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16 Technology-Based Carbon Pathway · TTS Annex H
🛢️

Bio-oil Geological
Storage
TTS v1.0 - Annex H

Bio-oil Geological Storage converts sustainably sourced biomass into a viscous, carbon-rich liquid through fast pyrolysis, then injects that bio-oil into deep geological formations for long-term storage. Unlike gaseous CO₂ injection, bio-oil is a stable liquid at ambient conditions with far lower buoyancy and mobility - reducing the risk of upward migration and offering a simpler, lower-cost storage engineering profile than supercritical CO₂ injection, while achieving the same underlying goal: durably removing atmospheric carbon captured by growing biomass.

Technological TTS v1.0 Annex H ⏳ Class II–III ● Active
Submit Bio-oil Storage Project View TTS v1.0 Annex H →
>500 m
Minimum injection depth
Biogenic
CO₂ source - atmosphere-derived
$70–$180
Current cost per tonne
2
Approved methodologies
BOG-M01 & BOG-M02
Teravent Methodology Codes · TTS Annex H
View TTS Annex H →

How this pathway works

Fast pyrolysis rapidly heats biomass (agricultural residue, forestry residue, or dedicated energy crops meeting the Teravent Sustainable Biomass Criteria) in the absence of oxygen, typically at 450–550°C for under two seconds, decomposing it into three products: bio-char (a solid), bio-oil (a viscous, oxygenated liquid rich in carbon), and a non-condensable syngas often used to power the pyrolysis process itself. Bio-oil is the largest fraction by mass and carries roughly half the original biomass's carbon content in liquid form.

Under the Teravent Technology-Based Carbon Standard (TTS v1.0) Annex H, this pathway injects the bio-oil fraction into deep geological formations - more than 500 metres below surface - for long-term storage, earning Teravent Technology Credits of the Removal type (TTC-R) for verified net tonnes of biogenic carbon durably stored, net of full lifecycle project emissions. Bio-oil's chemical stability and viscosity at storage-site pressure and temperature conditions substantially reduce the buoyant migration risk associated with supercritical CO₂, though its long-term chemical stability over multi-century timescales is less extensively studied than mineral or gaseous storage, placing this pathway at Class II–III depending on demonstrated monitoring confidence.

Two methodology variants are approved under Annex H, differentiated by the storage formation depth and monitoring regime, which together determine whether a project achieves Class II (monitored, 100–1,000 years) or Class III (deep, unmonitored-equivalent confidence, >1,000 years) durability.

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Class II–III, by storage depth and monitoring regime. Credits issued under TTS Annex H carry Class III permanence where deep, well-characterised storage with structural containment equivalent to Annex G standards is demonstrated, or Class II permanence where storage is shallower or monitoring confidence is comparatively lower. Buffer pool rates of 7–25% (Class II) or 2–15% (Class III) apply accordingly.

TTS v1.0 - Annex H

This pathway is governed exclusively by the Teravent Technology-Based Carbon Standard (TTS v1.0). No external registry, standard, or methodology is referenced or incorporated. All requirements - additionality, quantification, durability, safeguards, and credit issuance - are defined within TTS v1.0 and Annex H, with reference to Annex G storage integrity principles for the deepest, best-characterised sites.

Teravent Technology Credit - Serial Number Format (TTS Annex H · Removal)
TCR TTS R BOG CA 00028 2025 000001
Registry TCR
Standard TTS v1.0
Pathway Code BOG
Credit Type TTC-R - Removal Credit
Durability Class II–III · by depth/monitoring

Two approved methodology variants

TTS v1.0 Annex H approves two methodology types for Bio-oil Geological Storage, differentiated by injection depth and the resulting monitoring and durability classification. Both require feedstock to meet the Teravent Sustainable Biomass Criteria before any capture or storage credit can be considered.

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Depth determines durability class: Bio-oil injected below 500 m into a well-characterised formation with confirmed containment can achieve Class III durability equivalent to Annex G geologic storage. Shallower injection, or formations with less-characterised containment, default to Class II, reflecting greater uncertainty in multi-century chemical stability and migration behaviour.
BOG-M01
Deep Formation Bio-oil Injection
Bio-oil injected into a well-characterised deep formation with confirmed caprock containment, achieving Class III durability

Where bio-oil is injected into a formation meeting the same site characterisation standard as Annex G geologic CO₂ storage - confirmed caprock integrity, adequate injection depth, and a monitoring regime equivalent to gaseous CO₂ storage sites - the project can achieve Class III durability. This methodology is most often deployed at repurposed depleted hydrocarbon reservoirs or dedicated saline formations, leveraging existing site characterisation data where available.

Permanence
Class III · Geological
Buffer Pool
2–8% (by SIRR)
Minimum Depth
> 800 m with confirmed caprock
Site Characterisation
Equivalent to Annex G standard
Bio-oil Carbon Content
Assayed per batch, typically 45–55% by mass
Metering Requirement
Injection volume and density, ±2% mass accuracy
Key Monitoring Indicators
  • Bio-oil injection volume and density at wellhead, converted to mass carbon injected at ±2% accuracy
  • Bio-oil carbon content assay per production batch, via elemental analysis
  • Formation pressure and caprock integrity monitoring, consistent with Annex G protocols
  • Feedstock chain-of-custody documentation confirming Sustainable Biomass Criteria compliance
  • Periodic core or fluid sampling to confirm bio-oil chemical stability under formation conditions
BOG-M02
Monitored Shallow Formation Injection
Bio-oil injected into a shallower formation (500–800 m) with an ongoing monitoring commitment, achieving Class II durability

Where full Annex G-equivalent deep site characterisation is not available or the injection formation sits above the 800 m Class III threshold, projects may still register under a monitored storage regime - accepting Class II durability (100–1,000 years) in exchange for a lower site characterisation bar, provided an ongoing monitoring commitment tracks bio-oil location and chemical stability over time. This methodology is well suited to smaller-scale, regional pyrolysis facilities without access to extensively characterised deep formations.

Permanence
Class II · Material (monitored)
Buffer Pool
7–20% (by monitoring confidence)
Injection Depth
500–800 m
Monitoring Commitment
Ongoing periodic monitoring for full credited durability period
Bio-oil Carbon Content
Assayed per batch, typically 45–55% by mass
Metering Requirement
Injection volume and density, ±2% mass accuracy
Key Monitoring Indicators
  • Bio-oil injection volume and density at wellhead, converted to mass carbon injected at ±2% accuracy
  • Bio-oil carbon content assay per production batch
  • Periodic monitoring well sampling to confirm bio-oil has not migrated beyond the injection zone
  • Groundwater quality monitoring at overlying aquifers per DNSH provisions, given shallower injection depth
  • Feedstock chain-of-custody documentation confirming Sustainable Biomass Criteria compliance

Which emission sources must be counted

TTS v1.0 Module 3 requires a full lifecycle GHG emissions inventory within the project boundary, deducted from the gross bio-oil carbon injected to arrive at the Net TTC figure.

Required
Bio-oil Carbon (Gross)
Primary benefit quantity. Injection volume and density metered at the wellhead, converted to mass carbon injected using per-batch elemental analysis of the bio-oil carbon content.
Required
Feedstock Cultivation, Harvest & Transport
Emissions from feedstock cultivation, harvest, processing, and transport to the pyrolysis facility, assessed per the Lifecycle GHG Assessment Protocol (TLP v1.0).
Required
Indirect Land-Use Change (ILUC)
Where feedstock is a dedicated energy crop rather than a residue or waste stream, a modelled ILUC emissions factor must be applied and deducted, as for BECCS (Annex B).
Required
Pyrolysis, Transport & Injection Energy
Electricity and thermal energy consumed by the pyrolysis process (net of any syngas self-generated energy credit), bio-oil transport, and wellhead injection, applying the applicable grid emissions factor per TLP v1.0.
Required where material
Co-Product Allocation
Where bio-char is separately sold or used (e.g. as a soil amendment potentially registered under Biochar, Annex A of THS), emissions and carbon credits must be allocated between the bio-oil injection stream and the bio-char co-product to prevent double counting.
Excluded
Non-Condensable Syngas Combustion
CO₂ from combusting the syngas by-product to power the pyrolysis process is treated as carbon-neutral under standard biogenic accounting where the syngas is not separately credited, and excluded from the core Net TTC calculation.

Measurement, reporting
& verification

Teravent's Science Advisory Board assesses each pathway against four MRV dimensions. Bio-oil injection quantification is very high confidence given straightforward volumetric and compositional metering, but long-term storage monitoring confidence is comparatively lower than gaseous or mineral storage, reflecting the pathway's earlier stage of commercial deployment.

Injection QuantificationVery High
Long-Term Storage MonitoringMedium
Permanence ConfidenceMedium–High
Additionality ClarityHigh
🔬 Measurement Requirements - TTS Module 3

Bio-oil quantity is measured via volumetric and density metering at the injection wellhead, accurate to ±2% mass, with carbon content independently assayed per production batch through elemental (CHNS) analysis. Because bio-oil chemical stability under multi-century subsurface conditions is less extensively studied than mineral carbonation or gaseous CO₂ trapping, this pathway requires ongoing periodic monitoring well sampling to confirm the injected bio-oil has not degraded, migrated, or reacted unexpectedly with formation fluids - the monitoring frequency and duration required scale inversely with the depth and site characterisation quality achieved (BOG-M01 versus BOG-M02).

Demonstrating additionality

TTS v1.0 Module 2 requires all projects to pass a three-test additionality framework, with a Technology Readiness Level (TRL) screen applied ahead of the common practice test. Bio-oil geological storage at commercial scale remains an early-stage technology, so most projects qualify for the streamlined TRL-based screen.

1
TRL-Based Common Practice Screen
Projects deploying bio-oil geological injection at Technology Readiness Level 7 or below automatically satisfy the common practice test - dedicated storage-purpose bio-oil injection remains uncommon outside a small number of pilot and demonstration projects globally. Facilities that repurpose bio-oil already being produced for other commercial uses (fuel blending, chemical feedstock) toward storage instead must additionally demonstrate the storage use is not simply following existing market demand.
2
Regulatory Surplus Test
The pyrolysis and injection activity must not be mandated by any legally binding waste management, biomass utilisation, or carbon capture regulation. Where a jurisdiction mandates agricultural residue processing for other environmental reasons, projects must demonstrate the specific bio-oil storage pathway goes beyond that requirement.
3
Financial Additionality Test
Carbon revenue must be necessary for project viability. Developers must submit a discounted cash flow analysis, net of any government grants or tax incentives (disclosed under Module 8) and net of any bio-char or syngas co-product revenue, demonstrating that pyrolysis, transport, and injection costs exceed available revenue absent carbon credit income.
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Government incentive disclosure: Where a project receives direct government grants, capital cost subsidies, or per-tonne tax credits for the same stored bio-oil carbon, this must be disclosed to the TSA at registration under Module 8. Double-claiming the same carbon benefit under both a government incentive programme and Teravent credits is prohibited.

Leakage types & deductions

TTS v1.0 Module 3 defines three leakage types applicable across all engineered pathways. Bio-oil Geological Storage shares the ILUC and residue-diversion leakage exposure of BECCS, plus an energy-source leakage consideration for the pyrolysis and injection process.

Indirect Land-Use Change Leakage
Displaced Agricultural Production
Where dedicated energy crop cultivation for pyrolysis feedstock displaces food or fibre production, that production may shift elsewhere, potentially releasing standing carbon. A modelled ILUC factor must be deducted for all non-residue feedstocks, as for BECCS.
Modelled per feedstock/region; mandatory for dedicated crops
Residue Diversion Leakage
Alternative Residue Use Displacement
Where agricultural or forestry residue feedstock would otherwise have supported soil carbon (left in field) or been used for another purpose, that counterfactual fate must be documented and deducted where material.
Default: 3–8%, assessed at PDD stage
Energy-Source Leakage
Grid Electricity Displacement
Where pyrolysis, transport, and injection equipment draws electricity from a constrained grid beyond what is self-generated from syngas, its consumption may increase marginal fossil generation elsewhere, requiring the regional marginal emissions factor.
Deduction: applicable regional grid factor, TLP v1.0

Buffer pool & reversal risk

Annex H durability class depends on injection depth and site characterisation quality. BOG-M01 achieves Class III where deep, well-characterised containment is confirmed; BOG-M02 defaults to Class II given shallower injection and a reliance on ongoing monitoring rather than deep structural containment alone.

Methodology Durability Class Buffer Pool Rate Primary Reversal Risks
BOG-M01 Deep Formation Class III 2–8% Caprock breach; wellbore integrity failure; long-term bio-oil chemical stability under formation conditions
BOG-M02 Monitored Shallow Class II 7–20% Shallower injection depth increases migration risk; monitoring lapse; groundwater intrusion
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Reversal notification: Project proponents must notify the TSA within 72 hours of discovering a reversal event - detected bio-oil migration outside the injection zone, wellbore integrity failure, or confirmed groundwater contamination. Buffer pool credits are cancelled proportionally to the verified carbon loss. Operators carry 30-year post-closure monitoring obligations (BOG-M01) or an extended ongoing monitoring commitment for the full credited durability period (BOG-M02).

Key registration criteria

Projects must meet all of the following minimum requirements to qualify for registration under TTS Annex H. Additional methodology-specific requirements are detailed in the Annex H methodology tables for each BOG-M code.

Feedstock sourcing documentation demonstrating full compliance with the Teravent Sustainable Biomass Criteria, including land-use change risk assessment
Bio-oil injection volume and density metering installed at the wellhead, calibrated to ±2% mass accuracy
Per-batch elemental (CHNS) analysis of bio-oil carbon content, conducted by an accredited laboratory
Site characterisation report submitted at registration, specifying injection depth and formation containment characteristics determining Class II or III eligibility
Ten-stage registration process completed, from technology eligibility assessment through validation to ongoing verification, per TTS Module 6
Three-test additionality demonstrated with TRL-based screening applied first; TRL documentation updated at each verification
Indirect land-use change (ILUC) risk score assigned at registration for any non-residue feedstock
Monitoring plan specifying sampling frequency and duration commensurate with the durability class claimed (BOG-M01 or BOG-M02)
Do No Significant Harm review covering groundwater quality, particularly for shallower injection sites (BOG-M02)
Co-product allocation methodology submitted where bio-char is separately sold or credited, to prevent double counting

Sustainable Development
Goal alignment

All Teravent registered Bio-oil Geological Storage projects must complete an SDG impact assessment at registration and at each verification period. Three SDGs are systematically tracked for this pathway. Projects may apply for co-benefit quality labels where independently verified indicators are met.

SDG 13 · Climate Action SDG 15 · Life on Land SDG 9 · Industry, Innovation & Infrastructure
Circular Feedstock+
Projects sourcing exclusively agricultural or forestry residues rather than dedicated energy crops are eligible for the Circular Feedstock label, reflecting the lowest ILUC risk feedstock profile.
Frontier Technology+
TSA TAP-designated first-of-kind bio-oil injection deployments with independently peer-reviewed methodology are eligible for the Frontier Technology label, reflecting this pathway's early commercial stage.
Zero Fossil Input+
Facilities powered entirely by self-generated syngas or verified renewable electricity for pyrolysis, transport, and injection are eligible for the Zero Fossil Input co-benefit label.
Community Benefit+
Projects sourcing residue feedstock from smallholder farmers or forestry cooperatives with verified fair pricing are eligible for the Community Benefit+ label at Premium and Frontier certification tiers.

Deployment scope: Regions with established agricultural or forestry residue supply chains and access to characterised sedimentary basins or depleted hydrocarbon reservoirs - currently most active in North America and Northern Europe.

🛢️ Bio-oil Geological Storage · TTS Annex H

Ready to register your
bio-oil storage project?

Submit a Project Concept Note under TTS v1.0 Annex H to begin your registration. Confirm your feedstock meets the Teravent Sustainable Biomass Criteria, select the BOG-M code matching your injection depth and monitoring regime, and appoint an accredited VVB to validate your PDD.