Standards and ObligationsCARBON REMOVAL TARGETS
Lever last updated: 14 September 2026
A specific, standalone quantity of carbon removal government commits to achieving by a set date.
Cost
Very low to Low
Public authorities pay for inventories, removal scenarios, consultation and progress reviews. A local target can reuse existing land and climate accounts; a national target needs broader sector analysis. Removal purchases and deployment support are budgeted through the chosen delivery programmes.
Complexity
Low to High
A policy target can use established inventories and planning powers. A binding national target may require legislation, new removal accounts and assigned responsibilities across ministries, particularly when land sinks and engineered removals are assessed separately.
Timeline
Short to Medium
A target based on existing public accounts can change the next programme or spending plan within one to two years. New legislation, removal accounting and departmental responsibilities may need two to five years before the target materially changes decisions.
Integrity, Transparency & MRV
Innovation & Cost Reduction
Social & Environmental Safeguards
Energy, Transport & Storage Infrastructure
Inputs & Capacity
Demand Formation
Bankability and Cost of Capital
Policy Architecture & Coordination
Overview
A public authority sets a specific quantity of carbon removal to be achieved across its territory or a defined sector by an agreed date. The target might specify an annual rate of net removals or a cumulative amount over several years. Stating that quantity separately from emissions-reduction goals gives ministries and public agencies a common scale against which to plan land management, project support and infrastructure. Separate targets can be used for land sinks and more durable removals where their delivery conditions differ. The goal may be written into law or adopted as government policy; achieving it requires the responsible authorities to put delivery measures and resources in place.
Key Considerations
The authority must decide whether the target covers the total net land sink, additional removals beyond an existing baseline, or specified removal methods. Annual rates and cumulative tonnes should be stated separately, with geography, storage duration and interim dates made explicit. Delivery assumptions need to reflect land condition, feasible projects and available infrastructure. The responsible departments should explain what happens after a missed milestone or a reversal. Where overseas removals contribute to the public target, national accounting must follow the applicable rules for authorised international transfers.
Opportunities
An explicit public removal quantity gives programme managers a basis for testing whether planned support is large enough and whether action starts soon enough. Land managers and infrastructure providers also gain a clearer view of the intended scale of activity. Separating removals from emissions cuts makes it easier for legislators and the public to question unrealistic assumptions or unexplained shortfalls. Milestones can bring those questions into current spending and policy decisions, while leaving the government free to choose the mix of measures used to deliver the goal.
Risks
One aggregate target can obscure whether the government is protecting an existing sink or adding new removals, and whether the carbon will remain stored for comparable periods. Overoptimistic volumes may encourage delay in emissions cuts or plans for projects that cannot be delivered. Targets unsupported by public measures can remain symbolic. Inconsistent national and international accounting may then overstate progress, while abrupt changes in the goal undermine the assumptions used for land and infrastructure planning.
Monitoring and Evaluation
Evaluation should compare delivered net removals with each milestone, separating annual from cumulative quantities and land sinks from more durable storage. Reports should identify the responsible actor, funded measures, forecast shortfalls and corrective decisions. Independent checks should distinguish a changed forecast from a weakened target and prevent contracted future tonnes from being reported as delivered.
Stakeholder Engagement
Engagement should test whether the proposed volumes, timing and method mix are credible and fair. Removal suppliers, land managers, infrastructure operators and scientists bring delivery evidence, while affected communities, climate councils, finance authorities and civil society can scrutinise safeguards, public cost and reliance on uncertain future capacity.
Governance Levels
Supranational institutions can agree collective removal objectives and allocate national contributions within their powers. National governments can set territory-wide or sector-specific goals and assign departmental responsibility. Regional, state and municipal governments can set goals for areas and activities within their remit, coordinating with wider inventory and land-use rules. These authorities control the public commitment and associated planning; delivery may involve private landholders and companies without making those actors the target setter.
Implementation Strategies
Target setters should establish separate gross-emissions and removal pathways with interim volumes. Land and engineered removals, storage durations and uncertainty should be visible so that an aggregate total does not hide incompatible assumptions.
The authority should assign delivery responsibility, ownership of the relevant inventory, public reporting and a process for correcting shortfalls before adopting the target. Each department needs to know which part of the goal it is expected to help deliver.
Each milestone should connect to the policies, purchasing decisions and infrastructure expected to deliver it. The plan should identify which measures are funded, which remain proposals and how delivery risk will be managed.
Fixed reviews should compare verified progress with milestones and update future assumptions transparently. A changed forecast should not erase the record of a missed commitment or conceal rising gross emissions.
Case Studies
European Union land-use and forestry target
The EU’s 2023 land-use and forestry legislation sets a collective objective of 310 million tonnes of net CO₂-equivalent removals in 2030, supported by national targets and a 2026–2029 budget period. Common accounting and allocated national responsibilities turn the Union figure into requirements governments must reflect in land-sector policy. The target concerns the net balance of forests and other managed land, including emissions as well as removals. The legislated objective carries compliance duties, but does not establish a separate target for engineered CDR or demonstrate that the 2030 sink will be delivered.
Germany’s statutory sink targets
Germany’s Federal Climate Change Act sets land-sector net-sink objectives of at least 25 million tonnes of CO₂ equivalent for 2030, 35 million for 2040 and 40 million for 2045. Each is assessed using the average of the target year and the preceding three years. The responsible federal ministry must propose and implement measures, making the targets an allocation of policy responsibility rather than a forecast alone. The Act also specifies climate neutrality by 2045 and an objective of negative emissions after 2050. These legislated land targets do not themselves specify an engineered-removal volume or establish that the required sink strength has been achieved.
United Kingdom engineered-removal ambition
The UK government's 2021 Net Zero Strategy set an ambition to deploy at least five million tonnes of engineered removals annually by 2030. Giving removals their own quantity and date provided a scale against which government could design commercial support and assess progress. This was a policy ambition, rather than a requirement that a named purchaser buy the stated volume. By June 2026, the Climate Change Committee was warning that the government's later pathway relied on rapid expansion after 2030 without sufficient delivery detail. The example shows both the value of an explicit public removal objective and why the supporting project pipeline, infrastructure and funding must be tested separately from the target.
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Cost
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Complexity
Medium to High
Timeline
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Integrity, Transparency & MRV
2–3Innovation & Cost Reduction
2–4Social & Environmental Safeguards
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N/AInputs & Capacity
1–3Demand Formation
2–4Bankability and Cost of Capital
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Minimum carbon-storing content requirements
A legal minimum share of durably stored atmospheric carbon in covered products.
Cost
Low to Medium
Complexity
High
Timeline
Medium to Long
Integrity, Transparency & MRV
3–4Innovation & Cost Reduction
2–3Social & Environmental Safeguards
2–3Energy, Transport & Storage Infrastructure
N/AInputs & Capacity
2–3Demand Formation
4–5Bankability and Cost of Capital
2–3Policy Architecture & Coordination
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Low-carbon fuel standards
A tightening ceiling on the average lifecycle carbon intensity of transport fuel.
Cost
Low to Medium
Complexity
High to Very high
Timeline
Medium to Long
Integrity, Transparency & MRV
2–4Innovation & Cost Reduction
2–3Social & Environmental Safeguards
1–3Energy, Transport & Storage Infrastructure
1–2Inputs & Capacity
1–3Demand Formation
2–3Bankability and Cost of Capital
1–3Policy Architecture & Coordination
2–3©2026 Alexander Mäkelä and Carbon Gap.
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Headline and barrier scores based on Carbon Gap analysis.