Event:16 September | Carbon Removal Policy Summit
Legal Limits on Residual EmissionsStandards and Obligations

LEGAL LIMITS ON RESIDUAL EMISSIONS

Lever last updated: 14 September 2026

A statutory cap on the emissions allowed to remain at net zero.

Cost

Very low to Low

The authority pays for drafting, sector analysis, consultation and periodic reassessment. A simple reduction floor can use existing inventories; detailed tests of unavoidable emissions require more specialist review. The investments needed to reduce emissions are separate from administering the rule.

Complexity

Medium to High

A statutory reduction floor requires legislation and consistent emissions accounts. Sector-specific definitions also need technical assessment, exemption procedures, appeal or review arrangements and coordination across climate, industry and planning authorities.

Timeline

Short to Medium

From formal initiation, amending an existing climate law can change sector plans within one to two years. Developing sector tests and implementing rules may take two to five years before authorities apply the limit in planning or compliance decisions.

Integrity, Transparency & MRV

2–4

Innovation & Cost Reduction

N/A

Social & Environmental Safeguards

N/A

Energy, Transport & Storage Infrastructure

N/A

Inputs & Capacity

N/A

Demand Formation

N/A

Bankability and Cost of Capital

N/A

Policy Architecture & Coordination

2–4

Overview

Lawmakers set a legal limit on the greenhouse-gas emissions that may remain at net zero. They can require a minimum reduction from a stated baseline, or define the circumstances in which particular emissions may be treated as residual and balanced with removals. The purpose is to stop the remaining quantity from expanding simply because emissions cuts prove inconvenient. Before setting the limit, government needs evidence that the required changes are achievable across the affected sectors. A credible rule combines a clear reduction requirement with transparent treatment of technical constraints, costs and essential services, and a process for revisiting those judgments as alternatives improve.

Key Considerations

The authority must define the emissions baseline, covered activities and target year before assessing how much can realistically be eliminated. Sector assessments should examine available substitutes, plant size, operating patterns, energy needs and access to supporting infrastructure. An installation should not be assigned a capture requirement solely because capture is technically possible; the cost and practicality of that installation's reduction options also matter. Where temporary exceptions are justified, the law should state the evidence required, who approves them and when they expire. For bioenergy, accounting must distinguish biogenic carbon from fossil emissions and assess net removal separately; difficulty adding capture does not itself establish a residual fossil-emissions allowance.

Opportunities

A published legal limit gives sectors a clearer expectation of the emissions cuts required and helps planners estimate how much balancing with removals may be needed. Transparent assessment of alternatives exposes where a claimed technical constraint is actually a temporary cost, infrastructure or operating problem. Periodic reassessment creates a route for tightening requirements as those problems are resolved. Separate gross-emissions and removal accounts also make it easier to see whether policy is delivering genuine reductions or merely increasing the amount expected from future CDR.

Risks

An unrealistically tight requirement may demand equipment that cannot operate economically at the relevant scale, infrastructure that will not be available in time or changes that undermine an essential service. A generous or poorly evidenced exemption can have the opposite effect, preserving avoidable emissions indefinitely. A single percentage applied uniformly to every company ignores differences between sectors and installations. Authorities therefore need transparent assessments and reviewable exceptions, while guarding against selective evidence and lobbying that turn temporary constraints into permanent allowances.

Monitoring and Evaluation

Evaluation should compare gross emissions, removals and the residual ceiling by sector and year. Reviews should test whether activities classified as unavoidable now have workable alternatives, whether exemptions remain justified and whether sink losses change the balance. Independent reporting can expose reclassification, accounting gaps and delayed reductions. Authorities should use that evidence to revise exemptions, tighten limits or require corrected sector plans.

Stakeholder Engagement

Engineers, operators and infrastructure providers should supply evidence on technically workable alternatives, costs, deployment times and constraints at different installation sizes. Economists and independent technical reviewers should test those claims rather than accept a sector's preferred assumptions. Workers and service users should explain consequences for livelihoods and essential services. Inventory experts must keep fossil emissions, biogenic carbon and net removals distinct, while legislators decide the acceptable trade-offs and conditions for any exception.

Governance Levels

SupranationalNationalRegional / State

Supranational, national and regional/state lawmakers can establish gross-reduction requirements and residual-emissions rules through climate legislation within their competence. The designated regulator applies sector tests and any exemption or review procedure. National and subnational authorities need compatible accounts where their rules cover the same emissions. Companies and other organisations can supply feasibility evidence or adopt voluntary limits, but the public authority decides the legal restriction.

Implementation Strategies

  • Lawmakers should choose a gross-reduction floor, a test for unavoidable emissions or a combination. A numerical floor fixes the overall limit; sector tests can explain which remaining activities justify using that allowance.

  • The rule should define the baseline, gases, sectors, land accounting and treatment of international transfers. Inventories should retain enough detail to distinguish actual gross reductions from changing accounting conventions.

  • Any sector or installation exception should require published evidence on achievable alternatives, costs, plant scale, infrastructure and essential services. The authority should assign an expiry or review date and explain what developments would justify tightening or ending the exception.

  • Reviews should revisit residual categories as technologies and practices improve. Authorities should publish gross emissions, removals and the residual balance separately, then require delivery plans to reflect any revised limit.

Case Studies

Portugal Climate Framework Law

Portugal’s 2021 Climate Framework Law requires emissions outside land use and forestry to fall at least 90 per cent from 2005 by 2050. It separately sets an average land-sink objective of at least 13 million tonnes of CO₂ equivalent for 2045–2050. The separate accounts prevent a larger land sink from substituting for the minimum emissions reduction. The law therefore establishes a quantitative ceiling on the emissions remaining in the covered account. It does not define every remaining tonne as technically unavoidable or cap all removal activity at 10 per cent. A complete residual-emissions regime would also explain which activities may use that remaining allowance.

California gross-reduction requirement

California’s 2022 Assembly Bill 1279 combines net zero by 2045 with a requirement to reduce gross anthropogenic emissions at least 85 per cent below 1990 levels. The state’s Air Resources Board must incorporate the objectives into its climate planning. Separating gross reductions from net balance constrains how much reliance on removals can substitute for cutting emissions. The remaining share is an economy-wide limit, not an automatic entitlement for each company to continue emitting 15 per cent of its baseline. The legislation illustrates the quantitative form of the lever; it does not establish a sector-by-sector test of which emissions are unavoidable.

More Standards and Obligations

©2026 Alexander Mäkelä and Carbon Gap.
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Headline and barrier scores based on Carbon Gap analysis.