8.4.5 Critical Factors Affecting the Timing of Emissions Reductions: The Role
of Technological Change
As pointed out by Grubb (1997), there are several key assumptions imbedded
in the energy-economy models that influence the shape of the least-cost mitigation
pathway. For a pre-determined target, these relate to the determinants of technical
change; capital stock turnover and the inertia in the energy system; discounting;
and, the carbon cycle. When the target is uncertain, they include in addition
the probability attached to each target and risk aversion (see Chapter
10) which tend to favour a more aggressive departure from current trends.
The discount rate will not be discussed because it is less important in cost-efficiency
frameworks (when the target is pre-determined) than in a cost-benefit one (when
the discount rate reduces the weight of future environmental impacts, see Chapter
10). Neither are the very few studies discussed which try to assess different
benefits in terms of environmental co-benefits of reducing GHG emissions presented.
Wigley et al. (1996), for example, show pathway-related differentials
up to 0.2°C in global mean temperature and 4cm in global mean sea-level
(by 2100) for the WGI and WRE 550 stabilization pathways. See Chapter
10 for an elaboration of these timing issues. This part will rather insist
on the key features of technical change that are numerically of utmost importance.
To the extent that the cost of reducing emissions is lower in the future than
at present, the overall cost of stabilizing the CO2 concentration
is less if emissions mitigation is shifted towards the future. This shift occurs
in all models. The extent of the shift that minimizes the cost of limiting the
concentration of atmospheric CO2 depends, at least in part, on the
treatment of technological change. Without technological change, the problem
is simple and the results of Hotelling (1939) apply. With endogenous technological
change, the problem becomes more complex.
This discussion of the determinants of technological change must begin with
the acknowledgement that no adequate theory of endogenous technological change
exists at present. Many researchers have contributed to the field, but the present
state of understanding is such that present knowledge is partial and not necessarily
fully consistent. Although no complete theory of technological change exists,
two elements have been identified and explored in the literature: induced technological
change (ITC) and learning-by-doing (LBD). Work by Ha-Duong et al. (1997),
Grubb et al. (1995), Grubb (1997), and Kypreos and Barreto (1999) examined
the implication of ITC, LBD, and inertia within the context of uncertainty and
an imperative to preserve the option of concentration ceilings such as 450ppmv.
They conclude that emissions mitigation can be shifted from the future towards
the present under appropriate circumstances.
Goulder and Mathai (1998) also explore how the effect on timing depends on
the source of technological change. When the channel for technological change
is R&D, ITC makes it preferable to concentrate more abatement efforts in
the future. The reason is that technological change lowers the costs of future
abatement relative to current abatement, making it more cost-effective to place
more emphasis on future abatement. However, when the channel for technological
change is LBD, the presence of ITC acts in two opposite directions. On the one
hand, ITC makes future abatement less costly but, on the other hand, there is
an added value to current abatement because such abatement contributes to experience
or learning and helps reduce the costs of future abatement. Which of these two
effects dominates depends on the particular nature of assumptions and firms.
In recent years, there has been a good deal of discussion about the potential
for ITC (e.g., Anderson et al., 1999). Proponents argue that such changes
might substantially lower, and perhaps even eliminate, the costs of CO2
abatement policies. These discussions have exposed very divergent views as to
whether technological change can be induced at no cost, or whether a resource
cost is involved. For example, in a 1995 article, Porter and van der Linde (1995)
contend that properly designed regulation can trigger innovation that may partially
or more than fully offset the costs of compliance. Indeed, they argue that firms
can actually benefit from more stringent regulation than that faced by their
competitors in other countries. However, in an accompanying article, a strongly
contrary view is put forward by Palmer et al. (1995). Examining available
data, they found that such offsets pale in comparison to expenditures for pollution
abatement and control.
188.8.131.52 ITC through Dedicated R&D
Including R&D driven ITC in climate mitigation models leads to ambiguous
results in terms of time profile and tax level in a cost-benefit framework In
a cost-effectiveness framework, the optimal tax is lower in the case with R&D
driven ITC and has to be set up early even if the effective resulting abatement
shifts from the near-term to the more distant future. If there are market failures
in the R&D market (e.g., knowledge spillover), then subsidies for R&D
are justified as it enhances social welfare and raises the abatement level (Goulder
and Schneider, 1999; Weyant and Olavson, 1999; Goulder and Mathai, 2000).
However, R&D driven-ITC can reduce the gross costs of a carbon tax under
special circumstances. Specifically, if R&D has been substantially over-allocated
towards the fossil fuel industries prior to the imposition of a carbon tax,
the carbon tax can reduce this allocative inefficiency and, as a result, its
costs can be quite low or even negative. A substantial prior misallocation towards
carbon-intensive industries could occur if there were prior subsidies towards
R&D in the fossil fuel industries (with no comparable subsidies in other
industries), or if there were substantial positive spillovers from R&D in
non-carbon industries (with no comparable spillovers in the fossil fuel industries).
Under other plausible initial conditions, however, R&D driven-ITC raises,
rather than lowers, the net social costs of a given carbon tax because of the
crowding out of R&D from other sectors; to put it clearly the tax level
for a given abatement is lower than under the hypothesis of exogenous technical
change and part of this decrease is offset when all the general equilibrium
effects are accounted.
The same model has been employed to compare the costs of achieving a given
abatement target through carbon taxes and R&D subsidies (Schneider and Goulder,
1997; Goulder and Schneider, 1999). If there are no spillovers to R&D, the
least-cost way to reach a given abatement target is through a carbon tax alone.
The carbon tax best targets the externality from the combustion of fossil fuels
related to climate change, and thus is the most cost-effective. However, if
there are spillovers to R&D, the least-cost way to achieve a given abatement
target is through the combination of a carbon tax and R&D subsidy. If spillovers
are present, there is a market failure in the R&D market as well as a (climate
change related) market failure associated with the use of carbon. Two instruments
(the R&D subsidy and the carbon tax) are needed to address the two distinct
market failures most efficiently. In general, a R&D subsidy by itself does
not offer the least-cost approach to reducing carbon emissions. Results from
this model are highly sensitive to assumptions about the nature and extent of
knowledge spillovers. Further empirical work that sheds light on these spillovers
would have considerable value.