Silent
Majority Speaks
Rescuing
Democracy in the United Kingdom from our current Elected
Dictatorship
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Spin, not
face-to-face confrontations with the voters, is the Government's
chosen method of communication. Ordinary
people are dangerous. Ordinary people might ask a question
which throws a politician 'off message'; the Cabinet member
might reveal himself or herself to be a human being like
us, and not a programmed android. Worse still, he or she
might tell the truth.
Ann Leslie - Daily Mail, September
16, 2004
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The
Economics of Nuclear Power
Briefing
Paper 8 - March 2004
Nuclear power is
cost competitive with other forms of electricity generation, except
where there is direct
access to low-cost fossil fuels. Decreasing fossil fuel costs in
the 1990s eroded nuclear energy's previous cost advantage in many
OECD countries, but higher gas prices are now changing the picture
again.
Fuel costs for nuclear plants are a minor proportion of total generating
costs and often about one-third
those for coal-fired plants. In assessing the cost competitiveness
of nuclear energy, decommissioning and waste disposal costs are
taken into account.
Relative costs of
generating electricity from coal, gas and nuclear plants vary considerably
depending on location. Coal is, and will probably remain, economically
attractive in countries such as China, the USA and Australia with
abundant and accessible domestic coal resources as long a carbon
emissions are cost-free. Gas is also competitive for base-load power
in many places, particularly using combined-cycle plants, though
rising gas prices have removed much of the advantage.
Nuclear energy is
in many places competitive with fossil fuel for electricity generation,
despite relatively high capital costs and the need to internalise
all waste disposal and decommissioning costs. If the social, health
and environmental costs of fossil fuels are also taken into account,
nuclear is outstanding.
External
costs
The report of a major
European study of the external costs of various fuel cycles, focusing
on coal and nuclear, was released in mid 2001. It shows that in
clear cash terms nuclear energy incurs about one tenth of the costs
of coal. The external costs are defined as those actually incurred
in relation to health and the environment and quantifiable but not
built into the cost of the electricity. If these costs were in fact
included, the EU price of electricity from coal would double and
that from gas would increase 30%. These are without attempting to
include global warming.
The European Commission
launched the project in 1991 in collaboration with the US Department
of Energy, and it was the first research project of its kind "to
put plausible financial figures against damage resulting from different
forms of electricity production for the entire EU". The methodology
considers emissions, dispersion and ultimate impact. With nuclear
energy the risk of accidents is factored in along with high estimates
of radiological impacts from mine tailings (waste management and
decommissioning being already within the cost to the consumer).
Nuclear energy averages 0.4 euro cents/kWh, much the same as hydro,
coal is over 4.0 cents (4.1-7.3), gas ranges 1.3-2.3 cents and only
wind shows up better than nuclear, at 0.1-0.2 cents/kWh average.
Fuel costs are one
area of steadily increasing efficiency and cost reduction. For instance,
in Spain nuclear electricity cost has been reduced by 29% over 1995-2001.
This involved boosting enrichment levels and burn-up to achieve
40% fuel cost reduction. Prospectively, a further 8% increase in
burn-up will give another 5% reduction in fuel cost.
The
cost of fuel
From the outset the
basic attraction of nuclear energy has been its low fuel costs compared
with coal, oil and gas fired plants. Uranium, however, has to be
processed, enriched and fabricated into fuel elements, and at least
three quarters of the cost is due to enrichment and fabrication.
Allowances must also be made for the management of radioactive spent
fuel and the ultimate disposal of this spent fuel or the wastes
separated from it.
In mid 2000, the
approx. US $ cost to get 1 kg of UO2 reactor fuel:
| U3O8
:
| 8 kg x $25
| 200
|
| conversion:
| 7 kg U x
$5.5
| 38
|
| enrichment:
| 4.3 SWU x
$105
| 452
|
| fuel fabrication:
| per kg
| 240
|
| total,
approx:
| US$ 930
|
This yields 3400 GJ
thermal which gives 315,000 kWh, hence fuel cost: 0.30 c/kWh.
But even with these
included, the total fuel costs of a nuclear power plant in the OECD
are typically about a third of those for a coal-fired plant and between
a quarter and a fifth of those for a gas combined-cycle plant.
Comparing
electricity generation
For nuclear power
plants any cost figures normally include spent fuel management,
plant decommissioning and final waste disposal. These costs, while
usually external for other technologies, are internal for nuclear
power.
Decommissioning costs
are estimated at 9-15% of the initial capital cost of a nuclear
power plant. But when discounted, they contribute only a few percent
to the investment cost and even less to the generation cost. In
the USA they account for 0.1-0.2 cent/kWh, which is no more than
5% of the cost of the electricity produced.
The back-end of the
fuel cycle, including spent fuel storage or disposal in a waste
repository, contributes up to another 10% to the overall costs per
kWh, - less if there is direct disposal of spent fuel rather than
reprocessing. The $18 billion US spent fuel program is funded by
a 0.1 cent/kWh levy.
French figures published
in 2002 show (EUR cents/kWh): nuclear 3.20, gas 3.05-4.26, coal
3.81-4.57. Nuclear is favourable because of the large, standardised
plants used.
The cost of nuclear
power generation has been dropping over the last decade. This is
because declining fuel (including enrichment), operating and maintenance
costs, while the plant concerned has been paid for, or at least
is being paid off. In general construction costs of nuclear power
plants are significantly higher than for coal- or gas-fired plants
because of the need to use special materials, and to incorporate
sophisticated safety features and back-up control equipment. These
contribute much of the nuclear generation cost, but once the plant
is built the variables are minor.
In the past, long
construction periods have pushed up financing costs. In Asia construction
times have tended to be shorter, for instance the new-generation
1300 MWe Japanese reactors which began operating in 1996 and 1997
were built in a little over four years.
Overall, OECD studies
in teh 1990s showed a decreasing advantage of nuclear over coal.
This trend was largely due to a decline in fossil fuel prices in
the 1980s, and easy access to low-cost, clean coal, or gas. In the
1990s gas combined-cycle technology with low fuel prices was often
the lowest cost option in Europe and North America. But the picture
is changing.

Source: US Utility Data Inst. (pre 1995), Resource Data International
(1995- )
Note: the above data refer to fuel plus operation and maintenance
costs only, they exclude capital, since this varies greatly among
utilities and states, as well as with the age of the plant. On the
basis of the OECD projections opposite, capital costs in USA are
55% of total for nuclear, 45% of total for coal and
16% of total for gas. Grossing these up on this basis for 2001 gives
3.73 c/kWh for nuclear, 3.27 c/kWh for coal and 5.87 c/kWh for gas.
Future
cost competitiveness
The OECD does not
expect investment costs in new nuclear generating plants to rise,
as advanced reactor designs become standardised. The future competitiveness
of nuclear power will depend substantially on the additional costs
which may accrue to coal generating plants. It is uncertain how
the real costs of meeting targets for reducing sulphur dioxide and
greenhouse gas emissions will be attributed to fossil fuel plants.
Overall, and under
current regulatory measures, the OECD expects nuclear to remain
economically competitive with fossil fuel generation, except in
regions where there is direct access to low cost fossil fuels. In
Australia, for example, coal-fired generating plants are close to
both the mines supplying them and the main population centres, and
large volumes of gas are available on low cost, long-term contracts.
The most recent OECD
comparative study shows that at a 5% discount rate, in 7 of 13 countries
considering nuclear energy, it would be the preferred choice for
new base-load capacity commissioned by 2010 (see Table below). At
a 10% discount rate the advantage over coal would be maintained
in only France, Russia and China.
Some comparative electricity generating cost
projections for year 2005-2010
|
| nuclear
| coal
| gas
|
| France
| 3.22
| 4.64
| 4.74
|
| Russia
| 2.69
| 4.63
| 3.54
|
| Japan
| 5.75
| 5.58
| 7.91
|
| Korea
| 3.07
| 3.44
| 4.25
|
| Spain
| 4.10
| 4.22
| 4.79
|
| USA
| 3.33
| 2.48
| 2.33-2.71
|
| Canada
| 2.47-2.96
| 2.92
| 3.00
|
| China
| 2.54-3.08
| 3.18
| -
|
US 1997 cents/kWh,
Discount rate 5% for nuclear & coal, 30 year lifetime, 75% load
factor.
Source: OECD/IEA NEA 1998.
A 1997 European electricity
industry study compared electricity costs from nuclear, coal and
gas for base-load plant commissioned in 2005. At a 5% discount rate
nuclear (in France and Spain) at 3.46 cents/kWh (US), was cheaper
than all but the lowest-priced gas scenario. However at a 10% discount
rate nuclear, at 5.07 c/kWh, was more expensive than all but the
high-priced gas scenario. (ECU to US$ @ June '97 rates)
In 1999 Siemens (now
Framatome ANP) published an economic analysis comparing combined-cycle
gas plants with new designs, including the European Pressurised
Water Reactor (EPR) and the SWR-1000 boiling water reactor. Both
the 1550 MWe EPR if built as a series in France /Germany and the
SWR-1000 (with an 8% discount rate) would be competitive with gas
combined cycle, at EUR 2.6 cents/kWh. The current-generation Konvoi
plants operating in Germany produce power at 3.0 cents/kWh including
full capital costs, falling to 1.5 c/kWh after complete depreciation.
A detailed study
of energy economics in Finland published in mid 2000 shows that
nuclear energy would be the least-cost option for new generating
capacity. The study compared nuclear, coal, gas turbine combined
cycle and peat. Nuclear has very much higher capital costs than
the others --EUR 1749/kW including initial fuel load, which is about
three times the cost of the gas plant. But
its fuel costs are much lower, and so at capacity factors above
64% it is the cheapest option.
April 2001 figures
put nuclear costs at EUR 2.40 c/kWh, coal 3.18 c/kWh and natural
gas at 3.21 c/kWh (on the basis of 91% capacity factor, 5% interest
rate, 40 year plant life).
The Finnish study
in 2000 also quantified fuel price sensitivity to electricity costs:

These show that a doubling of fuel prices would result in the electricity
cost for nuclear rising about 9%, for coal rising 31% and for gas
66%. These are similar figures to those from the 1992 OECD report
(bar chart below). Gas prices have already risen significantly since
the study.
The French Energy
Secretariat in 2003 published updated figures for new generating
plant. The advanced European PWR (EPR) would cost EUR 1650-1700
per kilowatt to build, compared with EUR 500-550 for a gas combined
cycle plant and 1200-1400 for a coal plant. The EPR would generate
power at 2.74 cents/kWh, competitively with gas which would be very
dependent on fuel price. Capital costs contributed 60% to nuclear's
power price but only 20% to gas's. While the figures are based on
40-year plant life, the EPR is designed for 60 years.
A UK Royal Academy
of Engineering report in 2004 looked at electricity generation costs
from new plant in the UK on a more credible basis than hitherto.
In particular it aimed to develop "a robust approach to compare
directly the costs of intermittent generation with more dependable
sources of generation". This meant adding the cost of standby
capacity for wind, as well as carbon values up to £30 per
tonne CO2 (£110/tC) for coal and gas. Wind
power was shown to be more than twice as expensive as nuclear power.
Without the carbon
increment, coal, nuclear and gas CCGT ranged 2.2-2.6 p/kWh and coal
gasification IGCC was 3.2 p/kWh - all base-load plant. Adding the
carbon value (up to 2.5 p) took coal close to onshore wind (with
back-up) at 5.4 p/kWh - offshore wind is 7.2 p/kWh, while nuclear
remained at 2.3 p/kWh. Nuclear figures were based on a conservative
£1150/kW (US$ 2100/kW) plant cost (include. decommissioning).
Present-day
cost of generating UK electricity (p/kWh) from new plant
| |
Basic cost |
With back-up |
With £30/t* CO2 |
| Nuclear |
2.3 |
n/a |
n/a |
| Gas-fired CCGT |
2.2 |
n/a |
3.4 |
| Coal pulverised
fuel |
2.5 |
n/a
|
5.0 |
| Coal fluidised
bed |
2.6 |
n/a |
5.1 |
| Onshore wind |
3.7 |
5.4 |
n/a |
| Offshore wind |
5.5 |
7.2 |
n/a |
*
£110/t C
Plant choice is likely
to depend on a country's international balance of payments situation.
Nuclear power is very capital-intensive while fuel costs are relatively
much more significant for systems based on fossil fuels. Therefore
if a country such as Japan or France has to choose between importing
large quantities of fuel or spending a lot of capital at home, simple
costs may be less important than wider economic considerations.
Development of nuclear
power, for instance, could provide work for local industries which
build the plant and also minimise long-term commitments to buying
fuels abroad. Overseas purchases over the lifetime of a new coal-fired
plant in Japan, for example, may be subject to price rises which
could be a more serious drain on foreign currency reserves than
less costly uranium.
FACTORS
FAVOURING URANIUM
Uranium has the advantage
of being a highly concentrated source of energy which is easily
and cheaply transportable. The quantities needed are very much less
than for coal or oil. One kilogram of natural uranium will yield
about 20,000 times as much energy as the same amount of coal. It
is therefore intrinsically a very portable and tradeable commodity.
The fuel's contribution
to the overall cost of the electricity produced is relatively small,
so even a large fuel price escalation will have relatively little
effect. For instance, a doubling of the 2002 U3O8 price would increase
the fuel cost for a light water reactor by 30% and the electricity
cost about 7% (whereas doubling the gas price would add 70% to the
price of electricity).
REPROCCESSING
& MOX
There are other possible
savings. For example, if spent fuel is reprocessed and the recovered
plutonium and uranium is used in mixed oxide (MOX) fuel, more energy
can be extracted. The costs of achieving this are large, but are
offset by MOX fuel not needing enrichment and particularly by the
smaller amount of high-level wastes produced at the end. Seven UO2
fuel assemblies give rise to one MOX assembly plus some vitrified
high-level waste, resulting in only about 35% of the volume, mass
and cost of disposal.

For different fuel
costs (fossil fuels) or lead time (nuclear plants). Assumes 5% discount
trate, 30 year life and 70% load factor. Note that the key factor
for fossil fuels is the high or low cost of fuels (top portion of
bars), whereas nuclear power has a low proportion of fuel cost in
total electricity cost and the key factor is the short or long lead
time in planning and construction, hence investment cost (bottom
portion of bars). Increasing the load factor thus benefits nuclear
more than coal, and both these more than oil or gas. (OECD IEA 1992)
SOURCES
OECD/IEA, 1992, Electricity
Supply in the OECD, (above Figure from Annex 9).
OECD/ IEA NEA 1998, Projected Costs of Generating Electricity
OECD, 1994, The Economics of the Nuclear Fuel Cycle.
Nuclear Europe Worldscan 7-8/97
NEI: US generating cost data
Siemens Power Journal, Dec 1999.
Tarjanne & Rissanen, 2000, in Proceedings 25th International
Symposium, Uranium Institute.
Percebois J. 2003, The peaceful uses of nuclear energy, Energy Policy
31, 101-08, Jan 2003
Gutierrez, J 2003, Nuclear Fuel - key for the competitiveness of
nuclear energy in Spain, WNA Symp.
Nucleonics Week 20/2/03.
Royal Academy of Engineering 2004, The costs of generating electricity.
Uranium Information
Centre Ltd
A.B.N. 30 005 503 828
GPO Box 1649N, Melbourne
3001, Australia
phone (03) 9629 7744
fax (03) 9629 7207

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