Trade and Environmental Sustainability
Structured Discussions (TESSD)
Communication from the United Kingdom
Revision
The
following communication, dated 1 November 2024, is being circulated at the
request of the delegation of the United Kingdom.
_______________
offshore wind energy
Technical paper by the United Kingdom
Contents
1 Introduction.. 2
1.1
Executive summary. 2
1.2 The importance of offshore wind energy in
achieving climate mitigation goals. 3
1.3 Lifecycle considerations for offshore wind
turbines. 4
2
Role of services. 5
2.1 Technical services. 5
2.2 Ancillary services. 5
2.3 Barriers to services trade. 6
3
Value chain diagrams. 7
3.1
Wind turbine. 8
4 Market access barriers. 14
4.1
Tariffs. 14
4.2
Broader challenges affecting trade in OSW.. 16
This
evidence paper explores the goods and services associated with the production
and trade in offshore wind (OSW) energy. This individual report follows on from
the UK's earlier technical paper titled 'Building our evidence based around
environmental goods' shared with TESSD in March 2023. The report aims to share additional
evidence on barriers to trade and steps that can be taken for these to be
overcome. The report outlines a number of key findings:
OSW has been identified as a key technology for achieving
climate mitigation objectives. Over the past year
there has been an increased focus on developing the OSW industry. However, the
International Energy Association and the International Renewable Energy
Association anticipate that OSW capacity
will need to exceed 2000GW in 2050 from just over 60GW today to reach net zero.
Whilst OSW contribution to climate mitigation is widely recognised, challenges
remain relating to end-of-life disposal of turbine blades, which often end up
in landfill.
OSW energy generation is
associated with a wide variety of services, however regulatory barriers
continue to restrict their delivery.
Key services include engineering and construction, in addition to maintenance
and repair services. Ancillary services such as research and development,
financial services, insurance, and consultancy are additionally utilised. Key
barriers include restrictions to services using electronic networks,
challenges concerning the environmental services workforce (such as quotas, labour
market test, limitation on duration of stay and citizenship requirements) and
failure to recognise international qualifications.
Value chain diagrams can be used to visualise the input and
intermediate goods involved in making final OSW goods. The report showcases a series of value-chain
diagrams for an OSW farm, mapping out the services and material inputs required
across the value chain. The diagrams have been further annotated with
illustrative commodity codes. The diagrams intend to increase transparency
around the processes involved in the development of UK OSW farms. In addition,
the diagrams form the basis of the report's analysis of where tariff or
non-tariff-based interventions to accelerate the trade of OSW could be most
effective.
Tariff-barriers to trade
of goods are identified throughout the OSW value chain, highlighting the
importance of taking a value-chain led approach. Analysis of the
value-chain diagrams enables identification of where higher tariffs may be
affecting dissemination and uptake of OSW goods. High tariff rates apply to
numerous input, intermediate and final goods across the offshore wind value
chain. This analysis demonstrates the value of taking a value-chain led
approach to analysis of tariff-barriers to environmental goods to ensure that
any intervention to address tariff-barriers considers all stages of the value
chain.
There are a number of broader challenges affecting trade of
OSW goods, thereby posing a barrier to dissemination of OSW technologies. Whilst reduced tariff
rates could reduce cost pressures across the OSW value-chain, it is critical to
consider non-tariff measures alongside any adjustment to tariff rates. The
following broader challenges facing trade in OSW have been identified:
Potential Barriers
|
Description
|
Local
Content Requirements
|
Local
Content Requirements are associated with a decline in trade and a loss in international
competitiveness in the countries imposing the measure. LCRs are often
imbedded in government's contacts, permits and incentives for renewable
energy projects. Subsidies which are contingent on the use of domestically
produced goods over imported goods are prohibited under the WTO's Agreement
on Subsidies and Countervailing Measures.
|
Guidance
Accessibility
|
Guidance
for auctions for OSW projects can lack transparency. Guidance should provide clear instruction
on how to commence projects for OSW investors/developers.
|
Procurement
issues
|
Local content requirements
attached to tenders in relation to procurement appear to act as a trade
barrier against third country suppliers.
|
Port
infrastructure
|
Port
infrastructure globally needs to be upgraded to reflect the growth in
investment in OSW to avoid port infrastructure being a bottleneck.
|
Foreign
Ownership Caps
|
Foreign ownership caps in the
OSW sector have curbed foreign investment. Relaxing these caps may allow
foreign companies to hold majority shares in projects, thereby accelerating
overseas involvement and skills transfer.
|
Feed-In
Tariffs (FIT)
|
FIT rate
negotiations can act as a barrier to trade when the
proposed FIT rate is misaligned from costs of energy or local production
costs. Supporting the spread of best practice in Power Purchase Agreements
and establishing reasonable FIT rates is key to allow OSW developers to
operate effectively across different international markets.
|
The
environmental benefits of wind energy are well understood. Reference is made
below to several useful and credible resources which support this.
The UN Climate Technology Centre and Network (CTCN) clearly
sets out that due to the renewable nature of wind energy, the large resource
availability, and the relatively advanced nature of the technology, wind energy
technologies have the potential to make a significant contribution to climate
change mitigation efforts. The uptake of wind energy can displace generation
from thermal power plants, which can prevent rises in CO2 emissions.[1]
Project Drawdown documents the impact
that OSW energy solutions have according to growth in energy output and
avoidance of GHG emissions worldwide:
"Offshore
wind turbines growing from the current estimated 60 terawatt-hours, to
1,850.04–2,175.56 terawatt-hours by 2050, could avoid 10.22–9.89 gigatons of
greenhouse gas emissions."
The International Energy Association (IEA)
stress that while OSW represents a small fraction of current power generation, it is important to prioritise efforts in this
area since improvements in technology and steep cost reductions make harnessing
the near limitless potential of wind within our collective grasp. Indeed, the
IEA have reported record growth in wind electricity production in 2021 (up
273TWh or 17%) – 55% higher than for 2020, and the highest growth among all
renewable power technologies.[2]
Both the International
Renewable Energy Association (IRENA) and the IEA have said they
expect OSW capacity will need to exceed 2000 GW in 2050, from just over 60 GW
today to achieve net zero. The Global Offshore Wind Alliance (GOWA), launched
at COP27 in November 2022, have pledged to a rapid ramp up of OSW, aiming to
accelerating growth to reach a total of at least GW installed capacity by
the end of 2030. This work includes active collaboration to remove barriers to
the deployment of OSW in new and existing markets.[3]
The UNIDO ITPO
Tokyo STePP platform describes the major features and advantages of
a mid‑sized wind turbine.[4]
A common problem for the deployment of wind energy in regions prone to periodic
high wind conditions is that the turbines can become damaged during extreme
weather events or other natural disasters. The platform documents a
medium-sized turbine which is designed to be easily transportable, relatively
simple to install, with strong lightning and earthquake protection, and
resistant to extreme and unstable winds (beyond the requirements of the
relevant IEC standard).
Similarly, the World
Intellectual Property Organisation's (WIPO) Marketplace for Sustainable
Technologies contains entries for typhoon-proof wind turbines[5],
among a variety of other wind energy technologies.[6] This resource shows not
only that there are a wide array of benefits to be realised from the uptake of
these technologies, but also that these technologies frequently have a high
Technology Readiness Level (TRL). This resource also documents a wide variety
of cooperation types under which wind energy technology transfer is possible
under voluntary but mutually agreed terms.
The
benefits to the environment from the uptake of wind energy are clear from the
sources above. Industry is now homing in on the outstanding lifecycle
challenges associated with select components
to maximise the environmental compatibility of this technology. A selection of
these challenges has been outlined below.
The disposal of turbine blades poses a challenge
during the end-of-life stage of a turbine's lifecycle, with the average blade
typically having a lifespan of 25-30 years.[7]
Whilst 85-90 % of wind turbines' total mass can be recycled, this is not the
case for the blades, which often end up in landfill.[8],[9]
Turbine blades are made from reinforced fibres (typically glass or carbon
fibres) and a polymer matrix. Whilst they are non-toxic and landfill safe,
commercially viable recycling methods are limited.[10]
The majority of currently viable recycling methods
are some form of 'down-cycling', where the new material produced is of lower
quality than the original material. Many recycling methods that produce higher
quality material involve much higher energy costs, however more research is
needed for accurate life cycle assessment of these techniques.[11],[12]
New materials are under development which can be
used for wind turbine blades that are more easily recycled into useful
products, however it remains to be seen whether these materials will be
economically viable at scale. In the meantime, the challenge remains regarding
how current turbine blades are disposed of when they are decommissioned, with a
predicted 43 million tonnes of blade waste being produced worldwide by 2050.[13]
[7] J. Beauson, A.
Laurent, D.P. Rudolph, J. Pagh Jensen. (2022). 'The complex end-of-life of wind
turbine blades: A review of the European context'. Renewable and Sustainable
Energy Reviews, Volume 155.
[11] Beauson, J.,
Laurent, A., Rudolph, D., Pagh Jensen. (2022). 'The complex end-of-life of wind
turbine blades: A review of the European context'. Renewable and Sustainable
Energy Reviews, Volume 155. Accessed 20/09/2024. Link: https://doi.org/10.1016/j.rser.2021.111847.
[13] Liu, P., Barlow, C. (2017). 'Wind Turbine Blade Waste in 205'. Waste Management, Volume 62. Accessed 20/09/2024.
Link: https://doi.org/10.1016/j.wasman.2017.02.007.