Title: Green growth: resources, sustainability and climate change
1Green growth resources, sustainability and
climate change
- Session 8
- Macroeconomics and the International Context
- MSc Economic Policy Studies
- Alan Matthews
2Learning objectives
- Valuing the threat of global warming and the
social cost of carbon - Implications of the EUs climate change targets
for the Irish economy - How can Ireland meet its GHG emission reduction
targets at least cost?
3Green growth
- Economic growth and environmental costs
- Energy, water, land, biodiversity, climate
- Have threshold boundaries been crossed?
- Awareness since Brundtland Report, 1987 and Rio
Earth Summit in 1992 - Green growth means fostering economic growth and
development, while ensuring that natural assets
continue to provide the resources and
environmental services on which our well-being
relies. (OECD, 2011) - Why invent a new discourse? (Jacobs, 2012)
4Green growth
- Contains the strong assertion that economic
growth can occur even while environmental impacts
are significantly reduced - Standard form
- the costs of tackling environmental damage are
not so great that they reduce the natural growth
rate of a well-performing economy to zero. - if such damage is not tackled, the costs to
growth of a worsening environment will be
greater. - Strong form
- Environmental protection is not just a drag on
growth, it can positively promote it.
5Green growth
- Keynesian stimulus argument
- green spending helps create jobs during a slump
- Ignoring/undervaluing natural capital means
current growth is sub-optimal - First mover advantage environmental policy
can create lots of new jobs in environmental
industries - Low-carbon technologies are potentially
transformative (like coal, oil, ICT)
6Valuing the social cost of carbon
7The science of climate change
- What is the sustainable level of emissions?
- Scientific consensus on global warming
- Climate is warming
- The cause, with high probability, is GHGs
- These emissions are in large part due to human
behaviour, including fossil fuel consumption - IIEA Occasional Paper on science of climate
change - IPCC Working Group 1 report summary for
policymakers
8Assessing the impact of climate change
- Projections of CO2 concentration in atmosphere
- General circulation models (GCM) models
- Expected temperature and precipitation effects
for different regions - CO2 concentrations now 380 ppmv compared to
pre-industrial levels of 280 ppmv - Projected to double by 2100 leading to
temperature increases of between 1.8 to 4
(faster warming when all GHGs included) - To have high probability of staying within the
2 target, mainstream view is to limit C02
concentration to 400 ppmv (50 probability at 450
ppmv)
9Source EEA SOER 2010
10Temperature implications of different levels of
CO2 concentration
11How likely are these trends?
- CGM models fit observed data from the past quite
well - But their weakness is that the physics of natural
climate change is poorly understood and therefore
there is uncertainty about model predictions - Others argue that models take inadequate account
of feedback effects and threshold mechanisms
which could accelerate climate change
12Integrated Assessment Models (IAMs)
- Seek to translate climate impacts into monetary
damages - Benefits of climate policy represent avoided
climate impacts that would otherwise cause
damages to society in the future. - Used to calculate Social Cost of Carbon (SCC)
(monetary estimates of the damage done to society
in emitting one tonne of carbon today) for use in
domestic CBA decisions - Used to determine optimal policy using form of
global cost-benefit analysis.
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14Areas of uncertainty in IAMs, leading to
different results for social cost of carbon
Target to be achieved, recycling of tax revenues,
speed of adjustment
Mitigation costs
15Impact of differences in climate sensitivity
- Models differ in their climate sensitivity, the
long-term temperature increase associated with a
sustained doubling of carbon dioxide
concentrations in the atmosphere - The higher the climate sensitivity, the greater
the damages - IPCC (2007) presented likely range for climate
sensitivity of 2-4.5C by end of century, with
best estimate of 3C.
16Differences in climate impacts
- Impacts of climate change are modelled using
climate damage functions for each region - Damage functions provide monetary estimates of
climate impacts as a function of average
temperature increase, often expressed as
percentage loss of GDP - Generally, damages assumed to rise non-linearly
with temperature different models assume
different curvature and steepness of the rising
damage function - Damage estimates often based on single study
which is then scaled up or down for application
to other regions
17Differences in adaptation assumptions
- The damages of global warming are a function of
how easily societies can adapt to higher
temperatures - The lower the adaptation costs, the lower the
benefits of avoiding climate change
18Differences in discount rates
- Some method of aggregating gains and losses from
different time periods is required. - In the prescriptive approach presented by
Ramsey (1928), the discount rate r can be
expressed as - r ? ?g
- where ? is the pure rate of time preference and
?g is the expected upward trend in income over
time (? is the negative of the elasticity of the
marginal utility of consumption (the rate at
which additional consumption provides smaller
increases in welfare) and g is growth rate of per
capita consumption) - The descriptive approach uses the market rate
of interest - Extensive debate about the appropriate values on
economic and ethical grounds (Stern Report
assumes zero rate of time preference)
19Discount rates and equity weights
- Higher rate of pure time preference lowers
calculations of benefits of climate change
policy, because future climate change damages are
discounted more heavily - Value of the marginal utility of consumption can
be varied to reflect equity weights (giving more
weight to impacts in poor regions) - Using purchasing power parity rates to aggregate
damages across regions (Stern, 2007) gives
greater weight to impacts in poorer regions where
majority of impacts will occur, producing effect
similar to equity weighting
20Migitation costs
- Emission reduction costs in models vary by an
order of magnitude - Depends on options/technologies considered
- Depends on behavioural parameters assumed
- Depends on assumed impact of climate policy on
technological change
21Social cost of carbon estimates (Tol, 2009)
Note SCC estimates can be converted into CO2e
costs by dividing by 3.66
22 Climate change is a moral problem. The main
reason to reduce greenhouse gas emissions is a
concern for faraway lands (Schelling 2000),
distant futures (Nordhaus 1982), and remote
probabilities (Weitzman 2009). The people who
emit most are least affected by climate change,
and the benefits of their abatement would be
diffused. Carbon dioxide dwells in the atmosphere
for decades and the effects on temperature and
sea level play out over even longer periods. On
central projections climate change and its
impacts are a nuisance for rich countries and a
problem for poor countries. But there is a chance
that things will go horribly wrong. If you do not
care about risk, the future, or other people,
then you have little reason to care about climate
change. Source Anthoff and Tol, 2010.
23Critique of SCC calculations
- Conventional economic analysis is rapidly
replacing the arguments of the climate skeptics
as the principal justification for inaction on
climate change (Ackerman, 2008) - Interests of future generations should be more
highly valued (ethics) - Prevention of worst-case risks should be
prioritised more than average outcomes
(insurance) - Some benefits cannot be given monetary values
- Some costs are better than others
24Costing the externality due to carbon emissions
- Social cost of carbon
- Measures the full global cost today of an
incremental unit of carbon emitted today, summing
the cost of the damage it imposes over its
lifetime in the atmosphere - Market price of carbon
- The value of traded emission rights in a market
given policy constraints on rights supply - Marginal cost of abatement
- Reflects the cost of reducing emissions rather
than the damage imposed by creating emissions - Under restrictive assumptions the three measures
will be broadly equal, at the margin.
25Policy approaches
- Command-and-control
- Use of regulation
- Market-based approaches
- Carbon tax
- Cap and trade
- Advantages and disadvantages
26The economic perspective
- Once target level of emissions set, what is the
least cost abatement strategy? - Government policies often industry and
technology-specific - Economists favour uniform price signals, on the
basis that the same value is attached to each
unit of emission reduction, whatever the source - Optimal policy is a carbon tax (or equivalent
cap-and-trade) at a low initial rate, increasing
subsequently in real terms
27Regulation vs tax to reduce pollution
Profits, costs of pollution, /unit
MP
MSC
Tax
Q
Q
Output of paper mill
28Rationale for market-based interventions
- To correct for negative market externality
- Huge differences in abatement costs across
different options - Use of market-based policy instrument can achieve
GHG emission reductions at lower cost than
command-and-control approach - Desirability of a uniform tax on all emitters as
the marginal value of abatement is equal - Impact channels for market-based approaches
- Firms adapt by switching from higher to lower
carbon fuels and invest in energy saving
technologies - Consumers adapt by purchasing less
energy-intensive goods and change behaviour in
ways that conserve energy - GHG pricing policies also provide incentives to
develop new technologies
29Comparison of GHG tax versus Cap and trade
- Both are market or incentive-based systems
- Under perfect information, both approaches would
produce the same overall level of emissions at
the same level of aggregate costs - But uncertainty over future cost of reducing
emissions can lead to different outcomes - Compare approaches wrt environmental
effectiveness, cost effectiveness and
distributional equity
30Environmental effectiveness
- Cap and trade provides emissions certainty,
whereas total emissions abatement effect of a tax
is uncertain when tax is set. - Certainty may be important in climate change if
there are systemic thresholds - Cap and trade provides certainty on emission
outcomes, but cost of meeting targets is
uncertain at firm level - Competitiveness effects and leakages?
31Cost effectiveness
- A tax is more flexible and allows firms to
minimise their compliance costs over time,
although Cap and trade can be designed to mimic
this (e.g. shifting emissions through time) - Volatility of permit prices under Cap and trade
schemes - Tax raises revenue, although can be mimicked in
Cap and trade if permits are auctioned - Carbon tax could have positive effects on GDP,
depending on how revenues are used - Grandfathering permits can gain political
acceptability, but at cost of positive growth and
distributional effects from recycling revenue
(inframarginal exemptions do the same for carbon
tax).
32Distributional consequences
- Not obvious the poor are worst hit by carbon
taxes (motoring vs home heating) - But proportionately poor will be hit more
- Distributional issues can be addressed by
compensation (may be easier to finance under
carbon tax unless emission permits are auctioned)
33The International response
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35UNFCCC RIO 1992
- UNFCCC came into force 1994
- Overall objective of stabilisation of GHG
concentrations in atmosphere at a level that
would prevent dangerous anthropogenic
interference with the climate system - Establishes principle of common but
differentiated responsibility - Commits to establishing inventories and reporting
standards for GHG measurement - Commits to launching national strategies to
mitigate GHG emissions - And to cooperate in preparing for adaptation to
climate change - Convention governed by Conference of Parties (COP)
36Kyoto Protocol 1997
- Annex 1 (developed) countries agreed to reduction
targets - Groups (bubbles) of countries can manage their
efforts in unison - Defined three flexible mechanisms
- Joint Implementation, Clean Development Mechanism
and Emissions Trading - US refused ratification
- EU ratified in 2002 and Protocol came into force
in 2005 following accession of Russia
37Copenhagen 2009
- Agreed the Copenhagen Accord
- Set long term goal of limiting global warming to
2 degrees Celcius - Called for new multilateral climate fund and set
goals of mobilising 30 billion in public finance
2010-2012 and 100 billion in public and private
finance in 2020 - Further defined how countries actions are to be
reported and verified - Called on countries to list mitigation pledges
(economy-wide targets for developed countries,
mitigation actions by developing countries)
38Durban 2011
- Agreed roadmap Durban Platform for Enhanced
Action to draw up legal framework for action by
all countries by 2015 to be implemented from 2020 - Second commitment period of Kyoto Protocol agreed
- Green Climate Fund made operational
39The eu response
40Initial EU responses
- Committed to goal of limiting global mean
temperature rise to 2C - Accepted -8 target under Kyoto for EU-15
- Burden-sharing agreement
- Penalties
- Introduced ETS in Jan 2005
- First (pilot) phase 2005-2007
- Second phase 2008-2012
- Third phase 2013-2020
- Countries targets and strategies set out in
National Allocation/Implementation Plans which
must be approved by Commission
41EU ETS experience
- Initial pilot phase 2005-07. ETS covers about
40-50 of EU emissions. - Combination of generous allowances and abatement
produced an initial price of 30 per tonne, but
fell to zero in late 2007, some recovery since
then, but more recent collapse. - Market value of allowances was passed through in
electricity prices, even though allowances
distributed free, resulting in considerable
windfall profits - The Linking Directive allows firms to meet some
of their obligations by purchasing certified
emission reductions achieved in projects in
developing countries and other developed
countries - Third phase introduced single EU-wide cap and
gradual increase in share of permits to be
auctioned
42Price of ETS allowances
Source www.eex.com/en
43EU Climate change 202020 package Dec 2008
- Overall EU target 20 reduction by 2020 (relative
to 1990 levels) - Increased to 30 if there is new international
agreement - Reduction effort split between ETS and non-ETS
sectors - ETS reduction (EU-wide) of 21 by 2020 (compared
to 2005) - Average EU non-ETS reduction target of 10 in
2020 (compared to 2005) - Overall, averages out at 14 reduction (compared
to 2005) and 20 reduction (compared to 1990) - Non-ETS effort is shared among EU countries
according to a formula based on GDP per capita. - 20 energy from renewables by 2020
- 20 increase in energy efficiency by 2020
44Long-term targets
- Spring European Council 2007 meeting agreed
indicative EU targets of 60-80 emission
reductions by 2050 - Economic activity by then needs to be largely
carbon-free - Implications?
45Irish targets for ghg emission reductions
46Irish policy commitments
- Second highest per capita emitter in EU
- EU Kyoto target was to reduce emissions by 8 by
2012 over 1990 - Under EUs burden-sharing agreement, Irelands
target was to limit to 13 increase - Irelands emissions in 2006 25.5 above 1990,
almost 13 above its Kyoto target
47Source EPA 2010
48Current situation
- EPA is charged with producing emission
projections annually - NCCS targets distinguish between (a) baseline (b)
baseline with existing measures and (c) baseline
with additional measures (post 2006) - Ireland met its Kyoto Protocol target, albeit
with the help of recession
49Ireland met its Kyoto target 2008-2012
Source EPA 20102
502020 targets
- For ETS sector Ireland is allocated 88 of its
2005 emissions which will be auctioned starting
2013 - The target for Ireland for non-ETS sectors is to
reduce emissions by 20 in 2020 relative to 2005
levels the limit has been provisionally
calculated by the EPA as 37.1 Mtonnes of CO2e. - In addition, Member States must annually limit
non-ETS greenhouse gas emissions in a linear
manner between 2013 and 2020, including by making
use of the flexibilities provided for in the
Effort Sharing Decision
51Likely path in reaching non-ETS targets
Source EPA 2012
52Gormley Climate change bill
- Set 2020 reduction target of 30 below 2005
emissions (12 below 1990 emissions) - Problematic as separation of ETS sector would
oblige Ireland to meet the gap between the EU
target (-20) and the Irish target (-30) through
emission reduction in the domestic non-ETS sector
- Very ambitious targets for 2030 (40 below 1990
levels) and 2050 (80 below 1990 levels) - National Climate Change Expert Advisory Body
- Uninformative Regulatory Impact Assessment
53Hogan Climate change bill
- 2011 National Climate Policy Strategy Review
- 2012 Heads of Climate Action and Low Carbon
Development Bill published - 2013 Legislation expected in second half of year.
54Irish Climate change policies
55National Climate Change Strategy
- Sets out in detail how Ireland will meet its GHG
commitments in period 2007-2012 - Carbon Fund established in 2007 managed by NTMA
to buy Kyoto Units with funding of 290m - NCCS does not deal with post-2012 situation
- Programme for Government commitment to reduce GHG
emissions by 3 p.a. for period of government. - Cabinet Committee on Climate Change and Energy
Security
56Climate strategy
- By 2020, Ireland will have achieved
- 20 improvement in energy efficiency across all
sectors - 33 energy end-use efficiency savings target for
the public sector - 40 renewable electricity (RES-E) share
- 12 renewable heat (RES-H) share
- 10 renewable transport (RES-T) share (including
10 electric vehicles penetration target)
57Carbon budgets
- First carbon budget presented in 2007
- Objectives to integrate climate change into
budgetary policy, to assess progress towards
targets and to help efforts to increase public
understanding - Measures introduced include
- Carbon tax
- Reform of motor tax regime
- New building regulations for new homes
- New national energy efficiency standard for
lightbulbs - Residential home insulation scheme grants
58Reading a marginal abatement cost curve
Issues Need to avoid double counting with
successive measures Considers
technical but not behavioural changes (e.g. modal
shift in transport)
Source McKinsey 2009 for SEAI
59Source McKinsey 2009 for SEAI
60Source McKinsey 2009 for SEAI
61Policy outlook - ETS
- Removal of ETS sector from national inventories
changes the ground rules - Irish tradable (ETS) sector covers around 34 of
Irish emissions (41 across EU) - Reduction requirement across EU is -21 or -1.74
p.a. - Price of CERs will reflect abatement cost to
industry - Irish operators exposed to competitive pressures
will continue to receive free allocation of
permits (to extent to be decided) - The measures to increase renewables share in
energy and improve efficiency of powergen sector
do not count in national emission inventories
62Policy outlook non-ETS sectors
- 66 of overall Irish emissions, mainly transport
and agriculture - Reduction of 20 on 2005 levels by 2020
- Use of flexible mechanisms limited to 3
- Huge challenge, even if less than PfG target and
targets set out in NCCS - Future position of carbon sinks still unclear
- Important flexibility introduced in EU package to
allow (some) trading in non-ETS sectors which
will cap marginal cost of abatement in Ireland - Differences in marginal cost of abatement in the
two sectors could create incentives to migrate
emissions (e.g. through electrification)
63Renewable energy
- EU targets 16 in total final energy use and
10 in transport use - Controversies over use of first-generation
biofuels - Doubts over penetration of electric vehicles and
their impact on emissions - Growing concern in other EU MS about cost of
meeting renewable targets
64Designing a carbon taxTol et al 2008
- What level of tax?
- Set equal to ETS permit price as then uniform tax
applied to all emission sources - Who should be taxed?
- All emission sources except those covered by the
ETS - What is expected revenue?
- 500 1,400m
- What to do with the revenue?
- What are macro-economic implications?
- What are the effects on emissions?
- Substitution vs growth effects
65Designing a carbon taxTol et al 2008
- What will be distributional consequences?
- Poor/rich Urban/rural
- Possible to compensate relatively easily
- How to tax internationally traded goods and
services? - ETS industries cement and aluminium
- Non-ETS sectors agriculture
- What about fuel tourism?
66Assessing the NCCS
- Preference for quantitative targets vs economic
instruments - Within economic instrument category, very high
reliance on subsidies (50 of overall total
emissions) how to finance? - Critique of individual measures McCarthy and
Scott (2008)
67Assessing the NCCS
- One-third of emissions regulated by tradable
permits mainly power - But double regulation (subsidies for renewables,
peat) - One-third of emissions regulated through carbon
tax and other instruments - But exemptions for coal and peat for home
heating, subsidies for renewable heating - One-third of emissions not regulated
68Adaptation issues
- Various recent reports
- Forfás , Adaptation to Climate Change Issues for
Business, 2010 - Irish Academy of Engineers, Critical
Infrastructure Adaptation to Climate Change,
2009 - EPA, A Summary of the State of Knowledge on
Climate Change Impacts on Ireland, 2009 - Sweeney et al, Climate Change Refining the
Impacts for Ireland, 2008
69Follow up and further information
- Institute for International and European Affairs,
Climate Change Group - EPA, Climate Change
- DOEHLG, Climate Change
- European Environment Agency, Data Viewer