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Tol, Richard S.J.
Working Paper
Why Worry About Climate Change? A Research
Agenda
Nota di Lavoro, No. 136.2006
Provided in Cooperation with:
Fondazione Eni Enrico Mattei (FEEM)
Suggested Citation: Tol, Richard S.J. (2006) : Why Worry About Climate Change? A Research
Agenda, Nota di Lavoro, No. 136.2006, Fondazione Eni Enrico Mattei (FEEM), Milano
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Why Worry About Climate
Change? A Research
Agenda
Richard S.J. Tol
NOTA DI LAVORO 136.2006
NOVEMBER 2006
CCMP – Climate Change Modelling and Policy
Richard S.J. Tol, Economic and Social Research Institute
Research unit Sustainability and Global Change, Hamburg University and Centre for
Marine and Atmospheric Science, Institute for Environmental Studies, Vrije Universiteit
Engineering and Public Policy, Carnegie Mellon University
This paper can be downloaded without charge at:
The Fondazione Eni Enrico Mattei Note di Lavoro Series Index:
http://www.feem.it/Feem/Pub/Publications/WPapers/default.htm
Social Science Research Network Electronic Paper Collection:
http://ssrn.com/abstract=945044
The opinions expressed in this paper do not necessarily reflect the position of
Fondazione Eni Enrico Mattei
Corso Magenta, 63, 20123 Milano (I), web site: www.feem.it, e-mail:
[email protected]
Why Worry About Climate Change? A Research Agenda
Summary
Estimates of the marginal damage costs of carbon dioxide emissions suggest that,
although climate change is a problem and some emission reduction is justified, very
stringent abatement does not pass the cost-benefit test. However, current estimates of
the economic impact of climate change are incomplete. Some of the missing impacts are
likely to be positive and others negative, but overall the uncertainty seems to
concentrate on the downside risks and current estimates of the damage costs may have a
negative bias. The research effort on the economic impacts of climate change is minute,
and should be strengthened, with a particular focus on the quantification of
uncertainties; estimating missing impacts, interactions between impacts and higherorder effects; the valuation of biodiversity loss; the implications of extreme climate
scenarios and violent conflict; and climate change in the very long term.
Keywords: Climate Change, Impacts, Valuation, Cost-benefit Analysis
JEL Classification: Q54
Address for correspondence:
Richard S.J. Tol
Economic and Social Research Institute
4 Burlington Road
Dublin 4
Ireland
E-mail:
[email protected]
1.
Introduction
Tol (2005a) reviews the literature on estimates of the marginal damage costs of carbon
dioxide emissions, the main cause of climate change. He finds that the estimated Pigou tax is
relatively small: For a 3% utility discount rate, the median estimate in the literature is $7/tC.
This estimate is higher than the actual price of carbon in most countries. However, only the
most optimistic studies of the costs of emission reduction suggest that $7/tC would buy
substantial abatement (Weyant, 1993, 2004). I am not aware of any serious study that suggests
that this carbon tax would buy atmospheric stabilisation. Indeed, cost-benefit analyses of
climate change show only modest emission reduction (Nordhaus, 1991; Nordhaus and Yang,
1996; Tol, 1999). Do economists such as Tol (2005a) therefore conclude that we should not
worry about climate change? This paper argues not.
Tol (2005a) is a literature review and meta-analysis. The quantified part of the climate change
impacts literature suggests that we should not worry too much (see Pearce et al., 1996 and
Smith et al., 2001, for a survey). However, before reaching a conclusion from an estimate,
one needs to consider the completeness of that estimate. Damage cost estimates are
incomplete. There are reasons to assume that some of the omitted impacts are substantial and
negative, but other omitted impacts may be positive. This paper does not argue “we don’t
know and therefore …”. Rather, it surveys the missing climate change impact estimates,
speculates why we should worry about them, and sketches what research will need to be done
to quantify these impacts.
I do not adopt a more risk averse, or prudent, or precautionary standpoint because there is a
long history of worrying about the unquantified impacts of climate change. Initially, people
were worried about widespread starvation (Hohmeyer and Gaertner, 1992), about extreme sea
level rise (Schneider and Chen, 1980), or about infectious diseases killing millions (Haines
and Fuchs, 1991). Later studies showed the initial worries to be exceedingly pessimistic
(Darwin et al., 1995; Nicholls and Tol, 2006; McMichael et al., 2003). At the moment, there
is concern about water resources (Arnell, 2004) and the thermohaline circulation (Rahmstorff,
1994), but here as well the concern may be overstated (Mendelsohn and Bennett, 1997; Link
and Tol, 2004).
Another argument against a precautionary approach is that climate change is a two-sided risk,
not a one-sided one. Gradual emission reduction is probably cheap, but stringent, rapid
emission reduction may well be expensive, even if implemented in a cost-effective manner
(Weyant, 2004). Governments may not adopt cost-effective abatement policies, which would
increase costs substantially. Currently, the price of carbon permits in Europe is higher than
economic models suggest it should be (e.g. Viguier et al., 2003), another reason for caution
on the abatement side.
Nonetheless, the policy suggested by cost-benefit analysis – emission reduction, but not
enough to stabilise emissions let alone concentrations – is intuitively wrong. It cannot be the
case that the best policy is to let the world get warmer and warmer and warmer still. An
obvious reason is that the human body fails if it gets too hot (Parker, 2000, suggests a limit of
43ºC), and if the ambient concentration of carbon dioxide is too high (the US Occupational
Safety and Health Administration has a provisional exposure limit of 10,000 ppm; see
NIOSH, 2001). But common sense suggests that climate change should be stopped at a lower
level. Our best estimates challenge the common sense, but it is as yet unclear whether our
research findings are superior to our gut feelings. Having worked in this field for 15 years, I
do not know.
There are two other reasons to challenge the recommendations of cost-benefit analyses of
climate change. The first is uncertainty. Uncertainties are vast, and negative surprises are
more likely than positive surprises. Qualitatively, such uncertainty almost always calls for
more stringent action. However, quantitatively, the uncertainties are unknown (CBO, 2005)
but perhaps very large (Tol, 2003). The second reason is equity. The largest (smallest)
emitters of greenhouse gases are least (most) vulnerable to climate change. Cost-benefit
analysis of climate change with inequity aversion typically recommends higher emission
abatement (Tol, 2001, 2002a). However, in other arenas, equity is not an important argument,
so why would it be in climate change?
This paper is structured as follows. In Section 2, I review estimates of the economic impacts
of climate change. I discuss direct costs, both total and marginal, and indirect costs. I
particularly emphasize the quality and completeness of the assumptions. In Section 3, I survey
four reasons why the economic impact would be higher than currently estimated. These are
biodiversity loss, extreme climate scenarios, violent conflict, and the very long term. Section
4 concludes the discussion.
2.
A review of the economic impacts of climate change
2.1.
Total costs
The first studies of the welfare impacts of climate change were done for the USA (Cline,
1992; Nordhaus, 1991; Titus, 1992; Smith, 1996). Although Nordhaus (1991; see also Ayres
and Walter, 1991) extrapolated his US estimate to the world, the credit for the first serious
study of the global welfare impacts goes to Fankhauser (1994, 1995). 1 Other global estimates
include those by Nordhaus (1994a,b), Tol (1995), Nordhaus and Yang (1996), Plambeck and
Hope (1996), Nordhaus and Boyer (2000), Mendelsohn et al. (2000a,b), Tol (2002b),
Maddison (2003), Hope (2006), Rehdanz and Maddison (2005) and Nordhaus (2006).
This is a rather short list of studies, and an even shorter list of authors. 2 Although most fields
are dominated by a few people, dominance is here for want of challengers. The effect of this
is hard to gauge. The reasons are lack of funding (this work is too applied for academic
sources, while applied agencies do not like the typical results), lack of daring (this research
requires making many assumptions, and taking on well-entrenched incumbents) and lack of
perspective (generalists have a hard time building a career).
Table 1 shows some characteristics of these studies. A few insights emerge. First, the welfare
impact of a doubling of the atmospheric concentration on the current economy is relatively
small. Although the estimates differ, impacts are not more than a few percent of GDP. The
estimates of Hope (2006), Mendelsohn et al. (2000a,b) and Tol (2002b) even point to initial
benefits of climate change. 3 With such estimates, it is no surprise that cost-benefit analyses of
climate change recommend only limited greenhouse gas emission reduction – one of the more
contentious findings of the climate economics literature.
Second, although the impact is relatively small, is not negligible. A few per cent of GDP in
annual damage is a real concern.
Third, climate change may initially have positive impacts. This is partly because the higher
ambient concentration of carbon dioxide would reduce water stress in plants and may make
them grow faster. Another reason is that the global economy is concentrated in the temperate
zone, 4 where a bit of warming may well be welcomed because of reductions in heating costs
and cold-related health problems. Even though initial impacts are positive, it does not
necessarily follow that greenhouse gas emissions should be subsidized (see below). The
climate responds rather slowly to changes in emissions, so the initial impacts cannot be
avoided. Impacts turn negative roughly at the same time as climate change can be influenced
by present and future emission reduction (Hitz and Smith, 2004; Tol, 2002c; Tol et al., 2000).
The fourth insight is that relative impacts are higher in poorer countries (see also Yohe and
Schlesinger, 2002). This is because poorer countries have a lower adaptive capacity (Adger,
2006; Alberini et al., 2006; Smit and Wandel, 2006; Yohe and Tol, 2002), particularly in
health (Tol, 2005b), and have a greater exposure to climate change, particularly in agriculture
and water resources. Furthermore, poorer countries tend be hotter and therefore closer to
temperature limits and short on spatial analogues should it get warmer still. This has two
policy implications. Any justification of stringent emission abatement is an appeal to consider
1
Hohmeyer and Gaertner (1992) earlier published some low quality estimates.
This problem is worse if one considers that Nordhaus and Mendelsohn are colleagues; that Fankhauser,
Maddison and Tol all worked with David Pearce; and that Rehdanz works with Maddison and Tol. Hope’s
estimates are averages of Fankhauser’s and Tol’s.
3
Studies published after 1995 all have regions with net gains and net losses due to global warming, whereas
earlier studies only find net losses.
4
At the same, the world population is concentrated in tropics.
2
the plight of the poor and the impacts imposed on them by the rich (Schelling, 1992, 1995).
While this makes for wonderful rhetoric and fascinating research (e.g., Tol, 2001), reality
shows little compassion for the poor by the rich. Furthermore, if poverty is the root cause for
vulnerability to climate change, one may wonder whether stimulating economic growth or
emission abatement is the better way to reduce impacts. Indeed, Tol and Dowlatabadi (2001)
and Tol and Yohe (2006) argue that the economic growth foregone by stringent abatement
more than offsets the avoided impacts of climate change, at least for malaria, while Tol
(2005b) shows that development is a cheaper way of reducing climate-change-induced
malaria than is emission reduction.
The agreement between the studies is remarkable if one considers the diversity in methods.
The studies of Fankhauser, Hope, Nordhaus, and Tol all use the enumerative method:
‘physical’ impact estimates are obtained one by one, multiplied with its price, and added up.
Mendelsohn’s work is based on direct, empirical estimates of the welfare impacts; this is still
done per sector, but physical modelling and benefit transfer are avoided. Nordhaus (2006)
uses empirical estimates of the aggregate economic impact, while Maddison (2003) looks at
patterns of consumption. Rehdanz and Maddison (2005) also empirically estimate the
aggregate impact, but use self-reported happiness as an indicator. The variety of methods
enhances confidence, not in the individual estimates, but in the range.
The shortcomings of the estimates are at least as interesting. Welfare losses are approximated
with direct costs (see below). In the enumerative studies, impacts are assessed independently
of one another, even if there is an obvious overlap as between water resources and agriculture.
Estimates are often based on extrapolation from a few detailed case studies. Valuation is
based on benefit transfer. Realistic modelling of adaptation is problematic. Many impacts are
unquantified (see below). The uncertainties are unknown – only 4 of the 14 estimates in Table
1 have some estimate of uncertainty. These problems are gradually solved, but progress is
slow. Indeed, the above list of caveats is similar to those in Fankhauser and Tol (1996, 1997).
2.2.
Marginal costs
Although the number of studies of the total costs of climate change is small, a larger number
of studies estimate the marginal costs. The marginal damage cost of carbon dioxide is defined
as the net present value of the incremental damage due to an infinitesimally small increase in
carbon dioxide emissions. If this is computed along the optimal trajectory of emissions, the
marginal damage cost equals the Pigou tax. Marginal damage cost estimates derive from total
cost estimates – the fact that there are more estimates available, does not imply that we know
more about the marginal costs than we do about the total costs. In fact, some of the total cost
estimates (Maddison, 2003; Mendelsohn et al., 2000a,b; Nordhaus, 2006; Rehdanz and
Maddison, 2005) have yet to be used for marginal cost estimation, so that the empirical basis
is actually smaller.
Tol (2005a) reviews 103 estimates from 28 studies. A number of new studies have appeared
since (Ceronsky et al., 2005; Downing et al., 2005; Guo et al., 2006; Hope, 2006; Wahba and
Hope, 2006) – all in response to the faux pas of HM Treasury (Clarkson and Deyes, 2002; cf.
Pearce, 2003). Tol (2005a) also overlooked the older studies of Nordhaus (1982) and Haradan
(1992, 1993), and the papers of Cline (2004), Hohmeyer (2004), Hope (2003, 2005), Link and
Tol (2004), Manne (2004), Uzawa (2003) appeared or came to my attention. There are now
210 estimates from 49 studies.
Tol (2005a) combines the estimates to a joint probability density function (PDF), assuming
that all estimates that do not report some measure of uncertainty have the same coefficient of
variation. This assumption emphasizes lower estimates at the expense of higher ones.
Therefore, Figure 1 shows the PDF of the best guesses, weighted by the quality of the study
and the importance that the authors attach to a particular estimates; cf. Tol (2005a) for details.
According to Figure 1, there is a 2% chance that the marginal damage cost is less than $0/tC,
a 54% change that it is less than $25/tC, a 68% chance that it is less than $50/tC, an 81%
chance that it is less than $100/tC, and a 95% chance that it is less than $250/tC. If only those
estimates are included that use a pure rate of time preference of 3%, then the estimate lies
below $100/tC with virtual certainty (99.98%), and it lies below $15/tC with a 50% chance. If
the pure rate of time preference is 0%, there is a 17% chance that the estimate lies below
$50/tC, and a 26% chance that it is greater than $250/tC. There is no chance that the marginal
cost is negative with even a 1% pure rate of time preference. Partly, this demonstrates the
power of discounting. 5 However, a high discount rate also dampens the uncertainty of future
development and climate; and it may be that authors who advocate lower discount rates would
also be more alarmed about climate change.
Figure 1 also shows the difference between all studies and the studies that do not use equity
weighting (cf. Azar and Sterner, 1996; Fankhauser et al., 1997, 1998). Equity weighting tends
to increase the marginal damage cost estimate, as the impacts on poorer, more vulnerable
regions attain greater weight. The chance that the marginal damage cost is less than $25/tC
($50/tC) rises to 64% (75%) if equity-weighted estimates are excluded.
This highlights that climate change is an ethical issue. Emissions of one generation cause
problems for the next generations, and richer countries emit more while poorer countries
suffer more damage. In an academic study, using lower discount rates or equity weights is
straightforward. In reality, decision makers do not necessarily care that much about other
generations and faraway lands (cf. Schelling, 1992, 1995).
2.3.
Indirect and higher order effects
The literature reviewed above is limited to estimates of the direct costs. The direct cost equals
price times quantity. This is a reasonable approximation of the welfare impact of small
changes. However, if the quantity change were larger, one would need to look at price
changes too, as well as at the implications for other markets. Studies about the general
equilibrium effects of climate change are now emerging. In addition, climate change may
have an effect on development as well.
General equilibrium studies of the effect of climate change on agriculture have a long history
(Kane et al., 1992; Fischer et al., 1993, 1996; Darwin et al., 1995; Tsigas et al., 1996).
Studies show that market adaptation matters, and may even reverse the sign of the initial
impact estimate. General equilibrium models have now entered other areas as well. Bosello et
al. (2004) and Darwin and Tol (2001) show that sea level rise would change production and
consumption in countries that are not directly affected. Ignoring the general equilibrium
effects leads to small negative bias in the global welfare loss, but differences in regional
welfare losses are much greater and may be negative as well as positive. Similarly, Bosello et
al. (2006) show that the direct costs are biased towards zero for health, while Berrittella et al.
(2006) emphasize the redistribution of impacts on tourism through markets.
Generally, richer countries are less vulnerable to climate change than are poorer countries (see
above). A cross-sectional analysis of per capita income and temperature may suggest that
5
Some recent studies (Nordhaus and Boyer, 2000; Newell and Pizer, 2003, 2004; Guo et al., 2006) use declining
discount rates, as advocated by Gollier (2002a,b) and Weitzman (2001). Declining discount rates lead to higher
(lower) marginal damage costs estimates than if the discount rate is held constant at its initial high (eventual low)
level.
people are poor because of the climate (Nordhaus, 2006; van Kooten, 2004; see below for
further discussion). This would suggest that warming would cause economies to shrink or
grow slower. This would increase the damages of climate change. As poverty implies higher
impacts, this would drag the economy down further.
Tol (2003) finds that the utility equivalent of the impacts of climate change may be infinitely
negative (see also Yohe, 2003). The mechanism is that climate change slows economic
growth, which increases impacts; this negative feedback eventually reverses economic growth
and drives the economy to subsistence level. The welfare loss may be infinite. However, as
shown in Fankhauser and Tol (2005) and Tol (forthcoming), only very extreme parameter
choices would imply such a scenario. 6 An extreme scenario would dominate other, less
extreme scenarios only under particular assumptions about utility and welfare (Tol, 2003) and
about international aid (Tol and Yohe, 2005). While these assumptions are defensible from an
academic perspective, they do not seem to be applicable in the real world.
Furthermore, one should not over-interpret cross-sectional analyses of dynamic processes.
The work by Nordhaus (2006) and van Kooten (2004) explicitly relates to climate change, but
other papers investigate the relationship between geography and development (Gallup et al.,
1999; Masters and McMillan, 2001). Easterly and Levine (2003) shows convincingly that the
conclusion of Gallup et al. (1999) are not robust, and that institutions are a better explanation
of income difference than is geography and climate. Acemoglu et al. (2002) reach the same
conclusion. However, Acemoglu et al. (2001) argue for climate as a root cause of
development, via the route of the mortality of European settlers. Future climate change will
not affect history, though.
The demo-economic models that follow Galor and Weil (1999) also put mortality 7 centre
stage. In their models, the difference between Malthusian stagnation and exponential growth
is determined by the quality-quantity trade-off for children, which is partly driven by infant
mortality. A risk-averse parent would opt for more children, so as to increase the chance of
old-age care; a large number of inadvertently surviving children would reduce the money
spent on their education. These children would become poor adults, unable to afford health
care for their offspring. Should climate change increase the prevalence of malaria and
diarrhoea, then the poverty trap would widen. This mechanism has not been studied for
climate change.
2.4. Missing impacts
The impacts of climate change that have been quantified and monetised include the impacts
on agriculture and forestry, water resources, coastal zones, energy consumption, air quality,
and human health. Obviously, this list is incomplete. Also within each impact category, the
assessment is incomplete. Studies of the impacts of sea level rise on coastal zones, for
instance, typically omit saltwater intrusion in groundwater (Nicholls and Tol, 2006).
Some of the missing impacts are most likely negative. Diarrhoea impacts have been
quantified recently (Link and Tol, 2004). Like malaria, diarrhoea is a disease that is driven by
poverty but sensitive to climate. Including diarrhoea tightens the link between development
and climate policy. Increasing water temperatures would increase the costs of cooling power
plants (Szolnoky et al., 1997). Redesigning urban water management systems, be it for more
of less water, would be costly (Ashley et al., 2005), as would implementing the safeguards
6
Kemfert (2002; see also Roson and Tol, 2006, and Kemfert, 2006) finds large dynamic impacts, but she
assumes that climate change impacts crowd out investment; this assumption is questionable for market impacts,
and indefensible for non-market impacts.
7
albeit of infants, not of grown settlers from distant places
against the increased uncertainty about future circumstances. Roads and bridges would suffer
from weather conditions for which they were not designed; this would imply either disruption
of traffic or expensive retrofits. Extratropical storms may well increase, leading to greater
damage and higher building standards (Dorland et al., 1999). Expenditures on these things are
relatively small. Even if climate change would double or triple the cost, the impact would be
small. Ocean acidification would reduce marine biodiversity, and may well harm fisheries
(Kikkawa et al., 2004). Ocean fisheries are only a small, and declining fraction of GDP, while
there are ready substitutes for wild fish protein (notably fish farming). The value of
biodiversity is unclear (see below).
Other missing impacts are probably positive. Higher wind speeds in the mid-latitudes would
decrease the costs of wind and wave energy (Breslow and Sailor, 2002; Harrison and Wallace,
2005). Less sea ice would improve the accessibility of arctic harbours, would reduce the costs
of exploitation of oil and minerals in the Arctic, and may even open up new transport routes
between Europe and East Asia (Wilson et al., 2004). Warmer weather would reduce
expenditures on clothing and food, and traffic disruptions due to snow and ice (Carmicheal et
al., 2004). Also in these cases, the impact of climate change is likely to be small relative to
the economy.
Some missing impacts are positive in some places, and negative in others. Tourism is an
example. Climate change may well drive summer tourists towards the poles and up the
mountains (Hamilton et al., 2005a, b). People, however, are unlikely to change the time and
money spent on holiday making. The effect is a redistribution of tourist revenue (Berrittella et
al., 2006). The global impact is close to zero, but regional impacts are measured in tens of
billions of dollars – positive in temperate, rich countries, and negative in tropical, poor
countries. This exacerbates the already skewed distribution of climate impacts. Some ski
resorts may go out of business, and others would need expensive snowmaking equipment
(Elsasser and Buerki, 2002; Scott et al., 2003). Other ski resorts would profit from the
reduced competition. Although regional impacts may be substantial, at the global scale
positives and negatives cancel.
Other impacts are simply not known. Some rivers may see an increase in flooding, and others
a decrease (Kundzewicz et al., 2005). At the moment, only a limited number of rivers have
been studied in detail, and it is unclear how to extrapolate to other rivers. It is clear though,
that land use and water management may greatly increase or reduce impacts. Although river
floods wreak substantial havoc and damages of a single event can reach substantial numbers,
average flood damage is in fact small relative to the economy (Tol et al., 2003). Tropical
storms do more damage, although a substantial share of the impact is due to bad planning
rather than bad weather (Burton et al., 1993). Nonetheless, tropical storms may prevent
capital accumulation and the plantation of lucrative tree crops such as banana (Ennos, 1997;
Mulcahy, 2004). Unfortunately, it is not known how climate change would alter the
frequency, intensity, and spread of tropical storms (McDonald et al., 2005; Pielke et al.,
2005).
3.
Reasons for concern / Gaps in knowledge
3.1.
Biodiversity loss
Climate change would have a profound impact on nature. The distribution of plants and
animals is partly determined by temperature and precipitation; while organisms that are
relatively robust to climate change may be affected through competitors, parasites, pests,
preys, and predators that are more sensitive to climate change. Most species would shift their
distribution and change their abundance; this implies local extinctions and new introductions.
Some species would be unable to adapt fast enough and go extinct, globally (Gitay et al.,
2001). From an economic policy perspective, there are three major problems.
First, there are few quantitative studies of the impacts of climate change on ecosystems and
biodiversity. Large-scale dynamic vegetation models were build to study the carbon cycle,
and have a very crude resolution for plant species (20 types at most) while ignoring animals
altogether (Sitch et al., 2003). Studies which are rich in species detail are few in number, and
confined to small groups of species and at best continental in scale (Burkett et al., 2005;
Harrison et al., 2003; Termansen et al., 2006). The reasons are that quantitative ecology is
still in its infancy, and that there are very many species to be modelled. Although ecosystem
impacts may be important, there is little hard material to go by.
Second, climate is not the only thing that is changing. Changes in land use, changes in the
nutrient cycles, alien invasions and acidification all have large-scale and profound effects on
nature. These effects are synergistic rather than additive. This hampers interpretation of past
observations (and hence model building), complicates making projections of the future, and
muddles the attribution of impacts to causes (Parmesan and Yohe, 2003; Root et al., 2003).
Third, valuation of ecosystem change is difficult. Great strides have been made in the
valuation literature, but methods and applications have grown more specific, focussing on a
single issue in a particular locality (e.g., Champ et al., 2003). The benefit transfer literature
reinforces this, demonstrating that values are heterogeneous and contextual (Ready et al.,
2004). Wide-spread change that is hard to detect and to attribute is beyond current valuation
methods. Furthermore, climate-change-induced ecosystem change is unlikely to be marginal –
a challenge for economic methods in general.
3.2. Extreme climate scenarios
Extreme climate scenarios are widely considered to be a main reason for concern about
climate change. Examples are a shutdown of the thermohaline circulation (e.g., Marotzke,
2000), a collapse of the West-Antarctic Ice Sheet (Vaughan and Spouge, 2002), and massive
releases of methane from the permafrost (e.g., Harvey and Huang, 1995). These scenarios
have a number of things in common. First, they would lead to rapid changes in the natural
system. Second, impacts have hardly been studied. Third, the mechanism is only partially
understood. Fourth, the probability is unknown but probably low.
Rapid climate change would be a problem, as there would be little time to adapt. This
suggests that impacts would be large, but there has been little research. This is partly because
output data is few and not readily available from climate models on extreme climate change.
Another reason is that impact models have been designed for more gradual climate change.
Nicholls et al. (2005), for instance, had to go back and reformulate their models of erosion
and coastal protection and redo the input before considering sea level rise faster than 1 metre
per century. That study reports an order of magnitude increase in the impacts of sea level rise
should the West-Antarctic Ice Sheet collapse in less than 200 years. If adaptation is more
difficult than assumed in the model (as suggested by Olsthoorn et al., 2005), impacts may be
even be worse. Link and Tol (2004) estimate the impacts of a shutdown of the thermohaline
circulation. In their scenario, a THC shutdown slows global warming, at least over land.
Unsurprisingly, they report benefits of a THC shutdown. Working with a finer spatial
resolution and a most drastic scenario, Link and Tol (2006) find a small negative effect on the
global scale, but much larger negative effects in some countries. Ceronsky et al. (2005) also
run more drastic scenarios than do Link and Tol (2004), also finding negative impacts of
abrupt climate change.
The policy implications are unclear. In a decision analysis, what matters is impact times
probability. It is hard to estimate probabilities because the mechanisms are still unclear, and
measurements are difficult. The thermohaline circulation, for instance, depends on the vertical
transport of water to great depth, which is hard to observe (Baehr et al., forthcoming; Keller et
al., forthcoming). The fate of the West-Antarctic Ice is determined at the interface of the ice
and the bedrock on which it rests (Vaughan and Spouge, 2002), that is, far below the surface.
The uncertainties about the mechanisms also hamper policy analysis in another way: It is not
clear whether greenhouse gas emission abatement would reduce the probability of a WAIS
collapse or a THC shutdown. It may be that these things would happen anyway, or that the
threshold has been crossed already, and even that climate change would reduce the probability
of collapse. These questions are firmly in the realm of the natural science, and firm policy
conclusions cannot be drawn before these questions are answered. The few available policy
analyses (Baranzini et al., 2003; Gjerde et al., 1999; Guillerminet and Tol, 2005; Keller et al.,
2004) therefore focus on methodological issues.
3.3. Violent conflict
Research into the determinants of violent conflict concludes that resource scarcity is at best a
contributing factor to, and never a cause of war (Alesina and Spolaore, 2005; Collier and
Hoeffler, 1998, 2005; Homer-Dixon, 1991, 1992; Homer-Dixon et al., 1993; Maxwell and
Reuveny, 2000).
The corollary is that climate-change-induced resource scarcity would not lead to war either,
although it may intensify pre-existing conflicts. It is therefore impossible to estimate the
impact of climate change on violent conflict without a scenario with background conflicts.
Such scenarios do not exist; all future scenarios for climate change are nice and peaceful
(Nakicenovic and Swart, 2001). Constructing scenarios of conflict would be hard, but not
impossible; such scenarios would necessarily be stochastic (Geller and Singer, 1998). Clearly,
an intensification of conflict would be something to worry about.
Despite the conclusions of studies quoted above, it is possible to imagine a scenario in which
climate change does cause violent conflict. One example may be prolonged drought, perhaps
in the Horn of Africa (Held et al., 2006), followed by mass migration. There are three reasons
to assume that this is unlikely. First, migration results from a complex of push and pull
factors, not from a single push factor (McGregor, 1994; McLeman and Smit, 2006). Second,
drought is only a real problem for the poor; a scenario like this would happen only if warming
and drying are faster than development. If not, food imports (Reilly and Schimmelpfennig,
1999) or desalination (Zhou and Tol, 2005) may be the preferred options. Third, drought is a
slow-onset disaster. It may exhaust people before they move. Poor and exhausted people are
unlikely to take up arms, and if they do, they are probably not very effective. The human
suffering would be substantial nonetheless.
A potentially more serious example is rapid sea level rise in the major deltas of Asia and
Africa. Coastal plains are often fertile and hence densely populated (Nicholls and Small,
2002). Without coastal protection, inundation, erosion and saltwater intrusion would drive
many people to higher grounds (Nicholls and Tol, 2006). They may resettle peacefully, or
start quarrelling with their new neighbours. One can speculate about the consequences of
large-scale migrations today. In West Africa, for instance, the situation is already so tense that
additional refugees are unlikely to do any good – but note that the coast of Cameroon, Gabon
and Nigeria are most vulnerable to sea level rise. Similarly, forced migration of large numbers
of Bengali from the coastal plain to the hills of northern Indian and Bangladesh would not be
without problems either, and may even escalate to nuclear war. However, these impacts will
not be on today’s world. Sixty-four years ago, Western Europe was at war. In 2070, South
Asia and West Africa may be stable and prosperous.
Terrorism is another unknown. Sea level rise will lead to the evacuation of a number of
islands (Nicholls and Tol, 2006). Forcibly moved populations may harbour resentment.
Sometimes, this is very strong, and a small minority may turn violent (e.g., van Amersfoort,
2004). It may well be that a Maldivian terrorist will try and blow up the headquarters of
ExxonAramco. As with the other scenarios above, one can think of the plot and make it sound
plausible. With the current state of conflict research, however, it is impossible to compute,
even bound probabilities and intensities.
As a further complication, although climate change may contribute to violent conflict and
terrorism, it does not follow that slowing climate change is the best response. Addressing the
other roots of violence may be easier or cheaper, and would have substantial co-benefits.
3.4.
The very long term
During this century, the world will probably run out of conventional oil and gas, the two most
important energy sources of today (Moomaw et al., 2001). If conventional oil and gas will be
replaced by renewable and nuclear energy sources, there will not be much of a climate
problem. If unconventional oil and gas take over, climate change will continue. If coal takes
over, climate change will be substantial (Nakicenovic and Swart, 2001). Energy is an essential
input to the economy, so the resource problem will have to be solved. This requires a
complete overhaul of the energy sector. Solving the climate problem also requires a complete
overhaul of the energy sector (Richels and Edmonds, 1995). Given the scale of the energy
sector and the longevity of its capital stock, it would make sense to overhaul the energy sector
only once, and solve the resource problem and the climate problem in one go. Perhaps, the
energy security problem can be solved at the same time.
Put differently, the energy system is heading towards to a bifurcation. There are various
solutions to the resource problem: coal; unconventional oil and gas; or renewables and
nuclear. If climate change is enough of a concern, the future of energy is renewable and
nuclear. From this perspective, we do not want to know the marginal costs of carbon dioxide
emissions. Instead, we want to know the difference in impacts between three radically
different futures, and compare it to the difference in energy costs between the alternative
futures. Unfortunately, we do not know the difference in impacts.
The first problem is that most of the tools of economics are designed for analysis at the
margin, that is, small change. That is adequate for most problems, where policy makers
indeed tinker at the margin. It may not be adequate for climate change.
The second problem is that most static impact analyses are for 2xCO2 only, while most
dynamic impact studies stop at 2100. The choice between a renewable and nuclear future and
a coal future is the choice between 2xCO2 on the hand and 4x, 6x, perhaps 8xCO2 on the
other. 8 Because of the inertia in the energy and climate systems, these scenarios will be still
be relatively close to one another in 2100, but the gap would widen between 2100 and 2500.
We have not even begun to study the impacts of climate change in the very long term. 9 If
2xCO2 leads to an equilibrium warming of 2.5°C, then 8xCO2 would imply 7.5°C warming –
radiative forcing and warming are logarithmic in CO2 concentrations. Sea level rise would not
stop at 2-3 m, but may go up to 10 m or so. Using Nordhaus’ (1994a) quadratic damage
8
Current estimates have that there is not enough fossil fuel to drive the atmospheric concentration of carbon
dioxide much above 2200 ppm (Moomaw et al., 2001)
9
Indeed, only a few climate change scenarios have been published (e.g., Lenton et al., 2006).
function, 2.5°C warming would lead to a welfare loss equivalent to a 1.3% income loss; 7.5°C
warming would lead to a damage of 11.7% of world income – but only in a distant future.
Does the difference justify the extra costs of renewables, nuclear, and carbon capture and
storage? Answering that question requires redoing this back-of-the-envelope calculation with
proper carbon cycle, climate and impact models, based on proper scenarios of development in
the long run.
7.
Discussion and conclusion
This paper reviews what is known and what is not known about the economic impacts of
climate change. What is known suggests that climate change is a problem that requires a
serious effort to reduce greenhouse gas emissions. However, the impact estimates do not
support drastic action. The marginal damage costs of carbon dioxide lies probably below
$50/tC – a tax like this would stimulate energy efficiency improvements but only minor fuel
switching. Higher estimates require that the discount rate is lowered below what is common,
or that an uncharacteristic weight is placed on the plight of developing countries.
What is known is only a small part of what matters. Many climate change impacts have been
identified but not estimated, and there are undoubtedly yet to be identified impacts too. Some
of these impacts are clearly negative, and some clearly positive. It is impossible to say with
any kind of certainty whether current impact estimates have a positive or a negative bias. Yet,
countries like Canada, Finland, Iceland, Norway and Sweden are cold but prosperous.
Warming would reduce costs and lift constraints and thus accelerate economic growth, but it
is hard to imagine that warming would unleash very rapid growth. At the same time, tropical
countries clearly suffer from violent storms, prolonged droughts, and the presence to tropical
diseases. Further warming would not be good, and subjecting more places to such conditions
cannot be positive either. Although not quantified, one can more easily imagine a scenario in
which warming has dramatic consequences than a scenario is warming has large positive
effects. So, at the least, the great many unknowns imply that the uncertainty is skewed to the
negative; and that, if anything, current impacts estimates are positively biased. This suggests
that greenhouse gas emission reduction should be more stringent than suggested by costbenefit analysis.
Policy should not fly blind, however. If the above diagnosis is correct, it would most of all
call for a vigorous research programme. Although some countries propose to spend billions of
dollars on emission reduction, and other countries pretend that climate change is a problem
that can safely be ignored, little effort is spent on supporting these courses of action by
research into whether climate change is a serious problem or not. Climate science is wellfunded, but climate impact research much less so. Furthermore, the climate change impact
research community is focussed on incremental improvements on what is known, ignoring the
big unknowns. The number of senior economists who do serious research on the impacts of
climate change can be counted on two hands. This is in no proportion to the alleged
seriousness of the climate change problem.
Future research should focus on:
•
the quantification of uncertainties;
•
the estimation of missing impacts;
•
the interactions between impacts of climate change;
•
the higher-order economic effects of the impacts of climate change;
•
ecosystem change and biodiversity loss and their welfare implications;
•
the impact of extreme climate scenarios;
•
violent conflict; and
•
the impact of climate change in the very long term.
This research agenda is not limited to the discipline of economics, but economists can and
should contribute to every single point. Only after answering these questions we can with
some confidence state that climate change is not a dramatic problem or justify the drastic
emission reductions proposed by some policy makers.
Acknowledgements
Discussions with Steve Pacala, Rob Socolow and Bob Williams helped to shape this
particular paper. My knowledge on the subject has greatly benefited from discussions with
Sam Fankhauser, David Maddison, David Pearce, Joel Smith, and Gary Yohe, and from the
series of Snowmass workshops masterly organised by Susan Sweeney and John Weyant.
Financial support by the Hamburg University Innovation Fund, the Princeton Environmental
Institute, and the ESRI Energy Policy Research Institute is gratefully acknowledged.
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0.9
0.8
0.7
no equity weighting
all
3% PRTP
1% PRTP
0% PRTP
fraction
0.6
0.5
0.4
0.3
0.2
0.1
0.0
<0
0-5
5-10
10-15
15-20
20-25
25-30
30-35
35-40
40-45
45-50
>50
dollar per tonne of carbon
0.9
no equity weighting
all
3% PRTP
1% PRTP
0% PRTP
0.8
0.7
fraction
0.6
0.5
0.4
0.3
0.2
0.1
0.0
<0
0-25
25-50
50-75 75-100
100125
125150
150175
175200
200225
225250
>250
dollar per tonne of carbon
Figure 1. Histogram of the best estimates of the marginal damage costs of carbon dioxide
emissions, in bins of $5/tC (top panel) and $25/tC (bottom panel), for the entire sample and
various subsamples.
Table 1. Impact estimates of climate change; numbers in brackets are either standard deviations or confidence intervals.
Study
Nordhaus (1994a)
Nordhaus (1994b)
Warming
3.0
3.0
Fankhauser (1995)
Impact
Minimum
Maximum
2.5
-1.3
-4.8
(-30.0 to 0.0)
-1.4
-4.7
China
-0.7
Tol (1995)
2.5
-1.9
-8.7
Africa
-0.3
Nordhaus and Yang
(1996)a
Plambeck and Hope
(1996)a
Mendelsohn et al.
(2000)a,b
Nordhaus and Boyer
(2000)
Tol (2002)
2.5
-1.7
-2.1
2.5
-2.5
(-0.5 to –11.4)
0.0
0.1
-1.5
-8.6
(-0.6 to -39.5)
-3.6
-0.5
-3.9
Developing
countries
Asia (w/o China)
2.3
(1.0)
-0.1
-0.4
-4.1
(2.2)
-14.6
-23.5
0.9
(-0.2 to 2.7)
-0.9
(0.1)
-2.6
(-0.4 to 10.0)
2.5
2.5
1.0
Maddison (2003)a,c
Rehdanz and Maddison
(2005)a,c
Hope (2006)a
2.5
1.0
Nordhaus (2006)
2.5
a
2.5
Africa
Africa
Africa
South America
Sub-Saharan Africa
Asia (w/o China)
Note that the global results were aggregated by the current author.
The top estimate is for the “experimental” model, the bottom estimate for the “cross-sectional” model.
c
Note that the national results were aggregated to regions by the current author for reasons of comparability.
b
0.9
Eastern Europe and the
former Soviet Union
Eastern Europe and the
former Soviet Union
Former Soviet Union
0.0
(-0.2 to 1.5)
4.0
1.7
0.7
Eastern Europe and the
former Soviet Union
Eastern Europe and the
former Soviet Union
Russia
3.7
(2.2)
2.5
12.9
0.3
(-2.5 to 0.5)
Western Europe
Western Europe
South Asia
Eastern Europe and the
former Soviet Union
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(lxxviii) This paper was presented at the Second International Conference on "Tourism and Sustainable
Economic Development - Macro and Micro Economic Issues" jointly organised by CRENoS (Università
di Cagliari and Sassari, Italy) and Fondazione Eni Enrico Mattei, Italy, and supported by the World Bank,
Chia, Italy, 16-17 September 2005.
(lxxix) This paper was presented at the International Workshop on "Economic Theory and Experimental
Economics" jointly organised by SET (Center for advanced Studies in Economic Theory, University of
Milano-Bicocca) and Fondazione Eni Enrico Mattei, Italy, Milan, 20-23 November 2005. The Workshop
was co-sponsored by CISEPS (Center for Interdisciplinary Studies in Economics and Social Sciences,
University of Milan-Bicocca).
(lxxx) This paper was presented at the First EURODIV Conference “Understanding diversity: Mapping
and measuring”, held in Milan on 26-27 January 2006 and supported by the Marie Curie Series of
Conferences “Cultural Diversity in Europe: a Series of Conferences.
2006 SERIES
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