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33 Hybrid Carbon Pathway · THS Annex N
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Constructed Soil
Carbon Systems
THS v1.0 - Annex N

Constructed Soil Carbon Systems engineers designed soil substrates - precisely blended combinations of mineral aggregates, organic amendments, biochar, and structural materials - on land where natural soil is absent, severely degraded, or being purpose-built, such as reclaimed mine sites, brownfield redevelopment, or engineered green infrastructure. Rather than working with an existing soil and amending it, this pathway builds a soil system from its constituent components specifically designed to maximise long-term carbon retention alongside its primary function (vegetation support, stormwater management, or land reclamation).

🌱 Nature: Engineered soil sequestration ⚙️ Tech: Designed soil substrates & amendments
Hybrid Pathway THS v1.0 Annex N ⏳ Class I–II ● Active
Submit Constructed Soil Project View THS v1.0 Annex N →
10–1,000 yr
Storage timescale (Class I–II)
Engineered
Purpose-designed substrate composition
$35–$110
Current cost per tonne
2
Approved methodologies
CSC-M01 & CSC-M02
Teravent Methodology Codes · THS Annex N
View THS Annex N →

How this pathway works

Some land has no functioning soil to amend - former mine sites stripped of topsoil, industrial brownfield redevelopment, or newly constructed green infrastructure like engineered rain gardens or green roofs - requiring an entirely built soil profile rather than the amendment of an existing one. Constructed Soil Carbon Systems designs this substrate deliberately, blending mineral components (for structure and drainage), biochar (for long-term carbon stability and water retention), and organic matter (for nutrient cycling and initial vegetation establishment) in specified ratios validated to maximise carbon retention over the system's design life.

Under the Teravent Hybrid Carbon Standard (THS v1.0) Annex N, this pathway is classified as hybrid because the carbon benefit results directly from the engineered substrate design - unlike passive soil restoration, the composition and structure of the constructed soil is a deliberate technology intervention distinct from allowing natural soil formation processes to occur. Teravent Hybrid Credits (THC) are issued for verified net tonnes of CO₂-equivalent sequestered in the constructed soil profile, net of full lifecycle project emissions.

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Class I–II, by substrate composition. Constructed soils with a substantial biochar or stable mineral-carbon fraction can achieve Class II permanence (100–1,000 years, buffer 7–25%); those relying primarily on organic matter accumulation default to Class I (10–100 years, buffer 20–40%).

THS v1.0 - Annex N

This pathway is governed exclusively by the Teravent Hybrid Carbon Standard (THS v1.0). No external registry, standard, or methodology is referenced or incorporated.

Teravent Hybrid Credit - Serial Number Format (THS Annex N · Class II, biochar-based substrate)
TCR THS CSC US 00143 2025 II 000001
Registry TCR
Standard THS v1.0
Pathway Code CSC
Credit Type THC - Teravent Hybrid Credit
Durability Class I–II · by substrate composition

Two approved methodology variants

THS v1.0 Annex N approves two methodology types, differentiated by site context and substrate design.

CSC-M01
Reclaimed Land Constructed Soils
Engineered soil substrates built on former mine sites, quarries, or severely degraded land lacking functional topsoil

Former mine sites, quarries, and other severely degraded land often lack any functional topsoil after extraction activity strips or destroys the original soil profile. This methodology builds a complete replacement soil system - blending overburden material, mineral amendments, biochar, and compost or other organic matter in carefully validated ratios - designed both to support vegetation re-establishment and to maximise long-term carbon retention within the reconstructed profile.

Durability
Class II (biochar-substantial); Class I (organic-dominant)
Buffer Pool
7–25% (Class II) / 20–40% (Class I)
Substrate Design
Validated blend ratio submitted at registration
Contamination Screening
Site remediation status confirmed prior to construction
Vegetation Establishment
Tracked as co-benefit and stability indicator
Soil Sampling
Periodic core sampling confirming composition stability
Key Monitoring Indicators
  • Substrate composition documented at construction - mineral, biochar, and organic matter ratios
  • Periodic soil core sampling confirming carbon pool stability and composition over time
  • Contaminated site screening and remediation documentation prior to construction
  • Vegetation establishment and cover monitoring as a co-benefit and erosion-stability indicator
CSC-M02
Engineered Urban Green Infrastructure Soils
Designed soil substrates for engineered rain gardens, bioswales, green roofs, and structural tree cells

Urban green infrastructure - rain gardens, bioswales, structural soil cells supporting street trees, and green roof substrates - requires precisely engineered soil media to meet drainage, load-bearing, and vegetation support specifications simultaneously. This methodology credits the carbon retention benefit of substrate designs that incorporate biochar or other stable carbon amendments into these already-required engineered soil systems, capturing additional climate value from infrastructure being built regardless for stormwater or urban greening purposes.

Durability
Class II (biochar-substantial); Class I (organic-dominant)
Buffer Pool
10–25% (Class II) / 20–35% (Class I)
Substrate Design
Validated blend ratio meeting engineering + carbon specifications
Infrastructure Type
Rain garden, bioswale, structural soil cell, or green roof
Co-Benefit
Stormwater management, urban heat mitigation
Soil Sampling
Periodic sampling given constrained urban access
Key Monitoring Indicators
  • Substrate composition documented at installation, meeting both engineering and carbon retention specifications
  • Periodic soil sampling at accessible representative locations confirming composition stability
  • Stormwater management or urban heat mitigation performance tracked as co-benefit indicators
  • Infrastructure maintenance records confirming the substrate has not been disturbed or replaced

Which emission sources must be counted

Required
Constructed Substrate Carbon (Gross)
Primary benefit quantity, based on validated substrate composition (mineral, biochar, organic matter ratios) and confirmed via periodic soil sampling.
Required
Substrate Component Production & Transport
Emissions from producing and transporting mineral amendments, biochar, and organic matter components to the construction site.
Required
Construction Equipment Energy
Fuel or electricity consumed by earthmoving, blending, and placement equipment during substrate construction.
Required where material
Site Remediation
Where contaminated site remediation is required prior to substrate construction, associated emissions must be assessed if material.
Excluded
Original Site Disturbance Emissions
Historic emissions from the mining, quarrying, or development activity that originally degraded the site are excluded - the baseline is the current degraded state, not the pre-disturbance condition.

Measurement, reporting
& verification

Substrate Composition VerificationVery High
Long-Term Stability ConfirmationMedium–High
Permanence ConfidenceMedium–High
Additionality ClarityHigh
🔬 Measurement Requirements - THS Module 3

Substrate composition - the mineral, biochar, and organic matter ratio - is precisely documented at construction, since this is a designed rather than naturally occurring soil system, giving very high initial confidence. Long-term stability is confirmed through periodic soil core sampling at representative locations, verifying the carbon pool has not degraded or eroded. Where biochar forms a substantial fraction of the substrate, the standard H/Corg stability protocol is applied to confirm Class II eligibility.

Demonstrating additionality

1
Common Practice Test
Deliberate carbon-optimised substrate design, incorporating biochar or other stable carbon amendments beyond standard reclamation practice, must exceed regional common practice.
2
Regulatory Surplus Test
Where site reclamation or green infrastructure construction is already mandated (e.g. mine closure bonds, stormwater regulations), projects must demonstrate the carbon-optimised substrate design exceeds the regulatory minimum specification.
3
Financial Additionality Test
Carbon revenue must be necessary for the incremental cost of the carbon-optimised substrate design relative to a standard reclamation or infrastructure specification, net of government reclamation or green infrastructure grants disclosed under Module 8.
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Government incentive disclosure: Direct government reclamation, brownfield redevelopment, or green infrastructure incentive payments must be disclosed to the TSA at registration under Module 8.

Leakage types & deductions

Amendment Source Leakage
Biochar/Mineral Sourcing Emissions
Where amendment components are sourced from elsewhere, embodied production and transport emissions are included in the required boundary rather than treated as separate leakage.
Included as required boundary item
Energy-Source Leakage
Construction Equipment Fuel
Earthmoving and blending equipment fuel use requires the applicable emissions factor.
Deduction: applicable emissions factor, TLP v1.0
Site Displacement Leakage
Alternative Land Use Displacement
Where the reclaimed or green infrastructure site displaces an alternative planned land use, this must be documented where material.
Default: 2–5%, assessed where material

Buffer pool & NPRR assessment

MethodologyDurability ClassBuffer Pool RatePrimary Reversal Risks
CSC-M01 Reclaimed LandClass I–II (by composition)7–40%Erosion; substrate disturbance during further site development
CSC-M02 Urban Green InfrastructureClass I–II (by composition)10–35%Infrastructure replacement or excavation ahead of design life
⚠️
Reversal notification: Proponents must notify the TSA within 30 days of a confirmed reversal - substrate disturbance, erosion, or infrastructure replacement ahead of the documented design life.

Key registration criteria

Validated substrate composition design submitted at registration, specifying mineral, biochar, and organic matter ratios
Baseline and periodic soil core sampling programme established with an accredited laboratory
Ten-stage registration process completed per THS Module 6
Three-layer baseline analysis submitted in the PDD
NPRR assessed by an accredited VVB; buffer pool applied by durability class
Do No Significant Harm review covering contaminated site management (CSC-M01) and worker safety
Site remediation status documentation submitted where applicable

Sustainable Development
Goal alignment

SDG 11 · Sustainable Cities & CommunitiesSDG 15 · Life on LandSDG 13 · Climate Action
Soil Health+
Verified vegetation establishment and water retention improvement is eligible for this label.
Community Benefit+
Brownfield redevelopment projects delivering local land revitalisation benefits are eligible for this label.

Deployment scope: Global - regions with legacy mining and industrial land requiring reclamation, and cities investing in engineered green infrastructure for stormwater management and urban greening.

🧪 Constructed Soil Carbon Systems · THS Annex N

Ready to register your
constructed soil project?

Submit a Project Concept Note under THS v1.0 Annex N to begin your registration. Select the CSC-M code matching your site context, validate your substrate design, and appoint an accredited VVB to validate your PDD.