emissions).120 Many suspect that Russia’s support for climate change actions is associated with
expanding its export market for natural gas in Europe and, to a much smaller degree, the value of
potentially selling its surplus AAUs to EU and other countries with GHG reduction obligations.
As noted above, Russia’s reduced GHG emissions is due primarily to economic collapse, leading
to steep drops in energy demand and production, as well as other activities (e.g., agriculture,
waste) that lead to GHG emissions. Replacing old, inefficient manufacturing and other
infrastructure has led to relatively slower increases in GHG emissions than in economic activity.
Figure 2. Russian Total Primary Energy Supply, 1990 and 2006
in million tons of oil equivalent (mtoe)
1000
879.6
Geothermal, solar,
900
wind
800
Combined RE and
677.6
700
Waste
Hydro
600
500
Nuclear
400
Gas
300
200
Oil
100
Coal/peat
0
1990
2006

Source: Novikova, 2009, op. cit.

119 Anne Karin Saether, “Moscow Environmental Conference Places Climate Demands on Medvedev,” Bellona, March
27, 2009, http://www.bellona.org/articles/articles_2009/environmentalists_put_climate_changes_to_medvedev; Simon
Shuster, “Russia offers climate goal with no real bite,” June 19, 2009, http://www.reuters.com/article/
environmentNews/idUSTRE55I3CP20090619; Ulkopoliittinen instituutti, “Russia’s Post-2012 Climate Politics in the
Context of Economic Growth,” May 11, 2008, http://www.upi-fiia.fi/fi/event/195/; or, Simon Shuster, “Russia Still
Dragging Its Feet on Climate Change,” Time, October 8, 2009, http://www.time.com/time/specials/packages/article/
0,28804,1929071_1929070_1934785,00.html.
120 Quirin Schiermeier, “Russia makes major shift in climate policy,” Nature -News (May 26, 2009),
http://www.nature.com/news/2009/090526/full/news.2009.506.html; Simon Shuster, “Russia offers climate goal with
no real bite,” June 19, 2009, http://www.reuters.com/article/environmentNews/idUSTRE55I3CP20090619; or 1. Oleg
Shchedrov, “Russia’s Medvedev warns of climate catastrophe,” November 16, 2009, http://www.reuters.com/article/
environmentNews/idUSTRE5AF1SU20091116.
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The government’s strategy for economic and social development has relied on reform and
expansion of the energy sector, in part because 50% of the central government’s revenue comes
from the oil and natural gas sector.121 The export value of oil and natural gas has driven a policy
emphasizing extraction of these resources for trade. However, many observers have noted a
concomitant, low level of investment in new capacity. The 2006 Russian Energy Strategy to 2020
sought to increase reliance on nuclear and coal-fired electricity for domestic use in order to
increase oil and natural gas available for export.122 Investments are being made to back out
natural gas use, for example, by investing in efficient, combined cycle gas turbine technologies.
These energy initiatives have mixed effects on GHG trajectories.
In 2005, the government adopted the Complex Action Plan for Implementation of the Kyoto
Protocol in the Russian Federation for 2004-2008. It gave coordinating authority to the
Interdepartmental Commission on Implementation of the Kyoto Protocol in the Russia
Federation. It established some sectoral targets for improving energy efficiency, although some
commentators allege that no actions would be needed to achieve them.123 The UNFCCC in-depth
review concluded that these targets had been only partially met.
The Mid-term Social-economic Development Programme of the Russian Federation for 2003–
2005 provided for economic incentives to modernize equipment and technologies, improving
energy efficiency and thereby reducing GHG emissions. To supplement these initiatives, a
Presidential Decree was issued in 2008 on measures for increasing the energy and environmental
efficiency of the economy of Russia. Other reported actions include:
• Gazprom, Russia’s state-owned natural gas enterprise, established an energy
conservation program for 2001–2010.
• Gazprom is implementing measures to reduce CH4 and CO2 emissions through
2012 (the annual reductions expected are a 10% reduction in CH4 emissions and
a 2.5% reduction in CO2 emissions); other measures to increase the efficiency of
gas transport and decrease losses by Gazprom (emission reductions of 3 Mt CO2
in the period 2001–2004 through reconstruction of pump stations).
• A federal program for housing for 2002–2010 targets housing retrofit and
modernization and includes energy efficiency measures and introduction of
small-scale renewable energy generation in the residential and services sectors.
On November 12, 2009, President Medvedev addressed the Federal Assembly and outlined his
proposal for Russia to “undergo comprehensive modernization.” In this speech Medvedev
announced that “increasing energy efficiency and making the transition to a rational resource

121 Jean Foglizzo, “Russia’s New Energy Strategy Seems a Lot Like its Old One,” The New York Times, March 30,
2008, http://www.nytimes.com/2008/03/30/business/worldbusiness/30iht-rnrgruss.1.11526942.html.
122 Kevin Rosner, “Dirty Hands: Russian Coal, GHG Emissions & European Gas Demand,” Journal of Energy Security
(August 27, 2009), http://www.ensec.org/index.php?option=com_content&view=article&id=207:dirty-hands-russia-
coal-ghg-emissions-aamp-european-gas-demand&catid=98:issuecontent0809&Itemid=349. The author raises, “The
significant issue is whether it would be more advantageous, from an environmental-security perspective within the
framework of Russia’s coal paradigm, that the majority of new coal capacity is driven by comparatively more regulated
OECD countries or whether it will revert back to Russia. Russia’s environmental record is not exemplary in this
regard.”
123 Ibid.
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consumption model is another of our economy’s [five] modernization priorities.”124 To this end,
he highlighted a number of new program proposals to:
• produce and install individual energy meters for households;
• transition to energy-saving light bulbs from 2011 to 2014;
• introduce energy service contracts and introduce payment for consumption of
services (and considering family incomes);
• increase efficiency in the public sector; and
• capture and sell natural gas co-produced with oil, instead of flaring gas.
President Medvedev also promoted developing waste-to-energy systems; super-conductors for
electricity production, transmission, and use; and nuclear generation, including nuclear fusion.
Some of these proposals were enacted into law in November 2009. The Russian government
plans to provide 1.8 trillion rubles ($62.5 billion) for energy-saving projects by 2020.125
According to the Kremlin website,126
... the new federal law introduces restrictions on the sale of incandescent light bulbs, sets
requirements for providing energy efficiency information on goods’ labeling, and also brings
in provisions on mandatory commercial inventories of energy resources, new buildings’
energy efficiency, and reductions in budget spending on purchasing energy resources. The
new law also introduces energy evaluations for the most energy-intensive organisations and
sets out provisions for transition to long-term tariff regulation and the establishment of a
common inter-ministerial energy efficiency information and analysis system.
Some observers have expressed reservations about Russia’s implementation of these policies,
based on past performance.127
The in-depth review of Russia’s Fourth National Communication under the United Nations
Framework Convention on Climate Change (UNFCCC) found that Russia did not report on its
specific domestic measures to abate GHG emissions or detail on how they would contribute to
meeting Russia’s GHG commitments.128 The review recommended that the government provide
greater transparency of how Russia’s policies and measures may be modifying long-term trends
in anthropogenic GHG emissions and removals. According to the UNFCCC in-depth review,
In the period 1990–1998, GHG emissions decreased almost in parallel with the economic
decline. In the period 1998–2006, GDP growth was accompanied by a relatively slower
increase in the level of GHG emissions, which was 9.9 per cent higher in 2006 than in 1998.
The differences between GDP and the GHG emission trends are mainly driven by: shifts in
the structure of the economy (particularly of non-energy intensive industries); shifts in the
primary energy supply (the share of oil and coal has decreased and the share of natural gas
and nuclear energy has increased); a decline in activities in the agriculture and transport

124 Dimtry Medvedev, “Presidential Address to the Federal Assembly of the Russian Federation,”
http://www.kremlin.ru, November 12, 2009.
125 Sergei Blagov, “Russia Seeks to Sustain its Energy Security,” Eurasia Daily Monitor, December 2, 2009,
http://www.cdi.org/Russia/johnson/2009-222-20.cfm.
126 Kremlin, November 23, 2009, http://eng.kremlin.ru/text/news/2009/11/222959.shtml.
127 For example, Novikova, 2009, op. cit. and Blagov, 2009, op. cit.
128 UNFCCC, op. cit., p. 4.
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sectors; the decrease in population (by 3.9 per cent); and the increase in energy efficiency.
These trends resulted in a 31.9 per cent decrease in the Party’s carbon intensity per GDP unit
in 2006 compared with that in 1990.
Russia has not reported estimates of how government funding or financial incentives may
influence GHG emissions.
Russia’s latest energy strategy, as updated in August 2009, focuses in 2013-2015 on recovery
from the current economic crisis. In its second phase, from 2015 to 2022, Russia would
emphasize introducing new technologies and more efficiency into its energy sector. An expansion
of renewable energy, including large hydroelectric plants, wind, and solar generation, would
occur only in the third phase of the new strategy, from 2022 to 2030, along with continued
development of hydrocarbon resources.
3. Covered Gases and Sectors:
Russia’s target under the Kyoto Protocol includes the six Kyoto Protocol gases.
4. Allocation of GHG reductions to various sectors:
None specified.
5. Any regulations or exemptions specific to trade-sensitive sectors:
Motor Vehicles: In 2005, limits on motor vehicle pollutant emissions were introduced, including
indicators of GHG emissions. These standards were comparable to the EURO 2–EURO 5
emission standards. (See Figure A-2 in the Appendix.)
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United States
1. Overall GHG emission target, if any, and timing:
The United States has not set legally binding targets to reduce its greenhouse gas (GHG)
emissions, neither under domestic law nor international treaty. The House of Representatives
passed a bill in June 2009 (H.R. 2454, the American Clean Energy and Security act of 2009) that
would cap GHG emissions at about 17% below 1990 emissions by 2020 and 83% below by 2050.
The Senate has been working on similar legislation, including S. 1733, the Clean Energy Jobs and
American Power Act, which contained a cap of 20% below 1990 levels by 2005 and 83% below
by 2050 when it was passed by the Committee on Environment and Public Works in November
2009.
On November 25, 2009, the White House announced that President Obama would attend the
December 2009 international negotiations in Copenhagen on an agreement to address climate
change beyond the year 2012. The White House stated that he is prepared to offer a “provisional”
emissions reduction target of 17% below 2005 levels by 2020, and “ultimately in line with final
U.S. energy and climate legislation.”129 On a path consistent with “pending legislation” for a
long-term policy objective of 83% below 2005 levels by 2050, U.S. GHG emissions would be
30% and 42% below 2005 levels in 2025 and 2030, respectively, according to the White House.
Had the United States become a Party to the Kyoto Protocol, it would have had an obligation to
reduce GHG emissions by 7% below 1990 levels during the first commitment period of 2008-
2012. In 2007, U.S. GHG emissions were about 16% above 1990 levels.130
Of the 50 States, 23 have set state-wide GHG mitigation targets, of which six are caps (maxima).
While some are enforceable, others are not.
2. Principal Policy Instrument(s):
Current federal climate change policies provide incentives, but few requirements, explicitly to
reduce GHG emissions; many programs exist, however, that contribute to limiting GHG
emissions through energy efficiency standards, and technical assistance and financial incentives
for renewable energy or other low-emitting technologies. For example, a number of tax incentives
are in place to encourage investment in renewable energy, more efficient vehicles, and efficiency
improvements to buildings. The White House identifies more than $80 billion of funding for
clean energy provided under the American Recovery and Reinvestment Act of 2009 (P.L. 111-5),
including the “largest-ever investment in renewable energy.”131 Other incentives induce
agricultural producers to enhance soil carbon. While temporary financial incentives have been
associated with greater investments, some stakeholders have indicated that longer duration of the
incentives and combining with other market correction measures are important to effectiveness.

129 White House, “Combating Climate Change at Home and Around the World,” November 25, 2009,
http://www.whitehouse.gov/blog/2009/11/25/combating-climate-change-home-and-around-world.
130 United States Environmental Protection Agency, The U.S. Inventory of Greenhouse Gas Emissions and Sinks: 1990-
2007
, EPA 430-F-06-010 (Washington DC: Office of Atmospheric Programs, 2009).
131 White House, 2009, op. cit.
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A suite of federal132 programs, including the Energy Star, Climate Leaders, and Climate
Challenge branded initiatives, provides information, technical assistance, and nominal awards to
businesses, universities, and other consumers to quantify and reduce their GHG emissions; such
programs generally are intended to encourage emission reductions that are already economical
but do not occur because of market inefficiencies.
Some GHG reductions are achieved by existing or contemplated regulations. A major regulatory
effort governs the energy efficiency of vehicles. For example, Corporate Average Fuel Economy
(CAFE) standards will tighten for Model Year 2011 cars and trucks to approximately 27.3 miles
per gallon (mpg). Again, these regulations have been put in place for reasons other than abating
climate change. However, the Department of Transportation and the Environmental Protection
Agency (EPA) are coordinating to propose new, joint CAFE and GHG emission standards for
Model Years 2012-2016. The proposal would reach an estimated combined average of 34.1 mpg
by 2016 (Table 1); combined with EPA’s compliance credits for improving air conditioners of
vehicles, the improvement could reach the GHG equivalent of 35.5 mpg. The proposed rules
contain flexibilities for manufacturers to comply with the new standards by earning credits by
over-complying, or by producing alternative or dual-fueled vehicles. Holders of credits may use
them for compliance of other model years or classes, or trade them to another manufacturer. The
agencies project that the new standards would reduce GHG emissions by about 900 million
metric tons,133 and reap net cost savings over the lifetimes of vehicles.
Table 1. Average Required Fuel Economies under Proposed Standards
(in miles per gallon for model year vehicles)

2012 2013 2014 2015 2016
Passenger
Cars

33.6 34.4 35.2 36.4 38.0
Light
Trucks

25.0 25.6 26.2 27.1 28.3
Combined

29.8 30.6 31.4 32.6 34.1
Source: National Highway Traffic Safety Administration, “NHTSA and EPA Propose New national Program to
Improve Fuel Economy and Reduce Greenhouse Gas Emissions for Passenger Cars and Light Trucks” fact sheet
available at http://www.nhtsa.dot.gov/portal/site/nhtsa/menuitem.d0b5a45b55bfbe582f57529cdba046a0/.
The United States has set minimum standards of energy efficiency for a wide variety of
residential and commercial equipment since the 1970s, with updates by several more recent
laws.134 Efforts are currently underway to address a backlog of regulations, such as for residential
water heaters, dishwashers, clothes dryers, and for commercial motors and lamps, and a number
of new, more stringent standards were issues in 2009. About two dozen additional standards are
planned over the next few years. In some instances, states may have set appliance efficiency
standards more stringent than federal standards (e.g., television standards in California).

132 See http://www.epa.gov/climatechange/policy/neartermghgreduction.html, http://www.pi.energy.gov/, and
http://www.usda.gov/oce/climate_change/index.htm.
133 White House, 2009, op. cit.
134 Established by Part B of Title III of the Energy Policy and Conservation Act (EPCA), P.L. 94-163, as amended by
the National Energy Conservation Policy Act, P.L. 95-619, by the National Appliance Energy Conservation Act, P.L.
100-12, by the National Appliance Energy Conservation Amendments of 1988, P.L. 100-357, and by the Energy Policy
Act of 1992, P.L. 102-486, and by the Energy Policy of 2005, P.L. 109-58.
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Methane emissions from landfills are controlled along with other air pollutants under the Clean
Air Act. According to EPA, the regulation requires installation of gas collection and control
systems for new and existing landfills and, generally, routing the gas to an energy recovery
system. The gas control system must reduce collected landfill gas (LFG) emissions by 98%.135
Large programs are devoted to developing new technologies that would be necessary to reduce
GHG emissions below current levels. Many experts contend that voluntary efforts (such as the
U.S. Climate Leaders Program), research on technologies, and existing regulatory and tax
incentives cannot achieve the GHG reductions necessary to avoid “dangerous” climate change.
Of the $6.4 billion in U.S. federal funding in FY2008 for climate change activities, almost all was
for scientific and technological research and development. In addition, tax incentives that could
help to reduce GHG emissions were equivalent to about $1.5 billion in FY2008. As mentioned
above, more than $80 billion in funding was available in FY2009. Funding for regulatory,
voluntary, and public education programs was a few percent of the total. President Obama has
also pledged, along with leaders of more than 20 other countries, to seek to phase out subsidies
for fossil fuels, reducing associated GHG emission by an estimated 10% or more by 2050.136
The 110th Congress enacted two broad pieces of legislation—an omnibus energy bill (P.L. 110-
140) and a comprehensive appropriations act (P.L. 110-161)—that include climate change
provisions. Both statutes increase climate change research efforts, and the energy act requires
improvement in vehicle fuel economies, as well as other provisions that would reduce (or
sometimes increase) GHG emissions. P.L. 110-161 directs the EPA to develop regulations that
establish a mandatory GHG reporting program that applies “above appropriate thresholds in all
sectors of the economy.”
In the absence of a federal regulatory framework to address U.S. GHG emission reductions, a
majority of states have established formal GHG mitigation policies, including targets for future
reductions. Sixteen states137 are regulating CO2 emissions from electric utilities: 11 using a
sectoral cap-and-trade approach, and five using emission performance standards. In several
regions, including the Northeast, the Midwest and the West, states are working together to create
regional schemes to cap GHG emissions and allow trading of emissions permits across borders.
All states but four now support “net metering” to allow producers of renewably generated
electricity to sell what they don’t use into the electric grid. Twenty-six states have set renewable
portfolio standards and another four have set alternative energy portfolio standards; these
standards require that a specified share of the state’s electricity must be generated by renewable
or alternative energy sources by a given date. An additional five states encourage renewable or
alternative energy sources with non-binding goals.
In the transportation sector, 15 states, led by California, are adopting GHG emission standards for
motor vehicles, and three additional states are poised to follow. Thirty-eight states offer tax
exemptions, credits, and/or grants to promote biofuels, of which 13 have set regulations requiring
a specified share of motor fuels to come from biomass. To address growth of traffic, 18 states
have set “smart growth” policies. Arizona, for example, has enacted laws and required improved

135 http://www.epa.gov/reg3artd/airregulations/ap22/landfil2.htm.
136 White House, 2009, op. cit.
137 Data on state policies come from the Pew Center on Global Climate Change website, extracted November 20, 2009.
http://www.pewclimate.org/states-regions.
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coordination of state agency spending to help communities address a variety of growth pressures.
Three of these states have also set targets to reduce vehicle miles traveled in the state. For
example, the State of Washington set a goal in 2008 to reduce annual per capita vehicle miles
traveled by 18% by 2020, 30% by 2035, and 50% by 2050, compared to 1990 levels.
Building codes typically fall under local authorities, although a growing number of states have set
performance standards that help to limit GHG emissions. Most states have set efficiency
standards for state, commercial, and residential buildings. Twelve have set appliance efficiency
standards as well.
Over the past five years, a proliferation of litigation relating to climate change also presses the
federal government toward actions to reduce GHG emissions. For example, the Supreme Court
ruled in 2007 that the EPA must consider regulating CO2 and other GHG emitted from motor
vehicles as pollutants under the Clean Air Act.138 The Obama Administration has made clear that
it would prefer Congress to enact GHG-specific legislation but that it will move to regulate in the
absence of such new law. Further litigation has been pursued, challenging the Executive Branch
to action, using the Endangered Species Act, the Energy Policy and Conservation Act and the
Outer Continental Shelf Lands Act. A few international-law claims have been filed against the
United States as well.139
3. Covered Gases and Sectors:
Only methane emissions currently are regulated directly, although CO2 has been proposed to be
regulated from motor vehicles (in a joint rule with fuel economy standards) and is reduced
through other regulatory measures.
4. Allocation of GHG reductions to various sectors:
Because no economy-wide reduction strategy is in place, there is no allocation among sectors.
5. Any regulations or exemptions specific to trade-sensitive sectors:
Because no economy-wide reduction strategy is in place, there are no regulations or exemptions
in place specific to trade-sensitive sectors. H.R. 2454, which passed the House on June 26, 2009,
includes two strategies to address possible shifts of GHG emissions from the United States to less
regulated companies in other countries: (1) free allocation of allowances (similar to that of the
EU), and (2) an international reserve allowance (IRA) scheme. The scheme would require
importers of energy-intensive products from countries with insufficient carbon policies to submit
a prescribed amount of “international reserve allowances,” or IRAs, for their products to gain
entry into the United States. Based on the GHG emissions generated in the production process,
IRAs would be submitted on a per-unit basis for each category of covered goods from a covered
country. Specifically, H.R. 2454 Section 768 requires EPA to promulgate rules establishing an
international reserve allowance system for covered goods from the eligible industrial sector,
including allowance trading, banking, pricing, and submission requirements. (See also the
Appendix, comparing U.S. efficiency standards for motor vehicles with those of other countries.)

138 Massachusetts v. EPA, 127 S. Ct. 1438 (2007).
139 See CRS Report RL32764, Climate Change Litigation: A Survey, by Robert Meltz.
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Appendix. Comparison of Vehicle Efficiency
Standards Internationally (as of Mid-2009)

Figure A-1. Comparison of International Fuel Economy and GHG Standards

Source: Feng An, “Revised Chart for World Standards,” Innovation Center for Energy and Transportation
(iCET) (2009). Available at http://www.icet.org.cn.
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Figure A-2. Standardized Comparison of
Select Vehicle Efficiency Standards Internationally
(standards as of mid-2009)

Source: Feng An, “Revised Chart for World Standards,” Innovation Center for Energy and Transportation
(iCET) (2009). Available at http://www.icet.org.cn.

Author Contact Information

Jane A. Leggett
Carl Ek
Specialist in Energy and Environmental Policy
Specialist in International Relations
jaleggett@crs.loc.gov, 7-9525
cek@crs.loc.gov, 7-7286
Richard K. Lattanzio
Larry Parker
Analyst in Environmental Policy
Specialist in Energy and Environmental Policy
rlattanzio@crs.loc.gov, 7-1754
lparker@crs.loc.gov, 7-7238


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