BOLD Carbon (CH₄) Framework (MvF) v1.0.2
BOLD Carbon (CH₄) framework (MvF) specification version 1.0.2.
Framework summary
| Property | Value |
|---|---|
| Methodology | BOLD Carbon (CH₄) |
| Version | 1.0.2 |
| Status | Published |
| Credit type | Carbon Credit |
| Token | TCC (C-CARB.CH4) — issued by this methodology |
| External reference | UNFCCC AMS-III.F v12.0 |
Scope
The BOLD Carbon (CH₄) MvF defines verification procedures for preventing methane emissions through composting organic waste that would otherwise decompose in landfills:
- Waste types: Food waste, green waste (garden, yard, and park trimmings), sludge from waste treatment plants, tobacco industry residues, and other organic subtypes classified under CDM waste codes
- Treatment: Aerobic composting at professional facilities
- Geography: Currently operational in Brazil, with the framework designed to be expandable to other regions
- Environmental claim: Prevented CO2e emissions from methane avoidance
Eligibility criteria
Participants must meet the same accreditation requirements as BOLD Recycling:
- Waste generators — Must be identified with valid documentation.
- Haulers — Required for truck and boat transport; optional for sludge pipe and cart collection.
- Processors — Exactly one processor must be identified per MassID.
- Recyclers — Exactly one recycler (composting facility) must be identified with valid accreditation dates.
- Network Integrators — Must have valid accreditation dates.
Verification requirements
BOLD Carbon (CH₄) includes all the verification checks present in BOLD Recycling, plus additional checks specific to emission quantification:
- All shared checks — Document validation, actor identification, event validation, geolocation, manifests, compliance, and integrity (see BOLD Recycling Framework)
- Emissions calculation — The
prevented-emissionsrule quantifies CO2e prevented using the UNFCCC AMS-III.F methodology - Project boundary — The
project-boundaryrule validates the geographic distance between pick-up and drop-off locations
Baseline scenario and emission factors
BOLD Carbon (CH₄) references the UNFCCC AMS-III.F v12.0 methodology for emission calculations:
- Baseline scenario — Organic waste decomposing anaerobically in a landfill, generating methane (CH4)
- Project scenario — The same organic waste composted aerobically, preventing methane generation
- Emission factors — Static factors are used for most organic waste subtypes. For waste classified under CDM code 8.7D ("Others, if organic"), dynamic factors are applied based on Ibama waste classification codes.
The prevented-emissions rule applies the formula: prevented CO2e equals the mass of composted waste multiplied by the prevented emissions factor per ton, minus the mass multiplied by the exceeding emission coefficient.
Scientific basis
The following standards provide the scientific foundation for emission calculations and waste classification in BOLD Carbon (CH₄):
UNFCCC Clean Development Mechanism
| Reference | Version | Description |
|---|---|---|
| AMS-III.F | v12.0 | "Avoidance of methane emissions through composting" — the basis for the prevented-emissions rule. Defines emission factors and calculation procedures for quantifying prevented CH₄ from composting organic waste. |
| CDM Tool 04 | v8.0 | "Emissions from solid waste disposal sites" — provides methodologies for estimating methane emissions from landfill disposal, used as the baseline scenario in emission avoidance calculations. |
| CDM Tool 13 | v2.0 | "Project and leakage emissions from composting" — defines procedures for estimating project emissions and leakage from composting activities. |
IPCC
| Reference | Year | Description |
|---|---|---|
| IPCC AR5 | 2013 | Fifth Assessment Report — provides Global Warming Potential (GWP) values used in emission calculations. The GWP for methane (CH₄) is used to convert prevented methane emissions to CO₂e. |
Regional standards
| Reference | Jurisdiction | Description |
|---|---|---|
| Ibama Brazilian List of Solid Waste | Brazil | Official waste classification system used by the regional-waste-classification rule. Maps waste types to CDM waste codes for emission factor selection. |
Emission calculation parameters
Baseline emissions — CDM Tool 04 v8.0
For calculating methane emissions from landfills and dump sites, BOLD Carbon (CH₄) uses UNFCCC CDM Tool 04 v8.0 — "Emissions from Solid Waste Disposal Sites."
| Parameter | Value | Description |
|---|---|---|
| φ | 0.85 | Model correction factor for model uncertainties |
| f | 0.00 (scenarios 1, 3) / 0.45 (scenario 2) | Fraction of methane captured and flared |
| GWP_CH₄ | 28 | Global Warming Potential of methane (IPCC AR5, 2013) |
| OX | 0.1 | Oxidation factor (methane oxidized in soil covering) |
| F | 0.5 | Fraction of methane in landfill gas (volume) |
| DOC_f | 0.5 | Fraction of degradable organic carbon that decomposes |
| MCF | 1.0 (scenarios 1, 2) / 0.8 (scenario 3) | Methane correction factor |
| DOC_j (food) | 0.15 | Degradable organic carbon fraction — food waste |
| DOC_j (green) | 0.20 | Degradable organic carbon fraction — green waste |
| K_j (food) | 0.40 | Decay rate — food waste (1/yr, wet tropical climate) |
| K_j (green) | 0.17 | Decay rate — green waste (1/yr, wet tropical climate) |
Three baseline scenarios are supported:
- Landfill without methane flaring — Highest emissions (f = 0)
- Landfill with methane flaring — Moderate emissions (f = 0.45, ~50% capture at 90% burn efficiency)
- Dump site — Intermediate emissions (MCF = 0.8)
Real emissions — CDM Tool 13 v2.0
For calculating emissions during composting, BOLD Carbon (CH₄) uses UNFCCC CDM Tool 13 v2.0 — "Project and Leakage Emissions from Composting."
| Parameter | Value | Description |
|---|---|---|
| EF_CH₄ | 2.0 g/kg waste | Methane emission factor per kg composted |
| EF_N₂O | 0.2 g/kg waste | Nitrous oxide emission factor per kg composted |
| GWP_CH₄ | 28 | Global Warming Potential of methane (IPCC AR5, 2013) |
| GWP_N₂O | 265 | Global Warming Potential of nitrous oxide (IPCC AR5, 2013) |
Default emission factors are for "Fresh Weight" (gross weight including water content). Additional factors for fossil fuel and electricity consumption apply but are not shown in the simplified formula.
Calculation example
For a composting facility using a 50/50 food waste to green waste ratio, comparing composting to landfill without methane capture:
| Metric | Value |
|---|---|
| Baseline Emissions (BE) | 2.451 tons CO₂e |
| Real Emissions from composting (RE) | 0.218 tons CO₂e |
| Avoided Emissions (AE) | 2.233 tons CO₂e |
This means composting 1 ton of food waste + 1 ton of green waste avoids approximately 2.2 tons of CO₂e over a 20-year period compared to landfill disposal.
Comparison across disposal methods
| Disposal method | Total 20-year emissions | Avoided vs. composting |
|---|---|---|
| Landfill without flaring | 2.451 tons CO₂e | 2.233 tons CO₂e |
| Dump site | 1.961 tons CO₂e | 1.743 tons CO₂e |
| Landfill with flaring | 1.348 tons CO₂e | 1.130 tons CO₂e |
| Composting | 0.218 tons CO₂e | — |
In every scenario, composting 1 ton of organic waste avoids more than 1 ton of CO₂e emissions.
Supported waste codes
BOLD Carbon validates waste materials against the Brazilian List of Solid Waste published by Ibama (IN nº 13, December 18, 2012) and maps each Ibama code to a CDM waste category from CDM Tool 04 v08.1. This mapping is enforced at submission time by the regional-waste-classification rule — see the Rules catalog and the Waste Classification reference for additional context.
CDM waste categories
The methodology supports 216 Ibama codes across the following CDM categories:
| CDM Code | Category | Supported codes |
|---|---|---|
| 8.1 | Wood and wood products | 8 |
| 8.2 | Pulp, paper and cardboard (other than sludge) | 8 |
| 8.3 | Food, food waste, beverages and tobacco (other than sludge) | 12 |
| 8.4 | Textiles | 5 |
| 8.5 | Garden, yard and park waste | 1 |
| 8.6 | Glass, plastic, metal, other inert waste | 47 |
| 8.7B | Industrial Sludge | 14 |
| 8.7C | Domestic Sludge | 26 |
| 8.7D | Others (if organic) | 95 |
Ibama code reference
Expand each category below to see the accepted Ibama codes. The Ibama Code is the value to send as LOCAL_WASTE_CLASSIFICATION_ID; the Description is validated against LOCAL_WASTE_CLASSIFICATION_DESCRIPTION.
For codes under CDM 8.7D where % Carbon is not listed, the recycler must specify the waste type and/or provide a laboratory report. The carbon fraction is used by the prevented-emissions rule (rule 21) to calculate dynamic emission factors — see Baseline scenario and emission factors.
Key parameters
| Parameter | Value |
|---|---|
| Composting cycle timeframe | Validated between DROP_OFF and RECYCLED events |
| Geolocation tolerance | Participant addresses validated against accredited addresses |
| Project boundary | Distance between first PICK_UP and last DROP_OFF validated |
| Document unit | Kilograms (kg) |
| Document type | Organic |
| Project period | RECYCLED event must occur on or after January 1st of the previous year |
Validation rules
See the BOLD Carbon (CH₄) Rules catalog for the complete list of validation rules, grouped by category with descriptions.
Downloads
Feedback: method@carrot.eco
BOLD Carbon (CH₄) Overview
BOLD Carbon (CH₄) methodology — certification of prevented methane emissions from organic waste composting.
BOLD Carbon (CH₄) Framework Rules v1.0.2
Complete catalog of specification-level framework rules for BOLD Carbon (CH₄) v1.0.2 — what must be verified for each MassID document.