It is an
occasional fallacy that we can have a successful market-based policy for our
energy needs and for tackling climate problems and that this can always be
easily reconciled with continuous downward trends in energy prices. Markets and prices are essential components
of an effective energy policy, especially one designed to attack the large
hidden costs of environmental damage and climate consequences. However the
essence of markets is that they allow costs and prices to go up as well as
down. Reflecting environmental costs in energy markets helps in stimulating low
carbon investment, in promoting low carbon operation of the capital stock, and
in encouraging lower and less wasteful consumption. But that will on occasions
mean that prices rise as part of the natural process, market or otherwise, by
which societies adjust to resource limitations and other constraints.
The Case for Carbon Pricing
A general and common sense
principle of economics is that if commodities are produced and sold at a price
below the cost of producing them, then this is a prime indication that
something is wrong. Fortunately market economies do not usually allow this to
happen. Planned economies in which
prices are set without reference to cost are a different matter. That is why so
much of the former Soviet economies was characterised by waste, inefficiencies
and shortages.
But market economies are also
in trouble when the largest costs are not carried directly by either producers
or consumers, but are imposed on the world at large. This prevents an efficient
allocation of resources and will reduce human welfare. That is what is
happening with fossil fuels and CO2 emissions. It is an annoying and
inconvenient truth that: “if damaging externalities
are not internalised in prices, there is no basis to assume that free markets
and free trade will improve human welfare”.[1]
In other words market economies that fail to deal with environmental
costs will also suffer the historically documented weaknesses of the Soviet
system, with excessive and wasteful use of energy produced in an
environmentally destructive way, inefficient choice between technologies, and
ultimately a shortage of the common good that we call environment.
When an activity is damaging
to society, one option is to prohibit or limit it; we try to do this with
dangerous drugs, excessive speed on our roads or various forms of water pollution,
usually through regulation but occasionally through a price mechanism. Arguably,
“health” taxes on tobacco or sugar also fall in this category. We are beginning
to understand, collectively and globally, the scale of our problem with burning
fossil fuels and emitting CO2. Immediate cessation may be an
impossibility, but limiting harmful CO2 emissions through a price or
tax penalty is widely seen as necessary and desirable.
The costs of not pricing
carbon
A market-based approach
that fails to incorporate adequate carbon pricing is unable to deliver low
carbon investment or even to ensure the most carbon-efficient operation of an
existing stock of plant. In other words
additional policy instruments become a necessity. This impacts on all
the main economic features of the sector – incentives for investment, true
costs against which the operation of existing plant can take place, and retail
prices that encourage economic use of resources (allocative efficiency).
The largest adverse consequence
of failure to internalise costs may be the effect on low carbon investment incentives,
such as the failures to incentivise the carbon capture investments widely
recognised as key, at least with known technologies, to decarbonisation of the
power sector at a reasonable cost. But it
can also lead to perverse operational choices between fuels, an obvious recent
anomaly (in Northern Europe) being the closure of highly efficient gas power
stations, while coal stations continue to operate baseload due to cheap coal.
To a significant degree this can be blamed on deficiencies in the EU
ETS have given rise to very low carbon prices. In climate terms this
is an expensive anomaly, even though the immediate financial implications for
the utilities were relatively trivial.
Recent UK experience is an
illustration of the scale of the issue at the operational level. Between 2009
and 2012 the substitution of coal for gas, induced by changes in gas/coal price
relativities, increased UK coal consumption by about 15 million tonnes. This
increased annual CO2 emissions by around 20 million tonnes, to which past Treasury
guidelines [2] might
have attached a notional “social cost of carbon” value of around £ 1.2 billion.
Actual fuel savings to generators are likely to have been at most 10% of this
amount. In other words this single failure
to price carbon will, on the basis of UK Treasury guidelines, have generated a real
but hidden long term net “social cost” of up to £ 1 billion per annum over that period.
Conditions for a successful
policies towards carbon pricing
In some senses carbon
pricing is a transitional issue. Since the direction of travel is to a near
zero carbon economy, the regulation and organisation of the sector in the very
long term will not depend on carbon markets or taxes. Energy prices can then
reflect only the cost of supply from zero carbon sources. But this is a very
long term perspective. In the short and medium term, even comparatively modest
levels of carbon prices can assist attainment of cumulative emission objectives
in the timescales with which we are concerned, even if they remain insufficient
to incentivise investment.[3] An important role for carbon prices is to counteract the “rebound effect”, when higher energy
efficiency induces (through lower costs to the consumer) additional use. This
is particularly important for the heat sector, where energy efficiency
programmes are a major instrument of policy.
If the cost of CO2 emissions
is at least partly internalised, explicitly through a tax or cap and trade
regime, or implicitly in policy, then consistency matters. Inconsistent or
incomplete coverage will lead to “leakage” between sectors or geographies, with perverse effects that can drive up total emissions and damage the
competitiveness of more carbon-efficient producers. Inter alia that implies a strong argument for
regional carbon markets such as the EU ETS. The ETS has had many deficiencies
which deserve a separate comment, and needs a serious overhaul, but the
principle of a wider international market is an important one and should be
retained.
It also implies that the coverage of the policies needs to be as wide as possible in sector terms, so that it covers all fuels giving rise to carbon emissions, in all parts of the economy, and not just particular sectors. Without this condition there is again a risk of distortions.
An
example of such a potential distortion was the “twin track” approach implicit
in UK Treasury guidelines, in which carbon prices differed as between “traded”
sectors governed by the EU ETS, and “non-traded”, governed by an assumed “social
cost of carbon”.
Finally, as in shown in a fuller discussion of the power sector, it is
quite clear that carbon prices alone are unlikely to be a sufficient measure to
achieve the low carbon infrastructure investments that are a necessary part of
meeting emissions and climate related targets.
[1] This expression of the idea is acknowledged to Michael Grubb, speaking at a BIEE Climate Policy Seminar.
[2] Valuation of energy use and greenhouse gas emissions for appraisal and evaluation. October 2011. DECC and HM Treasury.
[3] €15/ tonne may be
sufficient to induce early gas for coal substitution in existing plant, for
example.
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