EU Directive

Making sense of the Renewable Energy Directive

To help deliver on the EU’s increasing climate ambitions, including the EU-wide 55% emissions reduction target by 2030 and the target to achieve net neutrality by 2050, the targets set by the RED have been repeatedly increased. As a result, the RED has evolved from RED I to its latest version, RED IV. Starting from a target of 20% RES as a share of total final energy consumption by 2020 set in 2009, RED I was revised as part of the “Clean energy for all Europeans” package in 2018 to include a target of a 32% RES share by 2030, thereby becoming RED II.

In July 2021, as part of the “Fit-for-55” package, RED III was proposed and the target was raised to 40% by 2030. Following the Russian aggression against Ukraine, the Commission proposed a first amendment (RED IV) with a target of 45% as part of its “REPowerEU” plan. In November 2022, the Commission proposed a second amendment for a Council regulation to accelerate RES deployment.

In March 2023, the EU Parliament and the Council reached a tentative agreement to raise the target to a 42.5% RES share by 2030. Member states will need to increase their national contributions in their integrated National Energy and Climate Plans (NECP), which are due to be updated in 2023 and 2024, to collectively achieve the target. Achieving the target would bring EU member states’ total renewable energy generation capacity to 1236 GW by 2030.

RES considered within the RED’s scope include wind, solar, hydro, tidal, geothermal, and biomass. The binding target is supported by differentiated targets for a variety of sectors, such as heating and cooling, industry, and transport. The provisional agreement under RePowerEU also aims to remove barriers to the scale-up of renewable energy generation by making permitting processes for renewable energy installations quicker and easier. To this end, member states will define regions (so-called ‘go-to areas’) with limited environmental risks and high renewable energy generation capability, in which the permitting procedure shall be simplified. 

The RED and its impacts on biomass use

Biomass is considered a RES within the provisional agreement, provided that its use meets several sustainability criteria. These include requirements that woody biomass used in energy generation follows the cascading principle – ensuring that biomass of higher quality should serve purposes demanding higher-quality biomass first – and that forest biomass may not be harvested from areas with particular significance with regard to carbon stocks or biodiversity. Furthermore, no financial support shall be granted when energy facilities use stumps and roots for energy generation (as they are considered important, for example, to protect soil carbon stocks) or when they use high-quality biomass that should be reserved for other use cases under the cascading principle, such as industrial-grade roundwood, veneer logs, and saw logs.

The provisional agreement sets out a new binding combined target of 5.5% for advanced biofuels, generally derived from non-food-based feedstocks, and renewable fuels of non-biological origin, mostly renewable hydrogen and hydrogen-based synthetic fuels, in the share of renewable energy supplied to the transport sector. The increasing need for advanced biofuels that use biomass as a feedstock may conflict with the demand for the lower-quality biomass upon which several CDR methods rely, such as BECCS and biochar.

Where does BECCS fit in?

The recognition of biomass as a renewable energy source affects the feasibility and potential scale of BECCS. BECCS can both provide renewable energy and remove carbon dioxide from the atmosphere. The 2021 proposal states that member states should not support electricity production from installations producing only electricity, as opposed to, for example, installations producing both heat and power), unless these installations are located in regions included in the Just Transition Plan, or if the installations used CCS technologies to capture and store the associated (biogenic) CO2 emissions.

Currently, negative emissions stemming from BECCS cannot contribute towards targets set under any of the three main legislative pillars of EU climate action, namely the EU Emissions Trading System (EU ETS), the Effort Sharing Regulation (ESR), and the LULUCF Regulation.

The RED: Are sustainability criteria enough to ensure the sustainable use of biomass?

The role of biomass within the RED is important. While sustainability criteria exist to prevent the misuse of biomass for energy generation, the demand for biomass may increasingly exceed supply. Some communities might be adversely impacted, especially in terms of resource use and food security. It is therefore critical that future revisions of the RED take these concerns into consideration.

Update to the ETS

The ETS was revised as part of the Commission’s ‘Fit for 55’ package, which aims to introduce new or improve existing legislative tools for achieving the EU’s target of reducing net GHG emissions by at least 55% below 1990 levels by 2030. The proposed changes to the ETS include:

• Increased ambition to reduce emissions by 62% in the sectors covered by the ETS by 2030  and reduction of the cap by 4.3% per year in 2024-2027, and by 4.4% in 2028-2030.
• End of free allowances for sectors covered by the Carbon Adjustment Mechanism (CBAM) in 2026-2034.
• Phase-out of free emission allowances for aviation (25% in 2024, 50% in 2025 and 100% from 2026).
• Inclusion of maritime shipping in the ETS.
• Creation of a separate ETS for the building and road transport sectors, applying to the distributors that supply fuels for combustion. A new Social Climate Fund will direct part of the revenue from the auctioning to support vulnerable households and micro-enterprises.
• Increase in the Modernisation Fund and Innovation Fund.
• Strengthening the market stability reserve (MSR), the mechanism to help prevent excessive carbon price fluctuations.

Support for CDR through the Innovation Fund

Although the EU ETS is designed to incentivise emissions reductions as opposed to carbon removals, money raised through auctions of emission allowances under the ETS are reinvested into the EU’s Innovation Fund, which provides a source of funding support for technology-based CDR methods among other low-carbon technologies.

For more information on the link between CDR and the Innovation Fund, see here.

Should carbon removal be integrated into the EU ETS?

The inclusion of carbon removal (with permanent storage of captured carbon) in the EU ETS is subject to a nascent and growing debate in the EU policy ecosystem, in anticipation of the announced Commission report. Integrating negative emissions into the ETS would allow participants to offset a portion of their emissions by purchasing carbon removal credits. This, in turn, could create a potential long-term market for CDR.

Including removals in the EU ETS could have a number of benefits. As the ETS allowance cap is steadily reduced over time, integrating negative emissions would create additional market liquidity and decarbonisation options for hard-to-abate sectors. It would therefore help to satisfy demand for removal credits or allowances from hard-to-decarbonise sectors like aviation and would allow for carbon removal credits to be easily integrated into existing market infrastructure and trading platforms.

Carbon removal project developers and investors would gain greater confidence that there will be sustainable long-term demand for carbon removal credits. It would also allow removal projects to benefit from the carbon price. However, the price differential between the cost of CDR and the EU ETS carbon price will be a key consideration. The EU ETS would only incentivise CDR solutions within a certain range of the ETS price. This could be sufficient for some approaches such as BECCS (cost at scale  USD 15 – 400/tCO₂) and waste-to-energy with CCS, but additional incentives would be needed for direct air capture given its higher price point (cost at scale USD 100 – 300/tCO₂) – although this is expected to change as technologies improve and costs of different methods decrease. Complementary incentive mechanisms such as Carbon Contracts for Difference (CCfDs) could bridge the gap between the actual cost of certain CDR methods and the EU ETS carbon price to drive the investment needed. The Commission is considering CCfDs as part of the overall agreement on the revision of the ETS Directive.

However, it is imperative that the potential inclusion of carbon removal credits in the EU ETS does not undermine the incentive for emitters covered by the ETS to decarbonise, or the urgency with which they should do so. One option to address this risk would be to limit access or quantities of removals to specific sectors that are harder to decarbonise and more likely to have residual emissions.

Another important consideration is the impact that any inclusion of CDR in the EU ETS would have on the integrity of the market. Developing robust monitoring, reporting and verification (MRV) standards would safeguard the integrity of the ETS. The introduction of these standards is underway under the EU’s CRCF legislation.

An alternative approach might be establishing a separate, regulated negative emissions market. This separate market could later be linked with the EU ETS after the differential between CDR and ETS prices has been reduced and CDR technologies have a demonstrated track record at scale.

The EU ETS & other markets

The EU ETS was the world’s first international emissions trading system when it was set up in 2005. It has since inspired the development of emissions trading in other countries and regions, including most recently the UK and China. The potential role of the UK ETS as a market for CDR has been explored through a call for evidence published by the UK ETS Authority in 2022, the outcome of which is expected in 2023. In 2017, the EU and Switzerland signed an agreement to link their emissions trading systems. The agreement entered into force on 1 January 2020, and the link became operational in September 2020.

Context of the law

In 2021, the European Parliament requested that the Commission develop an EU-wide common legal framework for the protection and sustainable use of soil. The 2023 Framework proposal followed up on this request. Soil health also plays a key role in delivering existing EU strategies and targets, including the EU Biodiversity Strategy for 2030, the EU Soil Strategy for 2030 and the 8th Environment Action Programme.  

Reaching the new climate objectives set under the European Green Deal, as well as ensuring a stable food supply, relies on healthy soils. In the proposal, the Commission reports that an estimated 61% to 73% of agricultural soils in the EU are affected by erosion, loss of organic carbon, nutrient exceedances, compaction or secondary salinisation, or a combination of these threats, which not only impacts soil carbon sequestration but also food production capacities. For example, crop yields can be reduced by 2.5-15% by soil compaction. It is estimated that around 75 billion tonnes of organic carbon are stored in EU soil. As a point of reference, the EU’s total CO2 emissions were about 4.5 billion tonnes in 2017.  

What does it look like in practice?

The proposal for a directive applies to all soils in the territory of member states. Under the Framework, member states are required to delineate their territories in ‘soil districts’, which is a newly defined governable unit introduced in the directive. Some loosely defined parameters to determine soil districts are laid out in the proposal. A competent authority designated by each member state will be assigned for each soil district. Member states are then required to establish a monitoring framework based on a set of criteria laid out in the directive, ensuring comparability of measurement across soil districts and member states. Most importantly, the European Union now has a measurable definition of soil health. Using this framework, member states are required to accurately and regularly measure soil health. The Directive lays out methodologies to do so and an obligation to measure soils at least every five years.   

Under this proposed directive, member states would also be required to set up a mechanism for voluntary soil health certification, viewed as a way to incentivise the uptake of sustainable soil management practices by land owners. As per the current proposal, this certification would be complementary to the Carbon Removal Certification Framework (CRCF). This linkage is still unclear and needs to be further clarified by the Commission.

Room for improvement

The Commission’s plan to create a strong soil health monitoring framework is a positive move for Europe. It will help foster healthier soils, potentially leading to greater quantities of carbon being absorbed. Carbon Gap especially welcomes the establishment of measurable common thresholds for soil health across a wide range of variables, minimum criteria for determining sampling points, an EU-wide soil health assessment and reporting system, and a digital portal to make soil data publicly accessible as important steps towards boosting Europe’s soils through a harmonised framework.  

However, it is important to recognise that monitoring soil health does not necessarily mean that soil health will be improved. The proposed directive would better serve its purpose if it included a legally-binding target for soil health by 2050 holding member states accountable for their stated goal. Another concern is that the proposed frequency of measurement and the timelines for reporting cycles is insufficient. Effectively, if the law enters into force as it stands today, the first soil measurements would only be required within four years. New soil measurements would then be required every five years, meaning that it would take close to a decade before a clear view is established of whether EU soils are recovering, protected or enhanced.  

While the Commission’s desire to incentivise sustainable soil management principles is welcome, its proposed mechanism of soil health certification for land owners and managers raises concerns. The suggested link to the CRCF warrants scrutiny as soil health and soil carbon are not interchangeable, soil carbon fluxes are difficult to measure accurately at scale, and the durability of soil carbon storage is low. Therefore, soil health certificates should not be sold as carbon credits or used to contribute toward net-zero targets. Rather, these certificates might be supported by entities wanting to make contribution claims or do good for the environment and society.

Policy Landscape

The Green Claims Directive complements the Empowering Consumers Directive published by the European Commission on 30 March 2022 within the EU Together, they aim to improve the circularity of the EU’s economy and achieve climate neutrality. They respectively set requirements to substantiate environmental claims made to consumers and and other commercial practices.

Apart from the French ministerial decree n°2022-538, the Green Claims Directive is a first of its kind in the specificity with which it regulates environmental claims and addresses climate-neutrality claims. The French decree regulates advertising claims based on emission compensation projects. It has different requirements surrounding emissions reporting, compensation data, and net zero plans.

Aim

The Green Claims Directive proposal addresses the issue of greenwashing, increasingly prevalent in recent years. It seeks to standardise environmental claims and labels to improve transparency and credibility for consumers. The proposal aims to use delegated and implementing acts in the future to address substantiation methodologies for specific product groups and evolving commercial practices.

The preamble of the proposal states that climate-related claims are prone to being unclear and misleading, as they are often based on offsetting greenhouse gas (GHG) emissions through carbon credits of low environmental integrity and credibility, generated outside the company’s value chain and calculated based on methodologies that vary widely in transparency, accuracy, and consistency. Offsetting can also deter traders from reducing emissions in their own operations and value chains.

However, credible net zero claims have the potential to incentivise and drive the development of safe, just and sustainable carbon removals to transition towards real climate neutrality. Claims based on offsetting must be regulated through a robust and science-based system to prevent greenwashing.

Room for improvement

Unfortunately, the Green Claims Directive as it currently stands does not establish the necessary measures to do so:

• The Directive does not align with scientific consensus as it allows offsetting through emissions reductions and avoidance to substantiate carbon neutrality claims. The IPCC’s definition of net zero is clear: balancing emissions with physical removals. Accordingly, offsetting projects that avoid emissions, but do not physically remove and store carbon, must be barred from use in substantiating claims about net climate impacts.
• The proposal rightly requires companies to report GHG emissions separately from offsetting data, to disclose the share of their total emissions that are addressed through offsetting and whether these come from emission reductions or removals. This isn’t enough to monitor whether the claimed climate impacts are real There is a need for more extensive disclosure on the types of carbon credits companies are purchasing (avoidance, reduction, removals), which emissions they are claiming compensation for, and the methodologies used to ensure integrity and correct accounting.
• The proposal allows all types of offsetting without any clear criteria for which emissions they can compensate for, nor which climate claims they can substantiate. However, not all carbon storage is equal in terms of capacity, duration or reversal risk. This means that long-lived fossil fuel emissions otherwise impossible to abate can only be balanced by removals with high-durability storage in the geosphere where the carbon came from. Lower-durability removal and storage of carbon into the biosphere must be accelerated for its own sake, to halt and reverse the loss of ecosystems and natural carbon stocks but cannot be eligible to compensate for fossil fuel emissions. Failing to enshrine this non-fungibility principle in EU law would allow companies to continue offsetting their long-lived emissions through shorter-term carbon storage with higher risks of reversal.
• Although the Directive encourages companies to use offsetting only for residual emissions, it provides no robust definition for what constitutes these residual or ‘hard-to-abate’ emissions. Without a sector-specific and measurable definition, companies can weaken emission cutting efforts by manipulating the boundary between ‘emissions that must be reduced’ and ‘emissions that physical removals can offset’. The EU will need to establish a transparent process for classifying emissions as difficult-to-decarbonise.
• The proposal excludes from its scope environmental claims and labels substantiated by rules in the Carbon Removal Certification Framework (CRCF). However, the proposal for the CRCF has no rules for claim substantiation. Instead, the Green Claims Directive could establish guardrails for legitimate net zero claims, which could be substantiated through the purchase of high-quality carbon removal credits certified under the CRCF.

The CCS Directive was originally designed to assist the EU in meeting its CO₂ reduction obligations through capture and geological storage of CO₂. It is an essential tool to enable the activities for CO₂ management and, as such, an important tool in the CDR regulatory toolkit.

The CCS Directive governs the geological formations in which carbon can be stored. Member States are required to cooperate with the Commission to establish maps of existing, potential, and closed geological storage sites. The Directive also requires operators and competent authorities to establish 3D dynamic models of storage complexes, including protected natural areas. These data offer a critical resource for developing Europe’s carbon management plans, including CDR.

Transborder CO₂ movement

The Directive also includes provisions for the transport of CO₂ across borders and for storage reservoirs which span multiple countries. This is an important base on which to develop a modular CDR ecosystem where facilities employing CO₂ capture and storage sites might be located across Europe with CO₂ transported across national borders.

The recent revision (2022) of the Trans-European Networks for Energy (TEN-E) Regulation, which identifies priority corridors and priority thematic areas to develop and interconnect, updated the infrastructure categories eligible for support allowing CO₂ transport infrastructure to qualify as a Project of Common Interest (PCI). 14 such projects have already been submitted to the PCI selection.

Implementation

The implementation of the Directive varies across Europe. In addition to the restrictions allowing CO₂ storage only in geological formations which are permanently unsuitable for other purposes (see the EU’s Water Policy), Member States retain the right to not allow geological storage in parts or all of their territory (for example, Germany currently limits the amount of CO₂ that can be geologically stored annually to 4 million tonnes and does not allow new demonstration projects to be approved, meaning there is no underground geological storage of CO₂ taking place). CDR operators dependent on geological storage will have to navigate this fragmented regulatory landscape.

The information on the practical application of the Directive is limited, despite it being in force for more than 10 years. The uptake of CCS in Europe has been slower than predicted and the rules have not had the chance to demonstrate their effectiveness. The lack of CCS projects has largely been due to the low carbon price and absence of policy support measures to enable the deployment of CCS. Still, the Directive requires a rigorous reviewing process prior to permitting, which makes for intensive work on both storage applicants’ and the national authorities’ side. In any event, the European Commission’s upcoming strategic vision for CCS and CCU might yet provide the necessary fuel to jumpstart the industry and stress test the CCS Directive.