Memorandum by energywatch
energywatch welcomes the opportunity to respond
to the issues raised in the inquiry. This response is non-confidential
and we are happy for it to be published.
energywatch is the statutory independent watchdog
representing gas and electricity consumers in GB. We help domestic
and business consumers with their complaints against energy companies,
provide them with advice and information about the market and
act as an advocate for their interests to energy companies, government
and regulators.
SUMMARY
The UK Government is committed to playing its
part in achieving the EU's target to achieve 20% renewable energy
by 2020. This includes electricity, heat and transport. It is
likely that the UK's target will be 15%, or 13% more than we currently
achieve. This 700% increase in renewable energy will be very demanding.
energywatch supports the EU's proposal. However,
switching to renewable energy is relatively expensive in terms
of £/tCO2. Therefore, energywatch considers it essential
that the UK makes much more effort to reduce energy consumption,
for example by ratcheting up its energy efficiency programmes,
in parallel with the drive to meet the renewable target. It will
be easier, and cheaper, to meet the target on the basis of reduced
consumption.
energywatch considers it essential that consumers
are provided with clear, accurate and real time information about
their energy consumption. Smart metering and integrated real time
displays, coupled with tailored energy advice, would provide consumers
with this information and enable them to take greater control
over their consumption and usage patterns.
energywatch also considers it essential that
consumers are provided with greater transparency over the fuel
mix of their electricity supply to enable them to play a greater
role in driving demand for increased renewable generation.
Changes to the infrastructure and planning regimes
are also required to meet the volume of renewable energy required.
Consumers will have to pay to meet the target
either through their energy bills or through taxes. Assuming a
cost of £28 billion for the banded Renewables Obligation
by 2020, the cost to consumers by this year is expected to rise
to £33 per household per year. However, existing policies
are only expected to source 20% of electricity from renewable
sources, that is only half the estimated 40% target that the draft
Renewables Directive entails.
Given such high costs, energywatch considers
it essential that mechanisms for subsidising renewables are as
cost effective as possible. These costs will disproportionately
impact on low income and fuel poor households. In the commercial
sector, they will impact on small and medium-sized enterprises
facing higher energy bills. It is therefore essential that measures
are taken to mitigate these negative distributional effects.
energywatch supports the proposed reforms to
the Renewables Obligation outlined in the Energy Bill, since banding
will reduce the "deadweight" element of the subsidy
and increase renewable deployment. However, we recognise that
banding will also increase costs to consumers and again raise
our concerns for low income and fuel poor households.
energywatch would like further debate on where
the costs of subsidy should lie, for example, between energy consumers
and general taxpayers. We consider there may be a case for some
elements of the renewable subsidy being borne by taxpayers, for
example research and development for newer technologies. This
also represents a more progressive method of raising revenue.
energywatch considers that consideration of
the cost of renewable energy should not be made in isolation.
Comparisons should be made with fossil fuels and nuclear energy
and greater account should be taken of the various externalities
associated with other energy sources. Such externalities are mostly
negligible in the case of renewable energy.
energywatch considers that the potential contribution
from small-scale renewables and renewable heat and gas towards
the UK target is currently not being realised. We consider new
policies are required to stimulate this sector as a matter of
urgency. energywatch therefore supports the introduction of a
renewable energy tariff to support small scale renewables. This
would also bring about a number of additional benefits, such as
increasing energy security for consumers (generators) and allowing
them to play a greater role in renewable policy.
BERR evidence suggests that renewable heat technologies,
plus fuel cell micro-CHP, represent more cost effective means
of meeting renewable and carbon reduction targets than small scale
electricity technologies, such as PV and micro-wind. energywatch
therefore suggests that the proposed small scale feed-in tariff
should focus more on encouraging renewable heat than renewable
electricity. This is also likely to have a greater impact on reducing
fuel poverty (in that fuel poor households have a greater need
for low cost heat than low cost electricity).
energywatch recognises that parallel measures
are needed to encourage decentralisation of existing energy networks
to facilitate the deployment of renewables.
THE COSTS
OF MEETING
THE RENEWABLE
TARGET[70]
Poyry Consulting report
In March 2008 BERR published a report commissioned
from consultants Poyry Energy Consulting into the costs of meeting
the EU's 20% renewable energy target. Poyry concluded that there
is sufficient resource in the EU-27 to meet the target on condition
that:
reported biomass potential is realised,
sustainability and land-use competition
considerations do not adversely affect assumed global biofuel
supply volumes,
all technologies are capable of implementing
a step change in "build rate", and
additional support is provided to
incentivise investment above that in project baselines.
Poyry has estimated the resource cost to the
EU-27 of meeting the 20% target. This is the cost to the economy
from using higher cost renewable technologies in place of their
conventional alternative. Their central case "least-cost
scenario" gives the incremental annual cost of meeting the
target in 2020 as 18 billion, and the lifetime costs of
the project as 259 billion, discounted to 2006 prices. The
resource cost is sensitive to the costs of the conventional technologies
replaced as well as the overall renewable potential and the assumed
costs of each renewable technology.
Poyry estimates that the incremental annual
cost to the UK of meeting its share of the target in 2020 will
be in the range between 5 and 6.7 billion. The lower
end of the range will be achievable if trading with other Member
States is a realistic option. If it is not, then more expensive
domestic actions will be required. The lifetime costs will fall
in the range between 59 and 93.1 billion, again depending
on whether trading is an option.
Poyry estimates that meeting the target will
achieve substantial CO2 savings. The annual savings in 2020 of
meeting the target in the EU-27 will be 388 MtCO2 (32 in the UK),
while the total lifetime savings are expected to be some 9,834
MtCO2 (1,034 in the UK). These figures assume that biofuels are
zero carbon, which they may not be. Poyry concludes that these
savings will be sufficient to meet around 45% of the EU's 20%
reduction target.
Poyry identifies further research that will
allow its estimates to be refined over time. These are:
an audit of available biomass resource
potential across the EU,
detailed modeling of the global biofuel
supply market,
insight into the CO2 savings generated
through biofuel use,
review of potential supply chain
constraints on increased renewable deployment across the EU, and
assessment of missing or hidden costs,
such as the costs of additional network investment or reinforcement
and infrastructure costs associated with heat grids.
THE IMPACTS
OF CHANGES
TO THE
RO
The Government intends that the Renewables Obligation
(RO) will remain the principal instrument for delivering the required
investment in renewable capacity, although it is exploring possible
support mechanisms for renewable heat (see following section).
Capital grants will no doubt continue to exist alongside the RO,
but the level of these grants may decrease as the level of the
RO increases.
The major regulatory burden imposed by the RO
is that, in order to provide additional support for the generation
of electricity from renewable sources, costs to all electricity
consumers are increased. These costs are capped by the levels
of the RO and the "buy-out" price in the RO. The RO
also imposes some regulatory burdens on renewable generators and
the electricity supply industry in relation to the administration
required to benefit from and comply with the scheme.
From 1 April 2009 the RO will be banded: each
technology will be assigned to one of four banding levels: 0.25,
1, 1.5 and 2 ROCs. The change will result in additional investment
in renewables generation, in particular in higher cost technologies.
The modelling indicates that under central electricity and central
technology cost assumptions, the amended RO will deliver 8.6%
ROC eligible renewables generation by 2010, 13.5% by 2015 and
13.5% by 2020. This is an increase to UK renewables capacity of
40% over 2009-15 compared to the existing RO.
The cost to the economy of producing renewable
energy as opposed to conventional generation is expected to be
£4.8 billion. However, the ability to target support in a
banded RO, means that banding has the potential to significantly
increase the efficiency of the RO (reducing the "deadweight"
element of the subsidy) through providing support levels more
closely linked to the needs of different technologies.
The precise outcome will of course depend on
the impact of the changes on renewables generation, which in turn
rely on a number of external market forces. Among those factors
external to the RO are future electricity prices, future carbon
prices, and future capital and operating costs for renewables.
Sensitivity analysis carried out by BERR indicates that a 10%
reduction in future generation costs has the potential to increase
the level of ROC- eligible renewable electricity generation by
10-15% in 2015.
Ofgem estimates that the total subsidy will
amount to £28 billion over the lifetime of the RO, which
equates to £33 per electricity consumer per year by 2020[71].
This will save 103.1 MtC of Carbon over the lifetime of the technologies,
an increase of 12.5 MtC over the existing RO. The figure for £/tonne
of carbon is £188 higher than the existing RO. Introducing
a banded obligation will increase the cost to consumers by an
additional £1.4 billion, compared to the existing RO, over
the lifetime of the RO. The out-turn will vary with the actual
level of deploymentincreased deployment will be accompanied
by increased costs to consumers.
|
| Option Three: Four Bands | Low
| 20151
Central
| High | Low
| Lifetime
Central
| High |
|
| Resource Cost £bn | 1.1
| 1.1 | 1.1
| 19.9 | 19.4
| 19.1 |
| Carbon Saved MtC | 3.9
| 4.5 | 5.1
| 86.8 | 103.1
| 123 |
| NPV Cost-Benefit £bn (cost+/benefit-) |
0.8 | 0.8
| 0.7 | 14.4
| 12.9 | 11.5
|
| Cost-Effective £/tC | |
| | 229
| 188 | 155
|
| RO Deadweight Cost £bn | 0.2
| 0.3 | 0.5
| 3.8 | 5.7
| 9.5 |
| Distributional Analysis |
| | | |
| |
| Exchequer Cost £bn | 0.1
| 0.1 | 0.1
| 1.8 | 2.2
| 2.6 |
| Firms Cost £bn | 1.1
| 1.1 | 1.0
| 19.1 | 18.5
| 18.1 |
| Consumer Cost £bn | 1.3
| 1.4 | 1.6
| 23.7 | 25.1
| 28.6 |
|
| Notes: |
| 1. All costs are at 2007 real prices, discounted. Low scenario is modelled assuming technology costs are 10% higher in the central case, with a lower level of renewable generation. High costs assume technology costs are 10% lower than in the central case, with a higher level of generation, and therefore costs.
|
HEAT CALL
FOR EVIDENCE
In the 2007 Energy White Paper, Meeting the Energy Challenge,
the Government announced it would:
"...conduct further work into the policy options available
to reduce the carbon impact of heat and its use in order to determine
a strategy for heat. The work will look at the full range of policy
options, including the range of existing policy mechanisms such
as the EU ETS."
The Heat Call for Evidence, published in February this year,
includes information on CO2 emissions from the generation and
use of heat, assesses the potential for this to be reduced, and
asks about the effectiveness of existing policies to bring this
about. It also includes questions about whether further measures
might be needed and what shape these could take. The document
also includes consideration of the increasing role of cooling.
The Government has sought the views of stakeholders and heat
users in industry and local government, NGOs, academics and energy
companies. Existing practices in the UK and other countries have
been reviewed and assessed, including the impact of policy and
regulation.
Almost half of the final energy consumed in the UK (49%)
is in the form of heat. Heat is generated by burning fuels such
as gas, wood, coal or oil, or from electricity. Of this heat,
70% is used by households and in commercial and public buildings.
The remaining 30% is used in the industrial sector. In total 907
TWh of heat was consumed in the UK in 2005.
Households use heat for space heating (69%), heating water
(27%) and cooking (3%). The majority of household heat (81%) is
met using gas, similar proportions are met from electricity (9%)
and heating oil (8%). The remainder is from solid fuels such as
wood and coal (2%).
Household demand for heat varies from year to year according
to the severity of the winter. It has risen somewhat over the
past 30 years from 400 TWh/y to a little under 500 TWh/y. This
is despite the marked improvement in the energy efficiency of
homes (SAP rating). Householders now enjoy much warmer indoor
temperaturesthe average internal temperature of homes has
risen by 6°C since the 1970s.
The other reason for the growth has been the increase in
the number of households which have risen by about 40%. Heat for
the commercial and public sectors is mainly used in buildings
for space heating (71%), water heating (13%) and cooking (15%).
The industrial sector uses heat for a variety of processes
and at a range of temperatures. For example low-grade heat at
less than 100°C is used for purposes such as drying, while
high-grade heat at greater than 400°C is used for glass and
steel manufacture. Industry uses a diverse mix of fuels to meet
its heat requirement, including natural gas (47%), oil (26%),
electricity (19%) together with other fuels such as refinery flue
gases.
Generation of heat, including electrical heating, accounts
for around 47% of UK CO2 emissions. The domestic and industrial
sectors generate roughly the same level of CO2 emissions, even
though domestic heat demand accounts for a larger proportion of
final energy use. The reason for this is that industry uses a
higher proportion of more carbon-intensive fuels or electricity
to achieve the high temperatures needed.
The proportion of the UK's CO2 emissions from heat is forecast
to fall as a result of changing patterns of heat use together
with Government policies, including those announced in the Energy
White Paper. It is possible to reduce the emissions from heating
in several broad ways, which are not mutually exclusive.
First, we can enhance the energy efficiency and
management of buildings and processes so that less heat is lost
to the environment or is wasted by heating empty buildings. Government
runs a number of programmes to encourage households and businesses
to take-up cost-effective energy efficiency and management measures.
These include building regulations, Decent Homes Standard, the
Carbon Emissions Reduction Target (CERT), Warm Front, the activities
of the Carbon Trust and the Energy Saving Trust; better information
including Energy Performance Certificates and the recently announced
Green Homes Service. A number of recent reports have argued that
the Government could do much more to encourage installation of
energy efficiency measures[72].
Certainly, increased efforts to reduce energy consumption will
make it easier, and cheaper, to meet the renewable target. However,
this document focuses on the supply of heat and does not discuss
energy efficiency further.
Another broad approach is to decarbonise the energy
source, which means either making much greater use of renewable
heat sources or heating from low or zero carbon electricity (which
could be produced from either nuclear, fossil generating plants
fitted with carbon capture and storage, or from renewable electricity).
Finally, there is considerable potential to make
use of surplus heat that is presently discarded from high temperature
processes like electricity production. This would effectively
displace other, more carbon-intensive ways of generating heat.
Widespread use of surplus heat or other centralised heat production
might widen adoption of district heating.
energywatch also argues that much more can, and needs to
be done on engaging consumers with their energy consumption, both
gas (ie heat) and electricity. Smart meters with integrated real
time displays are one means of ensuring that consumers have access
to meaningful information about their energy use. In addition,
an integrated approach needs to be taken in relation to energy
efficiency, fuel prices, and income so that consumers have easy
access to comprehensible advice that is tailored to differing
household's circumstances.
ELEMENT ENERGY
STUDY
A study entitled "The Growth Potential for Microgeneration
in England, Wales and Scotland" part-funded by many organisations,
including BERR, was published in early June this year. The principal
findings are:
while strong policy support measures could drive
significant uptake of micro generation, the cumulative policy
cost of this subsidy would be £21 billion by 2020 and £76
billion by 2030[73];
this expenditure would save 24 million tonnes
of CO2 annually, which is about 4% of UK emissions (560 million
tonnes). This is a high cost for a modest contribution to fuel
saving and emissions reduction; and
a rapid rise in conventional energy prices would
render subsidy support needless, with a doubling in fossil fuel
prices driving spontaneous uptake in 10 million homes by 2030.
Further details of the costs and benefits of the different
subsidy options are set out below. The report included consumer
research into attitudes to micro generation. The main findings
among owner-occupiers were as follows:
the majority are satisfied with their existing
heating systems;
there is high interest in purchasing loft/roof
insulation;
a minority claim to have considered purchasing
micro generation;
few of those who claim to consider purchasing
micro generation actually go on to obtain quotes, and only a minority
of these actually buy the technologies;
respondents claimed the key driver for purchasing
micro generation would be reduction in energy bills;
among micro generation supportive policies options
examined, consumers strongly prefer grants;
consumers evaluate ongoing costs and benefits
over a short time period;
respondents strongly dislike maintenance costs,
and especially additional maintenance costs;
consumers strongly dislike inconvenience;
there is little evidence of regional or income
effects on consumer priorities; and
of the roof-based discretionary microgeneration
technologies, consumers significantly prefer solar technologies
to micro-wind.
SUBSIDY OPTIONS
CONSIDERED IN
ELEMENT ENERGY
STUDY
Annual subsidy
A £100 annual subsidy is sufficient to promote significant
uptake of Combined Heat and Power (CHP) by 2020, with over 2.5
million units installed by this time. CHP systems are modelled
as receiving between £200 and £500 under CERT or post-2011
supplier obligation, and a further annual subsidy is sufficient
to drive high sales. When CERT ends in 2020, the unfamiliarity
penalty associated with CHP has been reduced to zero, allowing
them to compete well with gas boilers. Increasing the annual subsidy
to £200 increases the microgeneration stock to six million
in 2020 and nearly 14 million in 2030.
Feed-in tariff
A tariff of 40p per kWh degressed at 1% per year increases
uptake of PV to 130,000 units by 2020 and 900,000 by 2030. The
tariff is insufficient to stimulate micro-wind, which has similar
costs to a 1kW PV system but a much lower energy output in most
sites. The value of the tariff to a household with a 2kW PV system
in 2008 is £680 per year. The same system installed in 2030
would receive £550 per year because of the low degression
rate. A 30p tariff at 1% degression results in only 240,000 PV
installations by 2030.
A 40p tariff is required to stimulate uptake before 2020,
although technology cost reductions mean that at a 1% degression
rate, the subsidy is equivalent to over 80% of capital costs by
2030. Paying a FIT every year, while ensuring that devices continue
to operate in the future, requires a much higher tariff for a
given level of uptake due to consumers' short time horizons. It
should be noted that in Germany, where an ongoing FIT has stimulated
installation of PV at a rate of 1 GW per year, uptake by domestic
consumers was largely dependent on the availability of soft loans.
This has the same effect as deeming in that it overcomes the capital
cost barrier, and the value of feed-in tariff in Germany is sufficient
to offset the loan repayments. Since soft loans were discontinued
in Germany, purchases by domestic consumers have fallen significantly
and most uptake is now by commercial and industrial consumers
who have access to low-cost finance and probably longer time horizons.
Heat-based feed in tariff
Deeming the feed-in tariff for 10 years at the government
discount rate of 3.5% leads to substantial uptake of air source
heat pumps (ASHPs), with over two million units installed by 2030.
Biomass boilers and ground source heat pumps (GSHPs) show no uptake
since they are unable to compete with ASHPs which receive the
same subsidy. Deeming at a commercial rate of 7% reduces uptake
slightly to 1.8 million units by 2030.
At the support levels modelled, the non-deemed heat based
feed-in tariffs can provide less support than the post-2011 supplier
obligation, and so uptake is lower than in the baseline in 2020.
This is particularly true for biomass, which receives favourable
support under the CO2-based supplier obligation but receives the
same subsidy as the lower cost heat pumps under the heat based
FIT.
Solar hot water systems receive very little benefit from
a 2p/kWh heat FIT. This is because a typical system installed
in 2008 generating 1,500 kWh of hot water per year only receives
£30 per year from the 2p/kWh tariff. Even when this is deemed
over 10 years, it is equivalent to a capital subsidy of less than
10%. Therefore, to support mass market uptake of solar thermal
using an energy-based subsidy, a higher p/kWh heat reward may
be required than for primary heating systems.
A tariff deemed at 3.5% leads to annual CO2 savings of nearly
1.5Mt by 2020 and 4Mt by 2020. Over 15TWh of renewable heat are
supplied in 2020, equivalent to 5% of the government's 2020 renewable
energy target. This rises to 39TWh per year in 2030.
The cumulative cost of a tariff deemed at 3.5% is £2.6
billion by 2020 and £6 billion by 2030. This compares with
a cumulative subsidy cost of £2 billion by 2030 for an undeemed
tariff. This underlines the cost-effectiveness of deeming a feed-in
tariff, as a tripling of the subsidy spend in the deemed case
leads to over five times more renewable energy being delivered.
Heat and electricity tariff
The undeemed combined renewable tariff results in a total
microgeneration stock of 4.5 million units and generation of 7
TWh of renewable heat and electricity in 2030.
Heat pumps and PV show much stronger uptake than in the baseline,
with one device for every five homes in 2030.
The deemed renewable tariffs are much more effective and
deliver microgeneration stocks of 2.8 million and nine million
units by 2020 and 2030. These generate over 17TWh of renewable
energy in 2020 and 45 TWh in 2030.
Despite the fact that PV has a higher stock than heat pumps,
the contribution of electricity to the total renewable energy
production is relatively small at less than 20%.
The costs of the deemed combined renewable subsidy scheme
are high, with a committed spend of around £8 billion by
2020 rising to over £26 billion by 2030. Although PV and
wind generate much less energy than heat pumps throughout the
scenario, they receive the bulk of the subsidy, taking over £20
billion of the ca. £26 billion by 2030. This suggests that
a heat feed-in tariff could contribute much more to overall renewable
energy targets for a lower cost than a renewable electricity tariff
can.
The final scenario illustrates that a relatively low level
of support of 5p per kWh is sufficient to drive widespread uptake
of CHP. This is because CHP systems, particularly fuel cells,
generate much more electricity than a PV system costing a similar
amount. Deeming the tariff means that the cost of a CHP system
is reduced to the same cost as a condensing gas boiler, since
the value of the deemed subsidy for a unit generating 4,000kWh
per year is £1,600.
The cost of a CHP subsidy is very high, with a cumulative
subsidy spend of £13 billion by 2020 and £44 billion
by 2030. This means the total subsidy spend for all electricity
and heat technologies is £21 billion and £76 billion
in 2020 and 2030.
While the Element Energy study suggests that a feed-in tariff
support mechanism does have considerable cost implications[74],
energywatch supports the introduction of a renewable energy tariff
for small scale renewables for the following reasons:
It would lever in new sources of investment for
renewable energy that are currently not being realised through
the Renewables Obligation; for example in Germany, 90% of renewable
investment comes from outside the energy industry.
By encouraging micro-generation, it would change
the balance between energy companies and consumers (who also become
generators).
If parallel mechanisms (eg subsidies for up-front
installation costs) are introduced to make sure that low income
and fuel poor consumers benefit from small scale renewable technologies,
particularly heat, it could have a dramatic impact on reducing
fuel poverty. Renewable technologies represent an effective solution,
alongside solid wall insulation, for fuel poor households living
in hard to treat properties (those off the gas network and/or
built with solid walls), many of which are found in rural areas.
Increased visibility and take-up of small scale
renewables by consumers will also help stimulate energy reducing
behavioural change and take-up of energy efficiency measures.
It may help encourage new entrants to the energy
market place, for example smaller companies able to offer energy
service packages, and thus increase the competitiveness of the
UK energy market.
FUEL POVERTY
ADVISORY GROUP
REVIEW OF
MICRO-GENERATION
A recent report to the Government's Fuel Poverty Advisory
Group[75] reviews the
potential of micro-generation for tackling fuel poverty. The review
was prompted by the problem of tackling fuel poverty among households
living in "hard to treat" properties (those built with
solid walls and/or off the gas network). The report argues that
50% of fuel poor households cannot be assisted by existing insulation
and heating grants, in part due to limitations on the measures
offered under conventional programmes (Warm Front etc).
The review examines a range of micro-generation technologies,
including air sourced heat pumps, ground sourced heat pumps, bio-mass
boilers, micro-wind, solar thermal, photovoltaics and micro CHP.
It considers their suitability for inclusion in retrofit programmes
aimed at the fuel poor.
The review argues that micro-generation technologies can
play a role in tackling fuel poverty. However, policy should focus
more on renewable heat technologies than electricity. This is
because low cost heat has a much greater impact on reducing fuel
poverty than low cost electricity (assuming initial capital costs
are grant-funded).
CONCLUSION AND
RECOMMENDATIONS
energywatch considers it is possible for the UK to meet the
challenging target of providing 15% of its energy from renewable
sources. However, this will require a number of new policy initiatives
for ensuring the target is met:
A dramatic increase in measures to reduce energy
consumption, for example, expansion of energy efficiency programmes,
universal smart meters[76]
and increased regulation of domestic housing and non-domestic
buildings to increase their energy performance.
The introduction of a feed-in tariff to encourage
the deployment of small scale renewable technologies, particularly
heat. Parallel measures should be introduced to encourage the
installation of such technologies in the homes of low income and
fuel poor consumers.
Renewables policy should address social objectives,
eg increased efforts to mitigate the impact of higher fuel costs
on low income households, as well as environmental (reduced carbon)
and economic (increased security).
A much greater policy focus on heat, particularly
renewable heat, in general.
Measures to address potential supply chain constraints
on increased renewable deployment.
Investment in grid and in network management to
encourage decentralisation of energy networks and to transport
renewable electricity to demand.
Meeting the target will entail increased costs for energy
consumers, either through energy bills or taxes. energywatch calls
for a debate on the most appropriate allocation of costs between
energy consumers and taxpayers, given that the latter course represents
a more progressive route for raising revenue.
energywatch also advocates a thorough analysis of the distributional
effects of the measures required to meet the targets and the introduction
of parallel measures to mitigate the negative distributional effects.
energywatch advocates the mandatory disclosure of the fuel
mix of individual tariffs and contracts to all fuel consumers.
We consider improved transparency will help drive consumer demand
for increased renewable content of their electricity supply. This
will also require the establishment of an independent accreditation
body to verify supplier's claims and to assess any additional
environmental benefits suppliers claim for "green tariff"
products.
June 2008
70
This document draws upon the following reports:
- Poyry Consulting report (http://www.berr.gov.uk/files/file45238.pdf)
- BERR Partial Impact Assessment for changes to the RO (http://www.berr.gov.uk/files/file39497.pdf)
- Heat Call for Energy(http://www.berr.gov.uk/files/file43609.pdf)
- Element Energy study on the growth potential for micro generation
in England, Wales and Scotland (http://www.berr.gov.uk/files/file46003.pdf Back
71
Ofgem (2007), Ofgem's response to BERR consultation on the
Renewables Obligation, Ofgem Back
72
For example, Boardman, B (2008), Home truths-a low carbon strategy
to reduce UK carbon emissions by 80% by 2050, Oxford University
Environmental Change Institute; CSE et al (2008), How low-achieving
optimal carbon savings from the UK's existing housing stock,
wwf Back
73
However, a recent report by the Government's Renewables Advisory
Board estimates that micro-generation has the potential to contribute
23% towards the 15% renewable target (RAB (2008), 2020 vision-how
the UK can meet its target of 15% renewable energy, RAB).
This demonstrates the considerable value in stimulating take-up
of micro-generation measures. Back
74
These costs do not necessarily have to be met in full by energy
consumers. energywatch advocates further debate on possible funding
routes for the measure. Back
75
Microgeneration sub-group of Fuel Poverty Advisory Group (2008),
Microgeneration-demonstrating its role in tacking fuel poverty,
report to FPAG, 5/6/08 Back
76
Improved billing and metering represent real tools for consumers
to take control of their energy consumption and contribute to
carbon reduction targets. Back
|