Memorandum submitted by EDF Energy
ABOUT EDF ENERGY
EDF Energy is one of the UK's largest energy
companies. We are a vertically integrated company with a balanced
portfolio of business throughout the energy chainfrom generation
to supply. Most pertinent to this inquiry:
We are the 5th largest electricity generator
in the UK. We own and operate an 800MW CCGT (combined cycle gas
turbine) power station at Sutton Bridge and 4 GW of coal-fired
generation assets that are currently being fitted with Flue Gas
Desulphurisation (FGD) equipment, as well as small CHP and renewable
generation assets.
EDF Energy is a major supplier of gas
and electricity, with 5 million electricity and gas customer accounts
throughout the UK, supplied through our retail brands EDF Energy,
London Energy, Seeboard Energy and SWEB Energy.
EDF Energy also:
Owns and operates the electricity distribution
networks serving London, the East and South East of England, which
means that around one quarter of the UK population relies on our
distribution networks for their electricity. This makes EDF Energy
the largest distribution network operator (DNO) in the UK.
Is a major owner and provider of private
electricity infrastructures in the UK including those for the
major London airports, the London Underground, the channel tunnel
rail link, the Docklands Light Railway and Canary Wharf. We are
also a partner in the Metronet consortium.
As a company EDF Energy is committed to finding
the right balance between providing sustainable financial returns
and continually investing in serving our customers better. EDF
Energy is pleased to have the opportunity to contribute to the
Environmental Audit Committee's inquiry into "Keeping the
Lights On".
SUMMARY
25-35[1]
GW of new generation (in addition to new renewable capacity delivered
through the Renewables Obligation) will be required in the UK
by 2018 to replace closing coal and nuclear power stations and
meet demand. The large range is due to uncertainty surrounding
demand growth, reserve requirements for intermittent renewables
and the impact of environmental legislation on coal plant. Despite
currently high gas prices and small margins for gas-fired plants
the most likely replacement technology is CCGT due to its relatively
low capital costs and intermediate Carbon Dioxide (CO2) emissions.
If CCGT build alone replaces the closing capacity, some of which
is zero carbon, the UK electricity sector will not deliver major
reductions in CO2 and, based on DTI projections, CO2 emissions
in 2020 will be similar to the level of CO2 allowances distributed
in 2005.
It is the responsibility of Government to identify
its desired environmental outcome and put in place the required
regulatory framework and allow the market to support the development
of low carbon plant in the UK. Diversity in the fuel-mix in the
electricity sector also needs to be incentivised, since a UK electricity
generation portfolio dominated by CCGTs creates risks to physical
security of supply and electricity prices. EDF Energy believes
that the general mix of fuels and technologies is a legitimate
matter for Government interest and policy action.
EDF Energy believes the construction of new
nuclear power stations in the UK, particularly in view of the
forthcoming closure of existing nuclear power stations, should
be part of the solution to the challenge of reducing CO2 emissions.
It will also increase security of supply and reduce energy price
volatility. Potential investors in nuclear power need a stable
long-term energy policy framework within the UK before they can
invest. This should include appropriate and reliable incentives
that recognise the role nuclear and other carbon-free technologies
can play in achieving the UK's climate change objectives. There
are many barriers to new nuclear build including licensing, planning
and waste management and disposal. These barriers need to be tackled
now if nuclear is to directly replace some of the closing plant
because new nuclear stations will take approximately ten years
to become operational.
EDF Energy supports the Renewables Obligation
(RO) provided it delivers against the current targets for renewable
energy at a reasonable cost to the customer. Large volumes of
intermittent renewable generation capacity will entail significant
additional reserve costs. Renewable targets should not be increased
at this stage beyond those currently in place until a significant
volume has been built and the technical and economic impact has
been assessed.
Proven clean coal technologies with reduced
CO2 emissions due to major increases in thermal efficiency, as
well as CO2 sequestration technologies, also have the potential
to provide low CO2 generation in the future.
In conclusion, new nuclear, renewables, clean
coal and carbon sequestration along with gas and energy efficiency
should all play a role in meeting the predicted electricity generation
capacity shortfall while addressing climate change. Diversity
is the key to providing security of supply in a low carbon future.
A. THE EXTENT
OF THE
"GENERATION GAP"
1. What are the latest estimates of the likely
shortfall in electricity generating capacity caused by the phase-out
of existing nuclear power stations and some older coal plant?
How do these relate to electricity demand forecasts and to the
effectiveness of energy efficiency policies? [2]
The effect of the Large Combustion Plant Directive
(LCPD) will be to limit "opted-out" unabated coal station
output from 2008 before total closure by 2016 of 19 GW of coal
and oil plant, circa 25% of present GB generation. The exact profile
of opted-out plant closures between now and 2016 is uncertain.
The capacity of opted-in plant (some 13GW) that will upgrade their
NOx abatement equipment and operate beyond 2015 is also uncertain.
Nuclear decommissioning will result in all Magnox
(BNFL) stations shutting by 2010, a reduction of 2.5 GW, and the
closure of a number of AGRs (Advanced Gas-cooled ReactorBritish
Energy). If life extensions are not granted to AGRs, 5 GW could
close by 2014.
The shortfall in electricity generation capacity
is a function of both the closure of plant and the rate of growth
of demand. National Grid (NG) assumes average peak demand growth
of 0.79% per annum in its 2005 GB Seven Year Statement. On the
assumption that a system margin of 20% needs to be maintained
then circa 27 GW of new capacity needs to be constructed before
2018 subject to the exact profile of nuclear plant closures. 10
GW of intermittent renewable capacity may be connected by 2018;
however, this will require significant additional capacity as
back-up. If energy efficiency is assumed to reduce NG's peak demand
growth assumption by 1% then this would reduce the level of new
capacity required in 2018 by circa 8 GW.
In combination these drivers imply that 25-35
GW of new generation (in addition to new renewable capacity delivered
through the Renewables Obligation) will be required in the UK
by 2018 to replace closing coal and nuclear power stations and
meet demand. Substantially more new plant could be required by
2018 if some or all opted-in plant also close. If life extensions
are granted for several nuclear stations then that will cause
only a small reduction in the capacity shortfall for a period
of a few years.
A major uncertainty in any longer-term electricity
demand forecast is the demand for hydrogen (H2) transport fuel,
since hydrogen production is either via electrolysis, or via "synthesis"
from fuels such as coal, oil or gas. Synthesis itself directly
produces CO2, whereas electrolysis produces none, although of
course the generation of the electricity may have done. Our figures
above assume that either no demand for H2 fuel develops, or such
fuel is synthesised from hydrocarbons rather than produced through
the electrolysis of water. If there is a significant demand for
H2 fuels using electrolysis then the size of the generation gap
will be significantly greater than indicated above, as the current
UK road transport fleet has primary energy usage broadly equivalent
to the energy used in national electricity generation.
In the longer-term, national aspirations for
a reduction of CO2 emissions to 60% of 1990 levels by 2050 imply
that the UK will need to move towards a virtually-zero-CO2 generation
fleet as well as making radical emission reductions in space heating
and transportation. Once established, low carbon electricity supply
could also help make a significant contribution to CO2 reduction
emissions in other sectors by substituting for the use of fossil
fuels. It is important to note that assets constructed to replace
the shortfall caused by nuclear and coal plant closures before
2020 are likely to be operational in 2050 when the Government's
goal of 60% reduction needs to be delivered.
B. FINANCIAL
COSTS AND
INVESTMENT CONSIDERATIONS
2. What are the main investment options for
electricity generating capacity? What would be the likely costs
and timescales of different generating technologies?
What are the likely construction and on-going
operating costs of different large-scale technologies (eg nuclear
new build, CCGT, clean coal, on-shore wind, off-shore wind, wave
and tidal) in terms of the total investment required and in terms
of the likely costs of generation (p/kWh)? Over what timescale
could they become operational?
A number of recent studies have explored this
question. The main investment options are CCGT, OCGT (open-cycle
gas turbine), clean coal, wind and standalone biomass. Nuclear,
whilst a proven technology, has barriers to development in the
UK at present. We expand on this point later in our submission.
Wave and tidal technologies (apart from tidal barrages which can
have major environmental impacts) are currently still in development.
The table below summarises central capital and operating cost
views from these studies and our own internal analysis. More detailed
cost estimates for nuclear are included later in our submission.
Table 1
|
Advanced CCGT
| Clean
Coal
(IGCC) |
Advanced OCGT
|
Nuclear | On
shore
wind
| Off
shore
wind |
Marine
|
Biomass |
Capital Costs (£/kW) | 440
| 974 | 210 | 1,150
| 715 | 1,250 | 1,750 est
| 1,500 |
Fixed costs (£/kW pa) | 25
| 27 | 14 | 41 |
15 | 24 | 56 | 80
|
Efficiency (HHV) % | 54 | 45
| 37.5 | 39 |
| | | 35
|
Start of construction to commissioning (years)
| 2.5 | 3 | 1.5
| 5 | 1.5 | 2 |
2 | 2 |
Total time to commissioning incl planning |
4.5 | 5.5 | 3.5 |
8 to 10 | 3 | 4 |
4 | 4 |
NB The capital cost comprises all costs covered by the financing of the plant except for interest during construction and debt service reserve.
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|
Sources: | |
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| | |
ILEX Energy Consulting "Projections of the price for wholesale electricity in Great Britain", June 2005
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|
ILEX Energy Consulting "The value of renewable electricity in the United Kingdom", June 2005
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| | | |
|
The Royal Academy of Engineering (RAE) "The costs of generating electricity", March 2004
| | | |
| | | |
|
EDF Energy internal data | |
| | |
| | | |
| | |
| | |
| | |
Cost of generation is dependent on fuel cost, CO2 cost, site-specific
costs and required rate of return as well as capital and operating
costs of a plant. It can therefore vary significantly for individual
projects using the same technology. The RAE study estimates p/kWh
costs (tables 1.1 and 1.2 in their report). In the case of renewables,
two costs are cited by the RAE, one of which includes the cost
of the resulting extra national reserve ("standby generation")
requirement if electricity supplies are to remain secure.
The data listed below are based on the RAE view of generation
costs over a reasonable lifespan for new plants of each type,
and therefore include both construction and operation costs. The
RAE report provides a CCGT generation cost of 2.2p/kWh (excluding
the cost of CO2) based on a gas price of 23p/therm. Gas prices
in September 2005 are significantly higher at 47p/therm[3].
The gas-fired CCGT cost we quote below factors in this higher
gas cost. Coal costs are assumed to be £30/tonne. Discount
rate is assumed to be 7.5%. The costs of generation provided below
are a guide to the relative cost differences between technologies
subject to the uncertainties of fuel and CO2 costs and rate of
return described above.
Nuclear costs are subject to greater uncertainty than other
technologies relating to both the cost of the plant and the rate
of return required by investors. We explore this in more detail
later in our submission.
New CCGTS have CO2 emissions of c 0.4 tonnes/MWh, coal IGCCs
(Integrated Gasification Combined Cycle) would have emissions
of c 0.65 tonnes CO2/MWh and new fluidised bed and pulverised-fuel
coal plants would have emissions of c 0.8 tonnes CO2/MWh.
Cost of generating electricity for base-load plant (without/with
CO2 cost @ £10/tonne[4])
Gas-fired CCGT: 3.8/4.2 p/kWh
Nuclear fission plant: 2.3 p/kWh (unaffected by CO2
cost)
Coal-fired pulverised-fuel steam plant: 2.5/3.3 p/kWh
Coal-fired circulating fluidised bed (CFB) steam plant:
2.6/3.4 p/kWh
Coal-fired integrated gasification combined cycle
(IGCC): 3.2/3.9 p/kWh
Cost of generating electricity for selected renewables (without/with
standby generation)
Onshore wind farm: 3.7/5.4p/kWh
Offshore wind farm: 5.5/7.2p/kWh
Wave and marine technologies: 6.6/6.6 p/kWh
Biomass bubbling fluidised bed (BFB) steam plant:
6.8/6.8 p/kWh
Note that wind generation costs are significantly higher
where sites are sub-optimal (eg lower wind resource, higher capital
costs, etc). Enviros Consulting[5]
suggests that 3 TWh of onshore wind can be generated at a cost
of less than 5p/kWh (excluding additional reserve costs), 10 TWh
at a cost of less than 6p/kWh and 30TWh at a cost of less than
10p/kWh.
Additional interconnection with continental Europe can also
play a role in filling the generation shortfall as well as increasing
security of supply by increasing the amount of generation available
to meet the UK's national demand.
With regard to nuclear new build, how realistic and robust
are cost estimates in the light of past experience?
As far as nuclear power is concerned, there are varying estimates
of the cost available from around the world. We include below
some leading recently-published sources on the cost of nuclear.
Table 2
| MIT[6]
(2003)
| PIU[7]
(2002)
| Chicago[8]
(2004)
| RAE[9]
(2004)
| DGEMP[10]
(2003)
| Tarjanne[11]
(2003)
|
Generating cost
(p/kWh) | 3.9-4.312
| 3.0-4.0 | 3.1-3.6 | 2.26-2.44
| 2.013 | 1.7 |
Rates of return | 15% | 8% and 15%
| 12.5% | 7.5% | 8%
| 5% |
Capital cost | $2,000/kW
(£1,150/kW)
| $2,000/kW
(£1,150/kW) | $1,500/kW
(£865/kW)
| $2,000/kW
(£1,150/kW) | $1,413/kW
(£990/kW)
| $1,900/kW
(£1,330/kW) |
Load factor | 85% | 75-80%
| 85% | >90% | >90%
| >90% |
Economic life | 25 and 40 years
| 20 years | 15 years | 25 and 40 years
| 35-50 years | 40 years |
Construction period | 5 years
| Not identified | 5-7 years |
5 years | 5 years | 5 years
|
| |
| | | |
|
Costs for a single nuclear plant are significantly higher
per unit than for a series of plant by approximately 0.3-0.4p/kWh.
Designs such as EPR are already being constructed in France and
Finland (first commissioning: 2009) and so there is the potential
for some "first of a kind" costs to be incurred elsewhere.
Design UK licensing costs could be low if advance generic design
licensing became possible in the UK, leaving constructors only
needing to license a site, and not license the new (to the UK)
design at the same time. Thus, provided the principle of adopting
a vendor's standard design is retained without modification, costs
in the region of those shown in the table above could be expected.[12],
[13]
The generating costs in the international table above, vary
widely from about 1.7p/kWh to 4.3p/kWh. This range is primarily
due to differences in the assumed rate of return the investor
demands. A high rate of return increases the generating cost whereas
mitigating risks drives down the cost of nuclear substantially.
A high rate of return would be applied when there is a high level
of perceived risk in the project due to, for example, uncertain
revenues or low confidence in completion to time and cost. This
was the case in the US where nuclear was perceived to be very
risky in the 1980'shence the very substantial risk premium
that is used in the Chicago and MIT studies above. In contrast
in Finland the rate of return demanded is low (approx. 5%) given
the high confidence (low perceived risk) of investing in nuclear
and, particularly, the secure long term off-take contracts with
industrial consumers in place.
No new nuclear has recently been funded in the UK. Our understanding
of the UK market is that:
for new merchant gas-fired (CCGT) independent power
producers (IPPs), a nominal post-tax project return of 8-10% would
be considered appropriate; while
new contracted IPPs might now be undertaken on rates
of 7-9%.
The level of premium would be dictated by the relative conservatism
of particular sponsors, the extent to which, by the date of any
decision, the experience with nuclear new build has been positive,
the political/regulatory environment including aspects of the
planning regime, and possible new economic/market support for
lower-carbon generation. For nuclear, we expect that investors
would look at an additional premium of perhaps 1-2% relative to
CCGTs associated with the fact that nuclear new build may have
special risksfor example, at one American project on a
coastal spit, permission to operate was permanently withheld after
construction, as it was decided that local evacuation plans could
not work after all.
It is therefore clear that in the UK, given a Government
desire to mitigate both the perceived and real risks from investment
in nuclear energy, nuclear can be economic. However, in the absence
of risk mitigation (associated with licensing, planning, etc)
by Government, nuclear will not be built in the current market.
Pre-development costs are expected to be approximately £250
million for a "first of a kind" reactor (subject to
the point made above about the possibility of generic licensing),
falling to approximately £100 million for subsequent reactors
in the same series. Without reasonable expectation that these
costs can be recovered no investment will be made.
What are the hidden costs (eg waste, insurance, security) associated
with nuclear? How do the waste and decommissioning costs of nuclear
new build relate to the costs of dealing with the current nuclear
waste legacy, and how confident can we be that the nuclear industry
would invest adequately in funds ring-fenced for future waste
disposal?
We would assume that the UK Government would set a waste
disposal "levy" or fee on the basis of nuclear power
generated (MWh) and charge for this at the time of such generation.
We understand that this is the approach taken in the USA and Finland,
for example. To determine this fee, the government would make
assumptions about the waste disposal cost, when the cost would
be incurred, and the return realised on levy monies between the
date of receipt and the date of incurring the cost.
The Committee will be aware that the Government cancelled
the search for a deep waste depository in February 1997, from
which time there has been no plan or strategy to deal with the
existing waste inventory from the Royal Navy, hospitals, industry
and the civil power programme. It is hoped that a clear national
plan leading to an identified location will quickly be put in
place when CORWM reports in July 2006. The issue is increasingly
pressing and exists irrespective of new build, which would make
very little difference to its scale as the lifetime operation
of a fleet of 10 GW of new nuclear stations would add only 10%
to the existing volume of high-level radioactive waste.
Is there the technical and physical capacity for renewables
to deliver the scale of generation required? If there is the capacity,
are any policy changes required to enable it to do so?
The UK has a renewable resource (wind, marine, biomass) that
is theoretically large enough to replace the output being lost
from coal and nuclear plant closures. However, unlike the closing
plant, a number of renewable technologies are characterised by
intermittent output that limits their ability to act as a direct
substitute. Renewable intermittency places a cap on the amount
of capacity that can be accommodated in the UK without incurring
significant costs for additional reserve or increased interconnection.
The most economic renewable technology at present is onshore
wind. Current UK wind generation is c 1% of the national total.
Wind penetration of greater than circa 10% capacity carries significant
security of supply difficulties without significant additional
reserve. OXERA, the energy consultancy, illustrated the magnitude
of the intermittency problem in a report in June 2003 entitled,
"The Non-Market Value of Generation Technologies". OXERA
reported in its forecast that although average wind output is
up to 30% of capacity, there will be at least 23 one-hour periods
in a year when the output from all wind turbines in the UK is
less than 10% of declared wind capacity at the same time that
demand is 90% or more of annual peak demand. This is after making
allowance for the benefits of wind turbines being distributed
around the UK including offshore. Across the entire year, OXERA's
model showed that UK wind fleet output would fall below 10% of
total "nameplate"" capacity of the wind fleet for
18.7% of the time. In other words, wind is relatively unreliable
and by itself cannot substitute for closing capacity.
The UK has limited interconnection to neighbouring countries
and therefore additional UK reserve plant is required to back
up intermittent wind output. Additional reserve to back up intermittent
wind output is expensive. The RAE quantifies the cost of this
additional reserve as 1.7p/kWh.
EDF Energy does not believe that any significant policy change
is required at present with respect to renewables, which receive
support (either directly or indirectly) from a range of instruments
including the Renewables Obligation, Climate Change Levy exemption
certificates, Fuel Mix Disclosure, European Union Emissions Trading
Scheme and direct grants.
The Renewables Obligation (RO) requires suppliers to source
15.4% of their electricity from eligible renewable generation
by 2015-16 or pay a 3p/kWh (at 2002 prices) "buyout"
penalty, which is paid to suppliers to the extent that they were
compliant, thus increasing the true value of the renewables obligation
considerably above 3p/kWh). As a direct consequence of this obligation,
UK RO renewable output has increased from 5.6TWh in 2002-03 to
10.8TWh in 2004-05 at high cost to consumers (now 3.23pkWh of
the renewable generation target in 2005/06, equivalent to 0.18p/kWh
on customers' bills). The RO is clearly working and will deliver
significant additional generation (forecast to be between 25 and
30TWh in 2010). Physical constraints (the availability of sites
with planning consent, as well as transmission network infrastructure,
connections, etc) rather than Government policy are likely to
be the limiting factor for renewable build in the short to medium
term and are already being addressed.
Stability is a vital component of support mechanisms such
as the RO to provide investors with the confidence to provide
capital. One area of the RO that could be improved to boost confidence
are the arrangements that apply in the event that a supplier defaults
on its payments into the buyout fund. The DTI has recently introduced
a mutualisation scheme whereby non-defaulting suppliers have to
recover the default from their customers. This increases the cost
of the RO to customers; and there is no guarantee that a supplier
will be able to recover the full cost of the default from its
customers in a competitive market. As a result suppliers are likely
to continue to factor the risk of supplier default into the price
they are prepared to pay to generators for ROCs, reducing the
total volume of renewable generation that will be delivered by
the RO. A preferable solution would be one in which suppliers
provided letters of credit or made buy-out payments more frequently
to eliminate the risks associated with supplier default.
What are the relative efficiencies of different generating
technologies? In particular, what contribution can micro-generation
(micro-CHP, micro-wind, PV) make, and how would it affect investment
in large-scale generating capacity?
We believe that there are many barriers to be overcome before
micro-generation can make a significant contribution in the short-to-medium
term. For widespread adoption of micro-generation to be feasible,
the devices must be reliable, economic to purchase, and above
all easy to maintain with, crucially, sufficient trained maintainers/installers
available. Increased penetration of small-scale distributed generation
will reduce investment in large-scale generating capacity to the
extent that it reduces national transmission system demand. It
is highly probable that micro-generation will replace only a small
fraction of the generation shortfall caused by the large capacity
of closing plant.
3. What is the attitude of financial institutions to investment
in different forms of generation?
What is the attitude of financial institutions to the risks
involved in nuclear new build and the scale of the investment
required? How does this compare with attitudes towards investment
in CCGT and renewables?
We understand that financial institutions regard new nuclear
in the UK as potentially competitive with new CCGTs.
At present, investors in renewables require projects to have
off-take contracts for power, ROCs (Renewables Obligation Certificates)
and LECs (climate change Levy Exemption Certificates) before they
are prepared to provide finance owing to the perceived risks surrounding
ROC prices. Very few merchant renewables projects that will sell
their output on a short-term basis into the market are being developed
at present. Similarly large CCGTs being developed by non-vertically
integrated companies typically seek offtake contracts to lower
the risk profile associated with the project. It seems reasonable
to assume that similar levels of certainty regarding revenue streams,
to reduce risk, would be a requirement of financiers before they
would lend to new nuclear projects.
How much Government financial support would be required to
facilitate private sector investment in nuclear new build? How
would such support be provided? How compatible is such support
with liberalised energy markets?
A range of instruments could be used by Government to support
new nuclear build including capital support, revenue support,
obligations on suppliers to source a percentage of their output
from low CO2 sources (including CO2 sequestration and nuclear)
or long-term contracts for carbon emissions avoidance. Similar
support mechanisms for particular technologies already exist in
the liberalised UK energy market, for example the Renewables Obligation,
capital grants to Round 1 offshore projects and revenue support
to marine renewables and via Climate Change Levy exemption certificates.
In its implementation of phase 1 (2005-07) of the EU ETS
(emissions trading scheme), the UK has set aside a New Entrant
Reserve for distributing CO2 allowances for new installations.
Any operator commissioning a new installation will receive allowances
proportional to its projected output. However nuclear generation
is excluded from EU ETS and does not qualify to receive free allowances.
Government financial support that recognised the extent and magnitude
of CO2 savings delivered by new nuclear could be used to facilitate
private sector investment in new build. This could be achieved
by offering operators of new nuclear plant a carbon avoidance
contract that would pay operators at a predetermined rate on output
achieved (and CO2 emissions saved). The payments could be funded
by revenues raised from the auctioning of CO2 allowances.
The retention of a new entrant reserve (NER) in its present
form in ETS would discriminate against carbon free technology
and support the development of non-carbon free technology through
the issuing of free allowances to new build (eg CCGT), and would
significantly increase the complexity of the scheme and reduce
certainty for participants.
As previously suggested, one of the most valuable contributions
that Government could provide would be, through working with industry,
to reduce the risks associated with licensing, planning, etc.
This could be achieved through a joint Government-industry project
that shared these licensing and planning costs for a "first
of a kind" reactor in the UK. This would reduce the risk
a company would take in incurring large pre-development costs
with no return being delivered if the process failed to deliver
nuclear new build and also reduce the rate of return required
on the main construction project by investors.
What impact would a major programme of investment in nuclear
have on investment in renewables and energy efficiency?
Investment in new nuclear will not have any effect on renewables
or energy efficiency measures in the short-term before 2010. Investment
in renewables is driven by the distinct Renewables Obligation
mechanism. Similarly, investment in energy efficiency is currently
driven through the EEC mechanism. Given the lead times for new
nuclear generation associated with licensing, planning, etc physical
construction and major commitment of capital is unlikely to happen
until 2010 or later. At that point in time commercial or supply
licence condition/obligation-based drivers are likely to maintain
significant investment in renewables and energy efficiency.
C. STRATEGIC BENEFITS
4. If nuclear new build requires Government financial
support, on what basis would such support be justified? What public
good(s) would it deliver?
The public good delivered would in one sense be comparable
to the public good delivered from support for renewableszero
carbon generation. However, there are a number of key differences:
The good would be delivered far more cheaply.
The good would be delivered in a way that enhanced
security of supply.
Land use would be minimal.
There would be more long-term high-tech employment/training
in rural areas.
The potential volume of carbon-free generation would
be larger.
If existing (closing) nuclear sites are used, extensive,
expensive new high- or low-voltage transmission infrastructure
from remote sites is less likely to be required.
Relative to meeting the generation gap using CCGTs burning
increasing volumes of imported gas, nuclear build could also be
justified on the grounds that it enhances economic and physical
security of energy supplies in the UK.
Nuclear generation is not part of the EU ETS and does not
receive any direct benefit for reducing CO2 emissions. Government
could justify support on the basis that new nuclear prevents CO2
emissions that would otherwise have an associated cost in the
EU ETS.
To what extent and over what timeframe would nuclear new build
reduce carbon emissions?
Nuclear output would either displace closing coal generation
or prevent the need for additional gas fired generation to replace
closing nuclear plants. Coal generation currently emits roughly
0.95 tonne CO2/MWh and CCGTs emit approximately 0.4 tonne CO2/MWh.
The electricity sector accounts for roughly 25% of UK CO2 emissions
and the replacement of fossil fired generation with nuclear generation
could contribute significantly to achieve the UK's targets on
climate change. A 10 GW replacement nuclear programme could prevent
an increase in CO2 emissions of c 30 Mt CO2 per annum that would
occur if CCGTs replaced the closing capacity instead.
To what extent would nuclear new build contribute to security
of supply (ie keeping the lights on)?
Nuclear new build would contribute significantly to increasing
security of supply by reducing dependence on imported fossil fuel
supplies.
There is a body of evidence that identifies specific security
of supply deficiencies for renewables and CCGTs. In respect of
renewables, we have covered this in our earlier answer. In respect
of gas, the House of Lords' "Renewables: the practicalities"
report (14 July 2004) states in paragraph 2.5 that by 2020 we
will be reliant on imported gas, "more than half" of
which will come from Russia. "Interruptions in these supplies
may occur once every eight years with a duration of the interruption
of up to 180 days: The UK can at most only store 14 days' worth".
The House of Lords committee cites OXERA as the source for this
information and urge urgent [but unspecified] action. The drawbacks
of extensive national reliance on imported gas with very limited
ability to store it are self-evident. A number of new storage
and LNG import facilities are being constructed. However the storage
facilities are for short to mid-range storage and are not of sufficient
size to materially benefit the UK in the event of a prolonged,
major gas supply interruption. The LNG ships are themselves a
potentially vulnerable supply route; there has been a recent case
of a successful attack on an oil tanker[14].
If an incident occurred affecting the gas piped into Europe from
the East, the UK would face strong competition for LNG supplies.
Large percentages of world gas reserves are held in just
a few nations, Russia having over a quarter of world reserves,
and Quatar and Iran having a further 30% between them. The UK
has less than 1% of world gas reserves. Russia in particular,
which has become closer to Iran recently, has from time to time
spoken publicly of her desire for an OPEC-like gas cartel[15].
Is nuclear new build compatible with the Government's aims
on security and terrorism both within the UK and worldwide?
New nuclear build is capable of reducing the existing inventory
of Plutonium 239, which is a key ingredient of atomic weapons,
by converting it to other elements in the nuclear fission process.
To this extent, proliferation concerns can be ameliorated.
We understand that new PWRs with a containment dome are proof
against a design basis threat that generally includes hijacked
airliner crashes.
New nuclear build cannot be viewed in isolation when considering
security and terrorism risks associated with the UK energy industry.
There are major security and terrorism risks associated with the
transport and storage of LNG which the UK Government advocates
as a major contributor to replacing depleting supplies of gas
from the UK continental shelf. [16]
Existing nuclear risks are well managed. The Office of Civil
Nuclear Security's Annual Report (July 05) [17]states
that security arrangements applied within the nuclear companies
and bodies regulated by OCNS are comprehensive, well-managed and
effective [para 138, p 35 of the report]. We see no reason to
believe that risks associated with new build would be any less
well managed.
5. In respect of these issues [Q 4], how does the nuclear
option compare with a major programme of investment in renewables,
microgeneration, and energy efficiency? How compatible are the
various options with each other and with the strategy set out
in the Energy White Paper?
It is not credible that the UK can achieve a significant
reduction in the carbon intensity of its UK fleet if it allows
present nuclear stations to close without replacement except through
the use of carbon sequestration (which itself has significant
uncertainties, which may be resolved over time, associated with
the transport and enduring, safe storage of CO2). As for demand,
the Government has ambitions to permit extensive building of new
housing in the UK and the evidence is of public expectations of
winter warmth and even domestic summer air-conditioning becoming
more onerous as society becomes wealthier. Significant improvements
in energy efficiency at a level that can reverse demand growth
have been the general policy aim for two decades now, without
success. Renewables, with their penetration limited by intermittency,
are likely to, at best, service increased demand and cannot compensate
for the closing zero-CO2 nuclear output, let alone supplement
it and displace fossil-fired generation.
The Energy White Paper sets out four energy policy objectives:
1. to put ourselves on a path to cut the UK's carbon
dioxide emissionsthe main contributor to global warmingby
some 60% by about 2050 with real progress by 2020;
2. to maintain the reliability of energy supplies;
3. to promote competitive markets in the UK and beyond,
helping to raise the rate of sustainable economic growth and to
improve our productivity; and
4. to ensure that every home is adequately and affordably
heated.
Replacement nuclear power could clearly play a role in delivering
all four objectives due to its negligible CO2 emissions, diversifying
effect in the UK energy mix and relatively low price volatility
compared with gas.
In contrast most renewable technologies have a higher generation
cost and some have intermittent or unpredictable output, leading
to a less good fit than nuclear with objectives 2, 3 and 4, and
limitations on their total potential to contribute to the first
objective.
D: OTHER ISSUES
6. How carbon-free is nuclear energy? What level of carbon
emissions would be associated with (a) construction and (b) operation
of a new nuclear power station? How carbon-intensive is the mining
and processing of uranium ore?
Nuclear energy itself is 100% carbon-free, although when
you take into account other processes such as fuel production
and construction then there is a small amount of CO2 that can
be attributed to nuclear power. The actual emissions however from
the different processes will be very site specific and depend
on factors such as the type of plant and the process used for
the enrichment of the uranium. For example, the centrifuge approach
to uranium enrichment, which is used in the UK, uses only 1/30th
as much energy as the gas diffusion approach. The overall performance
of the plant itself (in terms of load factor) will also have an
effect on the emissions per kWh, as a plant with a greater annual
output will have lower overall emissions. More detailed information
on these issues can be found in Vattenfall's[18]
paper on the electricity production system.
A report by the Energy Technology Support Unit (ETSU) in
1995 found that the CO2 emissions associated with nuclear power
amounted to approximately 4 g/kWh[19].
More recent data released by the World Nuclear Association (WNA)
[20]suggests that anywhere
between nine and 21grams of CO2 equivalent per kWh can be attributed
to nuclear generation, although these figures include all greenhouse
gas emissions, not just CO2. EDF Group calculations show a range
of 3-40 g/kWh with EDF Group's own emission factor based on actual
plant performance equal to 4.5 g/kWh. Energy use in the mining
and milling of uranium ore is significant, and although this occurs
outside the UK, the WNA data accounts for this as it attempts
to quantify the environmental emissions from all stages of electricity
generation.
EDF Group's 4.5 g/kWh figure breaks down in the following
relative proportions:
Construction of nuclear power station = 8%.
Operation of the nuclear power stations = 9%.
Mining and treatment = 22%.
Enrichment = 54%.
Other/fuel fabrication = 7%.
This compares extremely favourably to emissions of 950 g/kWh
from existing coal-fired power stations and 400 g/kWh for gas
burned in a CCGT. The CCGT carbon-intensity we quote here understates
the real emission factor when the UK becomes reliant on a diverse
range of gas imports as there is a considerable amount of energy
involved21[21] in the
chilling, liquefaction, transportation, regasification and compression
of natural gas that is transported as LNG. Also there is a global
warming potential associated with methane emissions along long
Russian gas pipelines to the West, which have been said to be
very porous by Western standards.
7: Should nuclear new build be conditional on the development
of scientifically and publicly acceptable solutions to the problems
of managing nuclear waste, as recommended in 2000 by the RCEP?
The waste problem already exists and according to CORWM,
building 10 GW of new nuclear plant would only add 10% to the
existing high-level waste inventory during the lifetime of the
new nuclear plant. However, the waste problem is pressing and
Government should move to identify the optimum long-term solution
at the earliest possible moment. A number of scientifically acceptable
solutions do exist and the resolution of this debate should not
hold up the development of new stations.
23 September 2005
4303_uk_coal_producers_summer_interuptions.pdf
1
EDF Energy assessment, more detail later in submission. Back
2
In this section, except where stated, capacity and demand assumptions
are based on EDF Energy's own analysis. Back
3
Argus gas price 2006-10 (14 September 2005). Back
4
Carbon is presently trading at prices closer to £16/tonne,
but we have taken a deliberately conservative approach here. Back
5
Report to the DTI "The Costs of Supplying Renewable Energy"
17 February 2005. Back
6
MIT Study, the Future of Nuclear Power. Back
7
Performance and Innovation Unit (PIU) Energy Review Working Paper,
The Economics of Nuclear Power. Back
8
University of Chicago Study, The Economic Future of Nuclear Power/ Back
9
Royal Academy of Engineering, The Cost of Generating Electricity,
A Commentary. Back
10
General Directorate for Energy and Raw Materials (DGEMP) of the
French Ministry of the Economy, Finance and Industry. Back
11
Tarjanne, Laappeenranta University of Technology, Finland. Back
12
Based on 1 GBP = 1.734 USD (exchange rate used in RAE study). Back
13
Based on 1 EUR Õ0.7 GBP (Bloomberg, 10 March 2005). Back
14
http://www.cbsnews.com/stories/2002/10/06/world/main524488.shtml. Back
15
For example, see third from last paragraph in : www.ofgem.gov.uk/temp/ofgem/cache/cmsattach/ Back
16
Lloyds of London chairman, Peter Levene, made a speech to the
Houston Forum on 20 September 2004. Levene said "Gas carriers,
whether at sea or in ports, make obvious targets. Specialists
reckon that a terrorist attack on a LNG tanker would have the
force of a small nuclear explosion". Back
17
http://www.dti.gov.uk/energy/nuclear/safety/dcns_report3.pdf Back
18
http://www.worldenergy.org/wec-geis/publications/default/tech_papers/17th_congress/3_4_14.asp Back
19
ETSU, (1995). "Full Fuel Cycle Atmospheric Emissions and
Global Warming Impacts from UK Electricity Generation", ETSU
Report No. R-88, HMSO, 1995. It should be pointed out that ETSU
has recently been re-named "Future Energy Solutions". Back
20
http://www.world-nuclear.org/info/inf59.htm Back
21
See note 1 of http://www.foe.co.uk/cymru/english/press_releases/2004/anglesey_gas_plant.html Back
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