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23 Hybrid Carbon Pathway · THS Annex C
🌳

Agroforestry
with Biochar
THS v1.0 - Annex C

Agroforestry with Biochar integrates trees and crops in a designed multi-layer farming system, then closes the loop by converting woody pruning residues and other on-farm biomass into biochar through pyrolysis, which is returned to the soil as a durable carbon amendment. The result is a system that simultaneously builds living tree biomass carbon, improves soil fertility and water retention through biochar's porous structure, and locks a portion of the system's own carbon into a centuries-stable form - all within one integrated, working farm.

🌱 Nature: Trees & crops in integrated systems ⚙️ Tech: Biochar soil amendment
Hybrid Pathway THS v1.0 Annex C ⏳ Class I–II ● Active
Submit Agroforestry-Biochar Project View THS v1.0 Annex C →
100–1,000 yr
Biochar storage timescale (Class II)
10–100 yr
Tree biomass timescale (Class I)
$60–$180
Current cost per tonne
2
Approved methodologies
AFB-M01 & AFB-M02
Teravent Methodology Codes · THS Annex C
View THS Annex C →

How this pathway works

Agroforestry systems - alley cropping, silvopasture, and other designs that deliberately integrate trees with crops or livestock on the same land - already sequester carbon in growing tree biomass while delivering shade, windbreak, and soil-structure benefits to the associated agricultural system. This pathway adds a second carbon mechanism: woody biomass generated by routine tree pruning, thinning, or end-of-rotation harvest is converted to biochar through pyrolysis, then returned to the soil within the same agroforestry system, both amending the soil and permanently locking a portion of the biomass carbon into a highly stable, aromatic carbon structure resistant to microbial decomposition.

Under the Teravent Hybrid Carbon Standard (THS v1.0) Annex C, this pathway is classified as hybrid because it requires integrated monitoring of both the biological tree-and-crop system and the biochar production-and-application technology component operating within it - tree growth, pruning yield, biochar stability, and soil incorporation must all be jointly assessed under a single project boundary. Teravent Hybrid Credits (THC) are issued for verified net tonnes of CO₂ sequestered across both components, net of full lifecycle project emissions.

Two methodology variants are approved under Annex C, differentiated by the specific agroforestry system design - alley cropping and silvopasture - each with distinct pruning biomass availability and application logistics.

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Class I–II - a disaggregated dual-durability credit. Credits issued under THS Annex C are disaggregated by durability class in the issuance record: the living tree biomass carbon fraction carries Class I permanence (10–100 years, buffer 20–40%), while the biochar soil carbon fraction carries Class II permanence (100–1,000 years, buffer 7–25%), reflecting the substantially greater microbial resistance of pyrolysed carbon relative to living or decomposing biomass.

THS v1.0 - Annex C

This pathway is governed exclusively by the Teravent Hybrid Carbon Standard (THS v1.0), the companion standard to TNS v1.0 (Nature) and TTS v1.0 (Technology) purpose-built for systems where biological and engineered carbon mechanisms are integrated and jointly monitored. No external registry, standard, or methodology is referenced or incorporated.

Teravent Hybrid Credit - Serial Number Format (THS Annex C · Biochar fraction shown, Class II)
TCR THS AFB KE 00058 2025 II 000001
Registry TCR
Standard THS v1.0
Pathway Code AFB
Credit Type THC - Teravent Hybrid Credit
Durability Class I (tree biomass) + Class II (biochar), disaggregated
💡
Two durability classes, one project: A single Agroforestry with Biochar project issues credits under both Class I (the living tree biomass component, subject to standard biological reversal risk from fire, disease, or harvest) and Class II (the biochar component, verified through the H/Corg atomic ratio stability protocol). These are tracked and issued as separate serials within the same project registration, not blended into a single averaged durability figure.

Two approved methodology variants

THS v1.0 Annex C approves two discrete methodology types, differentiated by the specific agroforestry system design and its associated biochar feedstock and application logistics.

AFB-M01
Biochar-Amended Alley Cropping
Tree rows interspersed with annual crop alleys, with biochar produced from tree pruning residue applied to the cropped alleys

Alley cropping plants rows of trees - often nitrogen-fixing species or fruit/timber trees - with wide alleys of annual crops cultivated between them. Routine pruning to manage tree canopy shading and shape provides a steady, predictable biomass feedstock stream, which is converted to biochar via a farm-scale or centralised pyrolysis unit and then incorporated into the cropped alley soil, improving water retention and nutrient cycling for the annual crop while sequestering the pyrolysed carbon fraction long-term.

Durability
Class I (tree biomass) + Class II (biochar)
Buffer Pool
20–35% (Class I) / 7–20% (Class II)
Biochar Stability Test
H/Corg atomic ratio ≤ 0.4 required
Tree Biomass Monitoring
Allometric growth measurement, remote sensing
Application Metering
Biochar mass applied per hectare, ±5%
Feedstock Source
On-farm tree pruning and thinning residue only
Key Monitoring Indicators
  • Tree biomass growth tracked via periodic allometric measurement and, where feasible, satellite or drone-based remote sensing
  • Pruning biomass yield per harvest event, logged as biochar feedstock input
  • Biochar H/Corg atomic ratio tested per pyrolysis batch to confirm stability threshold (≤0.4) required for Class II crediting
  • Biochar application rate per hectare, metered at ±5% accuracy, and soil incorporation method documented
  • Crop yield in the cropped alleys tracked as an agronomic co-benefit indicator
AFB-M02
Biochar-Enhanced Silvopasture
Trees integrated with grazing livestock systems, with biochar produced from tree biomass applied to pasture soil

Silvopasture integrates trees into livestock grazing systems, providing shade and forage diversity for animals while building tree biomass carbon on land that would otherwise be open pasture. This methodology adds biochar production from tree pruning and thinning residue, applied to pasture soil to improve forage productivity and water retention, while also providing an additional durable carbon sink complementing the biological tree and soil carbon components already present in well-managed silvopasture systems.

Durability
Class I (tree biomass) + Class II (biochar)
Buffer Pool
20–40% (Class I) / 7–22% (Class II)
Biochar Stability Test
H/Corg atomic ratio ≤ 0.4 required
Livestock Integration
Grazing management plan documented to avoid tree/soil damage
Application Metering
Biochar mass applied per hectare, ±5%
Feedstock Source
On-farm tree pruning and thinning residue only
Key Monitoring Indicators
  • Tree biomass growth tracked via periodic allometric measurement and remote sensing where feasible
  • Grazing intensity and rotation schedule documented to confirm compatibility with tree health and soil biochar retention
  • Biochar H/Corg atomic ratio tested per pyrolysis batch to confirm stability threshold required for Class II crediting
  • Biochar application rate per hectare, metered at ±5% accuracy
  • Forage productivity and pasture soil health tracked as agronomic co-benefit indicators

Which emission sources must be counted

THS v1.0 Module 3 requires a dual-component accounting boundary spanning both the biological tree/crop or tree/livestock system and the biochar production technology component, with a full lifecycle GHG emissions inventory deducted from gross sequestration to arrive at the Net THC figure for each durability class.

Required
Tree Biomass Carbon (Class I)
Above- and below-ground living tree biomass carbon accumulation, tracked via allometric measurement and remote sensing, net of any biomass removed for pruning or harvest.
Required
Biochar Soil Carbon (Class II)
Stable pyrolysed carbon applied to soil, quantified from pruning biomass input mass, pyrolysis yield, and confirmed via H/Corg atomic ratio stability testing on representative production batches.
Required
Pyrolysis Process Emissions
Non-condensable syngas combustion and any fossil auxiliary fuel used to power the pyrolysis unit, applying the applicable emissions factor per THS Module 3.
Required where material
Biomass Transport & Biochar Application Energy
Fuel or electricity consumed moving pruning biomass to the pyrolysis unit and spreading finished biochar across the field, where this occurs beyond routine farm operations.
Excluded
Baseline Farm Operations
Emissions from the underlying crop production or livestock grazing operations that would occur regardless of the agroforestry-biochar project are excluded from this pathway's boundary.

Measurement, reporting
& verification

Teravent's Science Advisory Board assesses each pathway against four MRV dimensions. The biochar component of this pathway carries very high measurement confidence given direct laboratory confirmation of stability; the tree biomass component carries the somewhat lower confidence typical of biological carbon pools subject to growth rate and disturbance uncertainty.

Biochar Stability ConfirmationVery High
Tree Biomass QuantificationHigh
Permanence ConfidenceHigh (Class II) / Medium (Class I)
Additionality ClarityHigh
🔬 Measurement Requirements - THS Module 3

The biochar component is verified through the THS H/Corg atomic ratio stability protocol - a laboratory test of the hydrogen-to-organic-carbon ratio of representative biochar samples, with a ratio of 0.4 or below required to qualify for Class II durability crediting (lower ratios indicate greater aromatic carbon stability and microbial resistance). Biochar application rates are metered at ±5% mass accuracy per hectare. The tree biomass component is tracked through periodic allometric growth measurement at representative sample plots, cross-validated against satellite or drone-based remote sensing where available, following standard biological carbon MRV practice shared with TNS v1.0 forestry pathways. Pruning biomass yield feeding the pyrolysis process is logged at each harvest event.

Demonstrating additionality

THS v1.0 Module 2 requires a three-layer baseline: a biological baseline (the farm's tree cover and management practice absent the project), a technology baseline (common practice for biochar production and application), and a combined system net baseline reconciling the two.

1
Common Practice Test
Deliberate biochar production from agroforestry pruning residue, applied specifically for carbon sequestration purposes, remains uncommon in most regions, distinct from simple residue burning or open composting. Projects must document that both the tree integration and the biochar production-and-application programme exceed regional common practice.
2
Regulatory Surplus Test
The agroforestry establishment and biochar production activity must not be mandated by any legally binding land management, agroforestry, or waste management regulation. Where a jurisdiction requires tree cover for erosion control or similar purposes, projects must demonstrate the specific agroforestry design and biochar programme exceed that baseline 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 agroforestry or afforestation grants (disclosed under Module 8) and net of any timber, fruit, or forage productivity benefit, demonstrating that tree establishment, pyrolysis unit capital cost, and biochar application costs exceed available revenue absent carbon credit income.
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Government incentive disclosure: Where a project receives direct government agroforestry grants, afforestation incentive payments, or per-tonne carbon removal tax credits, 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

THS v1.0 Module 3 defines three leakage types applicable across all hybrid pathways. Agroforestry with Biochar shares the general biological displacement risks of tree-planting pathways alongside a feedstock-related consideration specific to biochar production.

Agricultural Production Displacement Leakage
Reduced Cropland or Pasture Area
Where converting land to alley cropping or silvopasture reduces the area available for annual cropping or open grazing, displaced production may shift to new land elsewhere. A market displacement assessment is required where a material reduction in cropped or grazing area is documented.
Default: 3–8%, assessed at PDD stage
Residue Diversion Leakage
Alternative Pruning Residue Use
Where pruning residue would otherwise have been used for firewood, animal bedding, or left as mulch supporting soil carbon, that counterfactual fate must be documented and deducted where material.
Default: 3–6%, assessed at PDD stage
Energy-Source Leakage
Pyrolysis Unit Fuel Use
Where the pyrolysis unit requires auxiliary fossil fuel beyond self-generated syngas, associated combustion emissions must apply the applicable emissions factor absent verified low-carbon alternatives.
Deduction: applicable emissions factor, TLP v1.0

Buffer pool & NPRR assessment

Annex C credits are issued across two distinct durability classes, each with its own buffer pool rate reflecting different reversal risk profiles - the living tree biomass fraction is subject to biological disturbance risk (fire, disease, harvest), while the biochar fraction, once confirmed stable via laboratory testing, carries substantially lower reversal risk.

Component Durability Class Buffer Pool Rate Primary Reversal Risks
AFB-M01 / M02 Tree Biomass Class I 20–40% Fire, disease, pest outbreak, premature harvest, land-use reversion
AFB-M01 Biochar (Alley Cropping) Class II 7–20% Soil erosion at application site; incomplete pyrolysis reducing stability
AFB-M02 Biochar (Silvopasture) Class II 7–22% Livestock trampling disturbing applied biochar; soil erosion on grazed slopes
⚠️
Reversal notification: For the tree biomass component (Class I), proponents must notify the TSA within 30 days of a confirmed reversal event - fire, pest outbreak, disease, or unauthorised harvest exceeding the documented management plan. For the biochar component (Class II), notification is required within 72 hours of confirmed physical loss (e.g. severe erosion) at the application site; ordinary microbial decomposition is already accounted for through the H/Corg stability threshold and does not constitute a reversal event on its own.

Key registration criteria

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

Agroforestry system design plan documented, specifying tree species, spacing, and integration approach (alley cropping or silvopasture)
Tree biomass baseline and growth monitoring plan established, using allometric measurement at representative sample plots
Biochar production facility with H/Corg atomic ratio testing capability, confirming a ratio of 0.4 or below for Class II crediting eligibility
Biochar application rate metered at ±5% mass accuracy per hectare, with soil incorporation method documented
Ten-stage registration process completed, from hybrid eligibility assessment through validation to ongoing verification, per THS Module 6
Seventeen-element Project Design Document submitted, including a three-layer baseline analysis and dual-durability crediting plan
Three-test additionality demonstrated for both the agroforestry establishment and the biochar production programme
Feedstock sourcing confirmed as on-farm pruning and thinning residue only, with documented counterfactual fate analysis
Do No Significant Harm review covering soil health, biodiversity, water resources, food security, and pyrolysis emissions per Module 5
Farmer or land manager consent and benefit-sharing agreement documented where the registering entity differs from the land occupier

Sustainable Development
Goal alignment

All Teravent registered Agroforestry with Biochar projects must complete an SDG impact assessment at registration and at each verification period. Four SDGs are systematically tracked for this pathway, reflecting its combined agricultural, forestry, and climate dimensions. Projects may apply for any of the eight THS co-benefit quality labels where independently verified indicators are met.

SDG 15 · Life on Land SDG 2 · Zero Hunger SDG 13 · Climate Action SDG 1 · No Poverty
Soil Health+
Projects with verified soil water retention and fertility improvement, documented through registered soil testing, are eligible for the Soil Health+ label.
Smallholder Inclusion+
Projects aggregating smallholder farms with fair benefit-sharing agreements and technical support for agroforestry establishment and biochar production are eligible for this co-benefit label.
Indigenous Stewardship
Projects led by or developed in genuine partnership with Indigenous communities, with FPIC documented and benefit-sharing agreements verified, are eligible for the Indigenous Stewardship label.
Biodiversity Corridor+
Projects that integrate native tree species and demonstrate measurable habitat connectivity benefits for local wildlife are eligible for the Biodiversity Corridor co-benefit label.

Deployment scope: Global, with particularly strong applicability in smallholder farming regions of Sub-Saharan Africa, South and Southeast Asia, and Latin America, where agroforestry systems are already widely practiced and pruning biomass availability is high.

🌳 Agroforestry with Biochar · THS Annex C

Ready to register your
agroforestry-biochar project?

Submit a Project Concept Note under THS v1.0 Annex C to begin your registration. Select the AFB-M code matching your system design, establish tree biomass and biochar monitoring, confirm biochar stability via H/Corg testing, and appoint an accredited VVB to validate your PDD and three-layer baseline analysis.