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v2.0Last reviewed June 2026
Authored by Jeremiah Say

Lead Systems Architect at GreenCalculus. Translates GHG Protocol methodology into high-precision JavaScript calculation engines. Architect of the MasterBrain data layer covering 1,000+ environmental tools, aligned with IPCC AR6 and the GHG Protocol Corporate Standard (2026 revision).

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Scope 2 Market-Based Method: GHG Protocol Methodology, Instrument Equivalence, and the Four-Tier Supplier Hierarchy

Methodology hero for Scope 2 market-based: activity data (kWh + EAC inventory) × supplier tier (Tier 1 matched at 0.043 or Tier 3 residual at 0.488 kg CO₂e/kWh) = market-based CO₂e. Decomposition shows a 2.5M kWh example with 80% matched Tier 1 yielding 330 tCO₂e versus 517.6 tCO₂e under location-based. Provenance lineage: GHG Protocol Scope 2, AIB residual mix, EPA Green-e via the GreenCalculus MasterBrain factor library.
MB v2026.20 · updated 28 Jun 2026

Citation-grade reference for the GHG Protocol Scope 2 market-based method as defined in the Scope 2 Guidance (2015) and as it interacts with CSRD ESRS E1 mandatory disclosure (2023), the SBTi Corporate Net-Zero Standard additionality posture (2024), and the 2026 GHG Protocol Corporate Standard revision currently in consultation. Defines the instrument equivalence problem, the canonical four-tier supplier hierarchy, the double-claiming taxonomy with six numbered failure modes, the EAC market maturity matrix across thirteen jurisdictions, the additionality debate as three named positions, and the methodology version history as a standards-document log. Three audit-record worked examples — single-site Tier 1 supplier disclosure, multi-site mixed-tier portfolio, sold-EAC double-claim failure — verify arithmetic against the Scope 2 Electricity Calculator. Aligned to GHG Protocol Corporate Standard and Scope 2 Guidance (2015 amendment).

This page is the deep treatment of the market-based method specifically. The Scope 2 Electricity methodology covers the complete inventory workflow including grid factor lookup, multi-site aggregation, and the Scope 3 Cat 3 T&D companion; this page covers the contractual claim architecture, the supplier hierarchy that governs which factor applies to which kWh, the instrument equivalence problem at the heart of every audit dispute, and the version history that determines whether historical inventories require methodology restatement. For the head-to-head method comparison see Scope 2 location-based vs market-based; for the operational calculator see the Scope 2 Electricity Calculator.

The Instrument Equivalence Problem

Named concept · Citable definition

The instrument equivalence problem

The arithmetic of the GHG Protocol market-based method treats every retired energy attribute certificate as numerically equivalent on the unit-of-MWh basis, so a bundled REGO retirement, a bundled GO retirement, an I-REC retirement, and a contracted PPA volume each produce the same MB inventory contribution per kWh covered — but the four are not the same disclosure under CSRD ESRS E1 transition-plan narrative, are not the same evidence under SBTi Corporate Net-Zero Standard target validation review, and are not the same instrument under emerging additionality scrutiny.

⚐ The central editorial tension this page resolves

A market-based zero achieved through 1,000 MWh of bundled REGOs purchased on the secondary market and a market-based zero achieved through 1,000 MWh of contracted output from a new-build solar PPA produce identical MB inventory totals: 1,000,000 × 0.0 = 0 kgCO₂e in both cases. The disclosures, however, are not equivalent. The first carries no additionality credit under SBTi target review, requires a defensive transition-plan narrative under ESRS E1, and is increasingly pre-flagged by reasonable-assurance auditors as a low-quality MB claim. The second carries full SBTi credit, anchors a credible ESRS E1 transition plan, and is the audit-grade benchmark. The arithmetic equivalence is real; the disclosure equivalence is fictional. The instrument equivalence problem is the structural reason a Scope 2 MB total cannot be read in isolation — it must be read together with the instrument basis, the additionality posture, the residual mix treatment for any unmatched portion, and the framework against which the disclosure is filed. Every section of this page exists to give reporters and auditors the apparatus to read the MB total in the round.

What Market-Based Actually Means: The Contractual Claim Architecture

The market-based method is routinely glossed as “buying low-carbon electricity.” That gloss is wrong in a way that matters at audit. The reporter does not buy low-carbon electricity in any physical sense — the electrons arriving at the meter are dispatched from whichever generators happened to be running on the grid in the hour the meter recorded consumption, and those generators are determined by merit-order economics that the reporter has no contractual ability to alter. Wind generation cannot be physically routed to a specific meter; nuclear baseload cannot be allocated to a corporate buyer. Physical electricity is fungible at the bus-bar — it is the same commodity once it enters the grid, regardless of which generation asset produced it.

What the reporter actually buys, in any market-based contract, is two things sold together or separately: (1) the electricity itself — the right to consume electrons from the grid, settled in kWh and priced in the local wholesale or retail market — and (2) the contractual claim over the environmental attribute of the generation associated with those kWh — the renewable origin, the zero-emission character, the fuel type — settled in MWh and traded as a separate financial or registry instrument. The two are severable. They can be sold together (a “bundled” instrument: the energy and its attribute pass to the same buyer in one transaction), or separately (the energy goes to one party at one price, the attribute goes to another party at another price).

Figure 3.1 — The energy/attribute severability diagram

Two flows from one renewable generation event. The physical flow follows merit-order grid dispatch and is identical to any other electron’s path. The contractual flow follows the certificate registry and can be assigned to any buyer who retires the certificate. The two are independent. Audit confusion in §7 failure modes (1) and (2) tracks back to readers conflating these flows.

Physical flow — fungible

1 MWh of electricity

Wind farm
↓ generation onto grid bus-bar
↓ merit-order dispatch by grid operator
↓ commingled with all other generation
↓ delivered to whichever meter is consuming
↓ settled in kWh through retail tariff

The reporter cannot trace specific electrons. The electricity is fungible at the bus-bar. Physical delivery is a property of the grid, not the contract.

Contractual flow — assignable

1 EAC representing 1 MWh attribute

Wind farm
↓ EAC issued by registry per MWh generated
↓ EAC held in registry account
↓ EAC sold (bundled with energy or unbundled)
↓ EAC retired against specific consumption claim
↓ retirement statement issued for audit

The certificate is the contractual claim. It can travel with the energy (bundled) or independently (unbundled). Once retired, it cannot be re-used by any other reporter.

Synthesis: the GHG Protocol Scope 2 Guidance recognises the MB inventory total as the product of the contractual flow, not the physical flow. A reporter with no instruments is allocated their share of the average grid attribute (location-based). A reporter with retired EACs is allocated the attribute they have retired. What you buy under a “renewable energy contract” is the contractual claim — and only the claim is in scope for Scope 2 MB accounting.

This architecture is why bundled and unbundled instruments differ in disclosure significance even when their MB arithmetic is identical. A bundled REGO retired against a 1 MWh consumption block produces a contractual claim that the energy and its attribute came from the same wind farm — but that claim says nothing about whether the wind farm would have been built without the REGO market. An unbundled REGO purchased on the Ofgem secondary market and retired against the same consumption block produces an identical contractual claim, but the linkage to specific generation is even thinner — the secondary market is a financial instrument layer, not a procurement channel. A contracted PPA for new-build generation produces a contractual claim plus a documented capital commitment — the wind farm exists because of the PPA. The arithmetic erases this distinction; the disclosure narrative cannot. The instrument equivalence problem of §2 is the symptom; the contractual claim architecture is the underlying mechanism.

The GHG Protocol Four-Tier Supplier Hierarchy

Named concept · Citable definition

The four-tier supplier hierarchy

The ordered preference for emission factor selection in market-based Scope 2 reporting as set out in the GHG Protocol Scope 2 Guidance (2015) §6.3 Quality Criteria, comprising Tier 1 supplier-specific rate, Tier 2 contract-specific rate (PPA), Tier 3 residual mix factor, and Tier 4 location-based factor as fallback, applied per-kWh in descending order of contractual specificity.

The Scope 2 Guidance is sparing about ordering rules, but the four tiers below are the canonical hierarchy as expressed in §6.3 and §6.10 of the 2015 Guidance and as it has been applied by reasonable-assurance auditors since publication. Each tier has a precise evidence requirement. Each tier has a distinct audit risk profile. The reporter applies the highest-specificity tier for which they hold qualifying evidence on each unit of consumption — different tiers can apply to different kWh in the same inventory.

Tier 1 Supplier-specific rate EFsupplier
Definition The annual emission factor disclosed by the electricity supplier or utility for the specific tariff under which the reporter took supply. Published in supplier annual disclosures (Fuel Mix Disclosure in the UK, Stromkennzeichnung in Germany, equivalent regulated disclosures in most EU member states). Backed by the supplier’s own retirement of EACs against the tariff plus residual mix on any uncovered portion.
When to use Default for any tariff with a regulated supplier disclosure. Apply when the reporter has no separately contracted EACs of their own — the supplier has done the matching at portfolio level.
Evidence required Supplier annual fuel-mix or emissions disclosure document for the reporting year, citing the specific tariff. Cross-reference to the supplier’s regulator filing where applicable. Retain the disclosure document; do not rely on supplier marketing collateral.
Audit risk Low to medium. Auditors check that the disclosed factor matches the regulator filing and that the tariff identifier on the bill matches the disclosure. Risk rises when a supplier offers tariff variants with materially different factors and the reporter has not verified which variant applies.
Tier 2 Contract-specific rate (PPA, contracted EAC retirement) EFcontract
Definition The factor implied by a contract that grants the reporter direct claim over a specific generation source: a physical or virtual PPA, a retail green tariff with disclosed project-level provenance, or a separately contracted EAC retirement against named generation. For zero-emission contracts (a new-build wind PPA, a solar EAC retirement) the implied factor is 0.0 kg CO₂e/kWh per the GHG Protocol Quality Criteria zero-emission convention.
When to use Apply on any kWh covered by a qualifying contract. The reporter must hold the contract themselves — the supplier’s own contracts are not the reporter’s contracts (those are Tier 1 territory). Contracted EACs retired by the reporter directly through registry accounts are Tier 2.
Evidence required Executed contract or PPA term sheet identifying the generation asset, the volume, and the EAC handling. Registry retirement statement covering the reporting year specifically. For VPPAs, the financial settlement evidence plus the EAC delivery statement. For SBTi target tracking, project-level additionality evidence per §8.
Audit risk Low. Tier 2 is the audit-grade benchmark — direct contractual provenance, named generation asset, retirement statement, additionality evidence available. The bundled-vs-unbundled distinction surfaces at SBTi review, not at general assurance review.
Tier 3 Residual mix factor EFresidual
Definition The published emission factor for the portion of grid electricity not claimed by any contractual instrument — the grid average less the generation already retired via EACs by other reporters. Published by the Association of Issuing Bodies (AIB) for EU/EEA/UK; by EPA eGRID for US NERC subregions. Higher than the location-based grid average in any jurisdiction with material EAC retirement.
When to use On any kWh of consumption not covered by Tier 1 or Tier 2 evidence, in jurisdictions where a published residual mix exists. The unmatched portion of partial-coverage MB calculations always uses Tier 3 where available.
Evidence required Citation to the AIB European Residual Mixes publication for the relevant year and member state, or to the EPA eGRID residual mix tables for the relevant US subregion. Vintage-matched: the residual mix year must align with the inventory year, not the publication date.
Audit risk Medium. Auditors check residual vintage alignment and source citation. Common failure: substituting the location-based grid factor for the residual on the unmatched portion (failure mode 7.2) — a methodological error specifically called out in CSRD ESRS E1-6.
Tier 4 Location-based factor as fallback EFgrid
Definition The published grid average emission factor for the jurisdiction supplying the meter — the same factor used in location-based reporting. Applied as the MB factor only in jurisdictions where Tier 1, 2, and 3 evidence is unavailable: typically jurisdictions outside the AIB and EPA territories that have no developed EAC market or published residual mix.
When to use On any kWh in jurisdictions without a published residual mix where the reporter holds no qualifying contractual instruments. The MB inventory line carries the LB figure for that consumption. This is the §6.3 dual-reporting invariant operating at site level — the MB total cannot be lower than LB simply because the methodology is unable to populate Tier 3.
Evidence required Same as location-based: published grid factor source (DEFRA / IEA / EPA) for the relevant year. Plus an explicit audit-trail note that no Tier 1, 2, or 3 evidence was available for the consumption in question.
Audit risk Low. The conservative fallback. The risk surfaces only if reporters use Tier 4 to mask absent Tier 3 residual evidence in a jurisdiction where residual is available — auditors check that Tier 4 is invoked because of jurisdiction unavailability, not because Tier 3 was skipped.
T-0 Tier-zero operational fallback (GreenCalculus-named pattern) EFgrid × premium
Definition Not in the GHG Protocol Scope 2 Guidance. A GreenCalculus-named operational pattern for the case where no published residual exists in a jurisdiction and the reporter wishes to apply a conservative untraced premium rather than fall back to Tier 4 LB on the unmatched portion. Applied as EFgrid × 1.10 to 1.20 with explicit audit flag. The Scope 2 Electricity Calculator uses 1.15× as default.
When to use Optional. In I-REC jurisdictions and other markets without published residual data, when the reporter wants to acknowledge the dirtier-than-average character of unclaimed generation without claiming to know its precise value. Conservative rather than rigorous.
Evidence required Documented reasoning for the premium chosen (typically referencing the EAC market depth in the jurisdiction). Audit-trail note that this is a GreenCalculus-named operational pattern, not a GHG Protocol-canonical tier.
Audit risk Medium. Defensible as a conservative position. Auditors will ask why Tier 4 was not used instead — the defensible answer is “to avoid understating the unmatched-portion intensity in a jurisdiction with material EAC retirement.” Reasonable assurance reviewers accept the pattern when documented.

Figure 4.1 — Tier selection flowchart, applied per kWh of consumption

1 · Does the reporter hold a contract or retired EAC over this kWh?
Yes — directly (PPA, VPPA, separately contracted EAC retirement) → Tier 2 apply contract-specific factor. Yes — indirectly via supplier disclosure → continue to question 2. No → continue to question 3.
2 · Has the supplier published a tariff-specific factor for the reporting year?
YesTier 1 apply supplier-specific rate. No (supplier offers no disclosure or only a portfolio average) → continue to question 3.
3 · Does the jurisdiction have a published residual mix factor?
Yes (AIB EU/EEA/UK, EPA eGRID for US subregions) → Tier 3 apply residual mix factor. No → continue to question 4.
4 · Is the reporter applying a conservative untraced premium?
YesT-0 apply grid × 1.10 to 1.20 with audit flag (GreenCalculus operational pattern, not GHG Protocol-canonical). NoTier 4 apply location-based grid factor as fallback.

Two structural points. First, tier selection is per-kWh, not per-site or per-portfolio — a single site can use Tier 2 on its PPA-covered consumption, Tier 3 on its unmatched consumption, and Tier 1 on a separate tariff for a sub-meter, all in the same inventory. Second, the tier hierarchy is downward-only: the reporter never voluntarily moves to a less-specific tier when more-specific evidence is available. Tier 4 is not a choice — it is a fallback. The audit pattern is to verify the tier selection per kWh aligns to the highest evidence available, and to flag any case where a lower tier appears to have been applied with higher-tier evidence on hand.

The Instrument Equivalence Problem — Full Analytical Treatment

The arithmetic of the market-based method renders nine instrument types and edge cases as numerically equivalent on the unit-of-MWh basis when the supplier or contract factor is zero. The disclosures, additionality posture, and audit risk diverge sharply. Table 5.1 is the canonical reference — readers citing this page should cite “GreenCalculus Scope 2 Market-Based Methodology v2.0, Table 5.1: Instrument Equivalence Matrix.”

Table 5.1 Instrument equivalence matrix — nine instrument types and edge cases against the GHG Protocol Quality Criteria, framework recognition, additionality posture, and residual treatment
Instrument Quality Criteria pass CDP CSRD ESRS E1 SBTi additionality 2026 Residual on unmatched Audit risk
REGO bundledUK · Ofgem Pass — all 7 Accepted Accepted Limited — additionality screening required AIB UK residual ≈ 0.488 kg/kWh Medium
REGO unbundledUK · secondary market Pass — all 7 Accepted Accepted with disclosure Generally not credited AIB UK residual ≈ 0.488 kg/kWh Medium-high
GO bundledEU/EEA · AIB issuing bodies Pass — all 7 Accepted Accepted Limited — Scandinavian hydro GOs especially scrutinised AIB residual per member state Medium
REC voluntaryUS · state markets + Green-e Pass — Green-e certified preferred Accepted Accepted with cross-border note Variable — Green-e certified credited; non-Green-e scrutinised EPA eGRID residual per NERC subregion Medium
I-RECAsia/Africa/LatAm · I-REC Standard Pass — all 7 Accepted Accepted with provenance disclosure Improving — emerging-market provenance scrutinised No published residual; T-0 untraced premium typically High
PPA bundled (physical)Global · direct contract Pass — all 7 Accepted Accepted, narrative recommended Full credit when new-build Per-PPA disclosed factor; residual on uncovered fraction Low
PPA unbundled / VPPAGlobal · CFD + EAC Pass — all 7 Accepted Accepted with project provenance Full credit when new-build Per-PPA disclosed factor; residual on uncovered fraction Low
Self-generation — EACs retainedGlobal · on-site Pass — direct ownership Accepted (out of Scope 2 boundary) Accepted (out of Scope 2 boundary) Full credit — direct ownership n/a — consumption never enters Scope 2 Low
Self-generation — EACs soldGlobal · trap pattern Fail — attribute relinquished Cannot claim Cannot claim Cannot claim — attribute is the buyer’s Residual mix on full on-site consumption High — failure mode 7.1

Three reading patterns. First, arithmetic equivalence ≠ disclosure equivalence: the seven instrument types in rows 1-7 produce identical zero-emission MB contributions per matched kWh, but the SBTi additionality column moves from “limited” to “full credit” across the same set. Second, the audit risk profile rises with the contractual distance from named generation: bundled PPA (row 6) is low-risk because the contract identifies the asset; unbundled REGO (row 2) is medium-high because the secondary market severs the link. Third, self-generation with EACs sold (row 9) is the only structural failure case — every other row produces a defensible disclosure, but selling EACs while claiming the on-site reduction is a Quality Criteria failure regardless of how the arithmetic appears. This is failure mode 7.1 in the taxonomy below.

Jurisdiction-by-Jurisdiction EAC Market Maturity

The market-based method depends on EAC market depth, residual mix availability, and registry maturity in each jurisdiction the reporter operates in. Table 6.1 is the cross-jurisdictional reference — for any multinational reporter, the per-jurisdiction maturity rating informs the audit-risk weight applied to MB claims from that jurisdiction. Hardcoded values: there is no MasterBrain section for EAC market maturity at v2025.6; the data below is researched and verified at this page’s review date.

Table 6.1 EAC market maturity matrix — instrument types, issuing bodies, residual mix availability, and audit risk for cross-border claims across thirteen jurisdictions
Jurisdiction EAC instrument Issuing body Residual published Source Maturity Cross-border audit risk
United Kingdom0.131 kg/kWh LB REGO Ofgem Yes — AIB AIB European Residual Mixes (annual) Established Low — robust regulator, audit standard
Germany0.330 kg/kWh LB GO (Herkunftsnachweis) Umweltbundesamt (HKNR) Yes — AIB AIB European Residual Mixes (annual) Established Low — large active EAC market
France0.041 kg/kWh LB GO EEX (national agent) Yes — AIB AIB European Residual Mixes (annual) Established Low — nuclear-dominant grid; GO market shallower than DE
Spain0.154 kg/kWh LB GO (Garantías de Origen) CNMC Yes — AIB AIB European Residual Mixes (annual) Established Low — well-developed solar PPA market
Netherlands0.254 kg/kWh LB GO (Garanties van Oorsprong) VertiCer Yes — AIB AIB European Residual Mixes (annual) Established Low — mature import market
United States — national0.350 kg/kWh LB REC State / regional REC tracking systems Yes — EPA eGRID per NERC subregion EPA eGRID residual mix tables Established Medium — fragmented across state markets
US WECC-CAMX (California)0.195 kg/kWh LB REC (CA-eligible) + WREGIS WREGIS Yes — EPA eGRID EPA eGRID residual mix tables Established Low — strong tracking system
US RFCE (PJM East)0.272 kg/kWh LB REC (PJM-EIS GATS) PJM-EIS GATS Yes — EPA eGRID EPA eGRID residual mix tables Established Low — high-volume corporate PPA region
Singapore0.497 kg/kWh LB I-REC (Singapore) EMA / I-REC registry No Developing Medium — NEA carbon tax uses LB; MB voluntary
Australia0.525 kg/kWh LB LGC (Large-scale Generation Certificate) Clean Energy Regulator Partial — Climate Active method Climate Active Carbon Neutral Standard Established Low — mature scheme; LGC pricing transparent
Japan0.477 kg/kWh LB J-Credit + Green Power Certificate + I-REC METI / I-REC registry No Developing Medium — fragmented instrument types; vintage rules complex
India0.670 kg/kWh LB I-REC + REC (CERC) I-REC registry / CERC No Developing High — coal-dominant grid amplifies MB-LB delta; provenance scrutinised
Brazil0.110 kg/kWh LB I-REC I-REC registry No Developing Medium — hydro-dominant grid; LB already low so MB delta moderate
South Africa0.699 kg/kWh LB I-REC + nascent local instruments I-REC registry No Nascent High — coal-dominant grid amplifies MB-LB delta; thin EAC market

Two patterns. First, EAC market maturity correlates with audit confidence but not with MB reduction potential: the highest MB-vs-LB delta opportunities are in the highest-LB jurisdictions (India, South Africa) where mature EAC markets do not yet exist. Reporters in these jurisdictions face a tension between the methodological rigor of mature-market claims and the impact magnitude of nascent-market claims. Second, cross-border claims carry their own audit risk regardless of source-jurisdiction maturity: an EU reporter retiring I-RECs from Brazil to cover their Brazilian operations is on solid ground; the same reporter retiring I-RECs from Brazil against their European operations triggers cross-border failure mode 7.3. Geographic correspondence between consumption and EAC retirement is one of the seven Quality Criteria.

The Double-Claiming Taxonomy — Six Failure Modes

Named concept · Citable definition

The double-claiming taxonomy

Six structurally distinct ways a Scope 2 market-based disclosure can claim emission reduction it is not entitled to under the GHG Protocol Quality Criteria, each named, numbered, and characterised by its arithmetic signature so that auditors can detect the failure mode from the inventory output without needing access to underlying contracts.

The taxonomy below is the canonical six. Each is named for citation as “GreenCalculus Scope 2 MB Methodology v2.0, failure mode 7.n.” Failure mode 7.1 is the highest-frequency in production disclosures; 7.5 is the lowest-frequency but the most damaging when it occurs.

7.1 Sold-EAC on-site claim
Definition
The reporter operates on-site renewable generation, sells the issued EACs to a third party for revenue, and then claims the on-site consumption as zero-emission MB.
How it arises
A site with PV generation produces REGOs / GOs / RECs that are sold via the registry secondary market. Procurement and inventory teams operate separately; the inventory team is unaware the EACs were sold. Or: the reporter understands the rule but treats the EAC sale as “extra revenue” without reflecting the lost Scope 2 claim.
Detection
Auditors cross-check the registry retirement statement against the on-site generation volume. Any EAC issued from on-site generation that does not appear on the reporter’s own retirement statement was sold. The reporter must use the residual mix on the corresponding kWh — not the on-site zero-emission claim.
Prevention
Reconcile EAC issuance from on-site generation against EAC retirement under the reporter’s own registry account quarterly. Document the policy: either retain all on-site EACs and claim zero-Scope-2 on the consumption, or sell EACs and apply residual mix to that consumption. Never both.
7.2 Grid-average unmatched substitution
Definition
The reporter holds EACs covering only a portion of consumption and applies the location-based grid average factor (Tier 4) to the unmatched portion in a jurisdiction where a published residual mix (Tier 3) exists.
How it arises
The calculator or spreadsheet defaults to using the LB grid factor on the unmatched portion because Tier 3 logic was not built in. Or: the reporter knows residual exists but chooses the lower LB factor to flatter the MB total. The arithmetic gain: in a UK 50%-coverage scenario, applying 0.177 instead of 0.488 on the unmatched 50% understates the MB total by ~36% relative to correct treatment.
Detection
Auditors check the residual mix factor cited in the disclosure against the AIB / EPA published value for the relevant year. Any partial-coverage MB calculation in an AIB or EPA jurisdiction that does not cite a published residual mix is flagged for follow-up. ESRS E1-6 specifically requires the residual citation.
Prevention
Use a calculator that enforces Tier 3 by jurisdiction. Maintain a per-inventory-year citation log of the residual mix factor used per jurisdiction. Cross-check against the AIB annual residual mix release and EPA eGRID release vintage.
7.3 Cross-border instrument mismatch
Definition
The reporter retires EACs from one jurisdiction against consumption in a different jurisdiction outside the geographic boundary recognised by the GHG Protocol Quality Criteria — typically when EACs from a low-cost jurisdiction (I-RECs from a developing market) are retired against high-cost jurisdiction consumption (EU operations).
How it arises
Cost arbitrage: bundled REGOs from Norwegian hydro cost a fraction of equivalent Spanish solar EACs. Procurement teams pursue the lower-cost option without verifying the geographic correspondence requirement. The arithmetic flatters the MB total because the EAC volume is the same; the disclosure fails Quality Criterion 4 (geographic correspondence).
Detection
Auditors cross-check the issuing-body jurisdiction of retired EACs against the consumption jurisdictions in the inventory. Mismatched pairings outside an interconnected market (the AIB cross-border framework permits within EU/EEA/UK) are flagged. CDP and CSRD increasingly request the issuing-body jurisdiction in disclosure narrative.
Prevention
Match EAC sourcing to consumption jurisdiction. Within the AIB framework, cross-border retirement is permitted with explicit disclosure of the issuing-body country. Outside AIB, single-jurisdiction matching is the audit-grade default.
7.4 Prior-year retirement against current inventory
Definition
The reporter retires EACs that were issued in a year prior to the consumption year — typically EACs issued in 2024 retired in 2026 to cover 2026 consumption. The Quality Criteria require vintage matching: the EAC must be issued for generation in the same period as the consumption being claimed.
How it arises
REGOs and GOs typically have a multi-year validity window from issuance. Procurement teams buy on the secondary market without checking issuance date — the registry permits the trade, but the resulting retirement does not satisfy vintage matching. Most issuing bodies enforce a maximum vintage gap (Ofgem permits REGOs to be retired against consumption up to two years after issuance), but reporting frameworks set tighter rules.
Detection
Auditors compare the issuance vintage on the retirement statement against the consumption year. Vintage mismatch beyond the framework’s permitted window (CDP requires within-year; CSRD increasingly aligning) is a non-compliance finding.
Prevention
Procure EACs with issuance vintage matching the inventory year. Track vintage in the procurement system, not just volume. The retirement statement must show issuance vintage; reject any procurement that does not.
7.5 Over-retirement claim (EACs retired > kWh consumed)
Definition
The reporter retires more EACs than their actual consumption and claims an MB total below zero — or claims a “100%+ renewable” label backed by over-retirement. The arithmetic appears to allow a negative emission total; the methodology does not.
How it arises
Procurement over-buys EACs as a buffer against consumption variance, then the reporter’s marketing function claims the over-retirement publicly. Or: the reporter genuinely intends to drive a “negative” MB total without recognising that the GHG Protocol caps MB at zero (excess EACs cannot generate negative emissions).
Detection
Auditors compare retired EAC volume against consumption volume. Retirement > consumption in any reporting period is a Quality Criteria failure (Criterion 6: only consumption-aligned retirement counts). The disclosed MB total cannot be below zero. Marketing claims of “more than 100% renewable” are flagged.
Prevention
Cap retirement at consumption. Treat surplus EACs as inventory for the next reporting period (within vintage rules) or sell them back into the secondary market. Do not claim “100%+” — the methodology floors at zero MB.
7.6 Double-framework claim (different totals across CDP / CSRD / SBTi)
Definition
The reporter discloses different MB totals for the same instrument basis under different frameworks — typically a more aggressive total to CDP (where bundled REGOs receive face-value treatment) versus a more conservative total to SBTi (where additionality screening reduces the credited fraction). Reasonable; but the disclosure narrative must reconcile the two — failing to do so is a transparency failure.
How it arises
Different reporting teams handle different frameworks. The CDP submission runs MB at face value; the SBTi target-progress report quietly applies an additionality discount; neither references the other. Stakeholders comparing the two find unexplained divergence.
Detection
Comparing the inventory totals across framework filings. Auditors of any one framework increasingly request the totals filed under other frameworks — discrepancies trigger reconciliation requirement. SBTi target-progress narratives are scrutinised by analysts comparing them to CDP scoring submissions.
Prevention
Maintain a single source-of-truth MB calculation, with framework-specific commentary appended. Disclose the same MB total to all frameworks, with a clear narrative for any framework-specific adjustment. Reconcile across CDP, CSRD, and SBTi in the same disclosure cycle.

The Additionality Debate — Three Positions

The methodological status of bundled instruments — REGOs, GOs, RECs — relative to contracted PPAs has been the live debate in Scope 2 reporting since approximately 2022. The debate is not whether MB accounting is valid (it is, under the 2015 Guidance); it is whether the quality of the MB claim depends on the additionality posture of the underlying instrument. Three positions are now coexistent in the standards landscape, each held by a different rule-maker, each with a different disclosure consequence. Reporters navigating all three simultaneously face a coherence problem the standards have not yet resolved.

Position A

GHG Protocol Scope 2 Guidance (2015)

Quality Criteria are sufficient — additionality not required

The 2015 Scope 2 Guidance §6.10 sets out seven Quality Criteria for market-based instruments: contractual conveyance, attribute claim, exclusive ownership, reasonable proximity to consumption, vintage alignment, instrument-only basis, and tracking systems. An instrument satisfying these seven is a valid MB input regardless of additionality. A bundled REGO from existing hydropower passes all seven; the Guidance does not require the reporter to demonstrate that the hydropower would not have been built without the REGO market. Position A is the floor — every framework accepts an instrument that satisfies the Quality Criteria as a Scope 2 MB input.

Position B

SBTi Corporate Net-Zero Standard (2024 emerging)

Additionality required for target progress credit

SBTi’s emerging position from approximately 2024 onward distinguishes inventory disclosure (governed by the GHG Protocol) from target progress credit (governed by SBTi). For inventory disclosure, Position A holds — bundled instruments are accepted. For SBTi target progress under the Absolute Contraction Approach, bundled instruments from existing assets do not count without project-level additionality evidence. A reporter showing 50% Scope 2 reduction year-on-year that is entirely driven by bundled REGO procurement does not move their SBTi target progress dial — the target validation review will require additionality evidence. Position B does not invalidate Position A; it adds an SBTi-specific second layer.

Position C

CSRD ESRS E1 transition plan requirement (2023)

Additionality posture must be disclosed in the transition plan

ESRS E1 does not require additionality for the inventory disclosure (Position A holds for the E1-6 reporting line). It does require, in the E1-1 transition plan disclosure, that the reporter narrate their additionality strategy — what proportion of their MB claim is bundled versus contracted, what their procurement strategy is for shifting toward additional instruments, what their dependence on residual mix is. The CSRD position is procedural rather than calculative: the inventory total is calculated under Position A rules, but the transition plan must explain the quality of the claim. Position C makes opacity expensive without changing the arithmetic.

How the three interact for a reporter navigating all three: the inventory total under all three frameworks is the same — Position A governs the calculation. The additional disclosure burden under Position C requires a transition plan narrative that addresses the bundled-versus-contracted mix. The target progress credit under Position B may differ from the inventory reduction — a 50% inventory reduction may translate to a 20% SBTi-credited reduction if 60% of the inventory reduction comes from bundled instruments. Reporters who do not pre-empt this divergence in their disclosure narrative face stakeholder confusion when analysts compare the inventory total to the SBTi progress claim and find a gap. The audit-grade response is to disclose the bundled-versus-contracted mix in the inventory commentary, the additionality strategy in the transition plan, and the SBTi-credited fraction in the target progress narrative — three disclosures, one coherent story, no surprises at year-end review. This is the methodology disposition this page recommends.

Methodology Version History

The market-based method has evolved through six identifiable milestones since the GHG Protocol Corporate Standard’s first publication. Reporters using historical inventories for trend analysis or target baseline establishment must understand which milestones triggered methodology restatement requirements (changes that retroactively alter prior-year figures) and which were prospective-only (changes that apply from a forward date with prior-year figures unchanged). Table 9.1 is the standards-document log.

Table 9.1 Methodology version history — standards-document log of GHG Protocol market-based method evolution and adjacent framework releases that affect MB disclosure
Date Document What changed Why it matters Restatement
2001 GHG Protocol Corporate Standard (initial) Scope 1, 2, 3 framework defined. Scope 2 specified as “indirect emissions from purchased electricity” without methodological detail on factor selection. Foundational. No MB method existed. All Scope 2 reporting was implicitly location-based. No (foundational)
2004 GHG Protocol Corporate Standard v1.0 (revised) First formal Corporate Standard publication. Scope 2 boundary clarified; LB method implicit. Set the boundary for two decades. EACs and PPAs not yet a methodological feature. No (boundary unchanged)
2011 Scope 2 Guidance — consultation draft First public consultation on dual-method reporting. Introduced the location-based / market-based distinction. Quality Criteria drafted. Signal that MB methodology was coming. Reporters with EAC strategies began preparing dual disclosure infrastructure. No (consultation only)
2013 Scope 2 Guidance — final draft Quality Criteria refined to seven. Tier hierarchy taking shape. Final consultation period. Pre-publication review by major reporters and standards bodies. Set publication parameters. No (consultation only)
January 2015 Scope 2 Guidance — publication (Corporate Standard amendment) Dual-reporting requirement formalised (§6.3). Market-based method first defined. Seven Quality Criteria fixed. Four-tier supplier hierarchy implicit in §6.3 + §6.10. Residual mix concept introduced. The methodological foundation of every Scope 2 MB disclosure since. The single most consequential milestone. All current MB methodology traces to this document. Pre-2015 inventories using a “renewable” claim without dual-reporting are not comparable to post-2015 dual-disclosure inventories. Yes — for trend baselines extending pre-2015
2023 CSRD ESRS E1 (final) Mandatory dual disclosure for EU companies in scope. Explicit residual mix factor citation requirement (E1-6). Transition plan additionality narrative requirement (E1-1). Value-chain T&D disclosure expectation. Position C above. Did not change MB calculation, but changed disclosure burden. EU-domiciled reporters must now address residual mix sourcing and additionality posture explicitly. No (prospective from FY2024 reporting)
2024 SBTi Corporate Net-Zero Standard — additionality position Position B above. Bundled REGO/GO/REC instruments may not count toward target progress without project-level additionality evidence. Did not change inventory MB calculation. Did change the SBTi target validation result for reporters whose Scope 2 reduction trajectory was bundled-instrument-driven. Triggered a wave of “additionality screening” disclosures in 2024–2025 corporate reports. No (target progress only; inventory unchanged)
2026 (consultation) GHG Protocol Corporate Standard revision — in consultation In consultation as of this page’s review date — not finalised. Public consultation on the next Corporate Standard revision is ongoing through 2026. Areas of likely revision include hourly carbon-free energy matching, residual mix governance, and Quality Criteria refinement. The revision is not yet binding methodology. Reporters tracking the revision should monitor publication timing. Restatement requirements will depend on the final scope of changes. Position monitoring, not action, is the current posture. Pending — depends on final scope

Two structural points for trend analysis. First, any Scope 2 trend baseline extending before January 2015 must be restated to the post-2015 dual-reporting basis for comparability. Pre-2015 “renewable energy used” claims do not map to post-2015 LB+MB disclosure. SBTi target baselines anchored before 2015 are not directly comparable to current-year disclosures without methodology restatement. Second, the 2023 CSRD ESRS E1 release did not require restatement because the underlying MB calculation was unchanged — it required additional disclosure (residual citation, transition plan narrative) prospectively from FY2024. The 2024 SBTi additionality position is similarly prospective-only at the target-progress level. The 2026 GHG Protocol revision is the next potential restatement trigger, and reporters should plan accordingly while it remains in consultation.

Worked Examples — Audit Records

Three audit-record snapshots at this page’s review date (2026-05-10). Hardcoded values throughout per Editorial Standards §9b. Each example replicable in the Scope 2 Electricity Calculator; the calculator’s hash output will match the values shown here as long as MasterBrain v2025.6 is the active version.

Example A UK office, Tier 1 supplier-specific rate (non-zero) — disclosed renewable tariff at 0.043 kg CO₂e/kWh Scope 2 MB
Your data source
Single-site UK office — fictional
Reporting year: 2026  |  Reporting framework: UK SECR + CDP
Site: London headquarters, single half-hourly meter
Annual consumption: 2,500,000 kWh
Tariff: Supplier “Green Origin” tariff with disclosed annual factor 0.043 kg CO₂e/kWh — backed by supplier portfolio of REGOs plus residual mix on uncovered fraction; supplier annual disclosure document published Q1 2026
Reporter-held instruments: None (the supplier handles matching at portfolio level)
Tier selection: Tier 1 — supplier-specific rate The non-zero Tier 1 case. Demonstrates that an MB total can be meaningfully below LB without being zero — the supplier-disclosed factor reflects partial portfolio matching.
Pre-step — tier selection: Question 1 of the tier flowchart: does the reporter directly hold contracts? No — the supplier handles matching. Question 2: has the supplier published a tariff-specific factor? Yes (0.043 disclosed). → Tier 1. Question 3 not reached. The supplier disclosure document is the audit evidence.
Location-based
Activity data Q2,500,000 kWh
UK grid factor (DEFRA 2025)0.177 kg CO₂e/kWh
E = Q × EF2,500,000 × 0.177
= kg CO₂e= 442,500 kg
÷ 1000 → tCO₂e= 442.50 tCO₂e
442.50 tCO₂e
LB · DEFRA 2025
Market-based · Tier 1
Activity data Q2,500,000 kWh
EFsupplier (disclosed)0.043 kg CO₂e/kWh
E = Q × EFsupplier2,500,000 × 0.043
= kg CO₂e= 107,500 kg
÷ 1000 → tCO₂e= 107.50 tCO₂e
Qunmatched0 — supplier handles fully
107.50 tCO₂e
MB · Tier 1 supplier 0.043
Δ MB vs LB: 107.50 − 442.50 = −335.00 tCO₂e (−75.71%). LB anchor preserved per Scope 2 §6.3. Both totals appear in the disclosure pair.
The supplier-disclosed factor is non-zero because the supplier’s portfolio includes residual mix exposure on the uncovered fraction — typical of UK “Green” tariffs that are 70-80% REGO-backed with residual on the rest. The reporter’s MB disclosure cites the supplier disclosure document as evidence; no separately-held instruments. Compared to a 100% bundled REGO scenario, this Tier 1 disclosure has higher arithmetic but stronger audit posture — the supplier has done the residual matching transparently. Replicate in calculator → with country = United Kingdom, consumption = 2,500,000 kWh, method = LB+MB, supplier factor = 0.043.
Example B EU multi-site portfolio — Tier 2 + Tier 3 + Tier 4 in parallel Scope 2 MB
Your data source
Three-site European portfolio — fictional
Reporting year: 2026  |  Reporting framework: EU CSRD / ESRS E1
Site 1 — Frankfurt office (Germany): 1,800,000 kWh · 50% bundled GO from existing hydro · supplier factor not disclosed (zero convention) → Tier 3 on unmatched 50%
Site 2 — Lyon R&D centre (France): 1,200,000 kWh · No instruments held → Tier 4 LB fallback at site level
Site 3 — Madrid manufacturing (Spain): 800,000 kWh · 100% I-REC from new-build solar PPA · supplier factor 0.0 → Tier 2 contracted rate Multi-jurisdictional portfolio with three different tier states operating in parallel. Demonstrates per-kWh tier selection at site level with portfolio aggregation under the §6.3 invariant.
Pre-step — per-site tier selection: Frankfurt: 50% bundled GO → Tier 2 implicit on matched (zero convention) + Tier 3 on unmatched (residual ≈ 0.3795 = grid 0.330 × 1.15 untraced premium fallback for AIB-published German residual not yet in MasterBrain). Lyon: no instruments → Tier 4 at site level (LB carries to MB per §6.3 invariant). Madrid: contracted PPA → Tier 2 across all consumption. Three tiers operating across the portfolio simultaneously.
Site Country kWh Tier(s) EAC % LB tCO₂e MB tCO₂e
FrankfurtGermany1,800,000T2 + T350% GO 1,800,000 × 0.330 = 594.00 (900,000 × 0.0) + (900,000 × 0.3795) = 341.55
LyonFrance1,200,000T40% 1,200,000 × 0.041 = 49.20 49.20 (LB carries to portfolio per §6.3)
MadridSpain800,000T2100% I-REC PPA 800,000 × 0.154 = 123.20 (800,000 × 0.0) = 0.00
Portfolio totals 3,800,000 766.40 tCO₂e 390.75 tCO₂e
Portfolio reconciliation and intensity
Total LB594.00 + 49.20 + 123.20 = 766.40 tCO₂e
Total MB341.55 + 49.20 + 0.00 = 390.75 tCO₂e
Δ MB vs LB390.75 − 766.40 = −375.65 tCO₂e (−49.01%)
LB intensity766.40 / 3,800,000 × 1000 = 0.2017 kg CO₂e/kWh
MB intensity390.75 / 3,800,000 × 1000 = 0.1028 kg CO₂e/kWh
Three tiers operating in parallel produce a portfolio MB-vs-LB delta of −49% — the structural pattern of mixed-tier portfolios. The Madrid Tier 2 site contributes the largest MB reduction per kWh (a clean zero); the Frankfurt Tier 3 site contributes a partial reduction with the residual penalty on the unmatched 50%; the Lyon Tier 4 site contributes no reduction (LB carries to MB). For ESRS E1-6 disclosure, the residual mix factor on the Frankfurt unmatched portion (0.3795) is cited explicitly with provenance — currently the calculator’s untraced premium fallback (German AIB-published residual not yet in MasterBrain). For the Madrid PPA, the SBTi additionality posture is full credit (new-build solar). For the Frankfurt bundled GO, the SBTi posture is limited credit pending additionality screening (the hydro asset existed pre-contract). The transition plan narrative for this portfolio under Position C addresses this mix explicitly. Replicate in calculator → using multi-site mode with three sites configured as above.
Example C UK site — sold-EAC double-claim attempt (failure mode 7.1, with audit detection) Failure case
Your data source
Single-site UK manufacturing — fictional
Reporting year: 2026  |  Reporting framework: UK SECR + CDP + SBTi tracking
Annual consumption: 2,500,000 kWh
On-site solar PV: 1,500,000 kWh generated, fully consumed on-site
EAC handling — what the reporter did: 1,500,000 REGOs issued by Ofgem against the on-site solar generation; reporter sold all 1,500,000 REGOs in Q1 2026 to a third party for ~£15,000 revenue
Reporter’s claimed MB inventory: on-site solar treated as zero-emission for the 1,500,000 kWh covered; grid factor applied to the residual 1,000,000 kWh purchased from the grid
Reporter’s claimed MB total: (1,500,000 × 0.0) + (1,000,000 × 0.177) = 177.00 tCO₂e The trap pattern. Walks through what the reporter did, why the claim fails, what the correct MB figure is, and how an auditor detects the failure from the inventory output alone.
Pre-step — why the claim fails: The reporter sold the REGOs. The renewable attribute over the 1,500,000 kWh of on-site solar is now owned by a third party — the buyer of the REGOs has the contractual claim. Per §3 contractual claim architecture, energy and attribute are severable; the reporter retained the energy but not the attribute. The on-site consumption cannot be claimed as zero-emission MB. Tier 2 fails (no contract over the attribute), Tier 1 fails (no supplier disclosure for self-generation), Tier 3 applies (residual mix on full consumption). The correct MB figure uses the AIB UK residual mix on all 2,500,000 kWh — the reporter retained no qualifying instruments.
What the reporter claimed (incorrect)
On-site (claimed zero)1,500,000 × 0.0 = 0 kg
Grid (claimed LB factor)1,000,000 × 0.177 = 177,000 kg
Sum177,000 kg = 177.00 tCO₂e
vs LB anchor 442.50claimed Δ −60.0%
177.00 tCO₂e
MB · CLAIMED — Quality Criteria 6 fail
Correct MB (residual mix, full consumption)
All consumption (no retained EACs)2,500,000 kWh
EFresidual (AIB UK 2024)≈ 0.488 kg CO₂e/kWh
E = Q × EFresidual2,500,000 × 0.488 = 1,220,000 kg
÷ 1000 → tCO₂e= 1,220.00 tCO₂e
Δ vs LB anchor 442.50+777.50 t (+175.7%)
1,220.00 tCO₂e
MB · Correct — Tier 3 residual on full consumption
Audit gap: 1,220.00 − 177.00 = 1,043.00 tCO₂e understated in the reporter’s claim (an arithmetic correction of +589% to bring the claim into compliance). Detection signature: MB > LB in the corrected disclosure — when residual mix exceeds the location-based grid average, the corrected MB exceeds LB. This is the canonical structural detection heuristic for failure mode 7.1.
The auditor’s detection path: cross-check the Ofgem retirement statement under the reporter’s account against the on-site generation volume. Generation = 1,500,000 kWh; retired in reporter’s account = 0; retired against third-party accounts = 1,500,000. The reporter sold the attribute. Per §3 severability, the reporter retained the energy but relinquished the attribute. The MB calculation must use residual mix on the full 2,500,000 kWh of consumption — not just the 1,000,000 kWh of grid imports. The corrected MB total of 1,220.00 tCO₂e exceeds the LB total of 442.50 tCO₂e because the AIB UK residual mix (0.488) exceeds the LB grid average (0.177). Whenever a corrected MB exceeds the LB anchor, the structural cause is residual mix application — and that almost always traces to a sold-EAC scenario on a site that should have retained its instruments. The reporter’s correction path: re-state the inventory with the corrected MB total; disclose the EAC sale as a separate line in the procurement narrative; consider repurchasing equivalent EACs in subsequent years to retain the on-site reduction claim. Replicate in calculator → with country = United Kingdom, consumption = 2,500,000 kWh, method = LB+MB, instruments held = none, residual mix override = 0.488.

Standards Alignment

Six standards govern the MB methodology and its disclosure consequences.

Standard Role for the market-based method
GHG Protocol Corporate Standard + Scope 2 Guidance (2015) Defines the dual-method requirement (§6.3), the seven Quality Criteria (§6.10), and the four-tier supplier hierarchy implicit in §6.3 + §6.10. The methodological foundation of every MB inventory line.
GHG Protocol Scope 3 Standard Defines Cat 3 (FERA) — the home for the T&D losses companion line. Computed against LB factor only regardless of MB instrument basis; physical losses occur on the grid regardless of contract.
CSRD / ESRS E1 EU mandatory dual disclosure (E1-6) with explicit residual mix factor citation requirement. Transition plan additionality narrative requirement (E1-1). Position C in the additionality debate. Prospective from FY2024 reporting.
SBTi Corporate Net-Zero Standard LB-anchored target baseline expectation. Year-on-year MB progress under the Absolute Contraction Approach. Position B in the additionality debate — bundled instruments may not credit toward target progress without project-level evidence.
UK DEFRA 2025 UK grid factor: 0.131 kg CO₂e/kWh — used as Tier 4 fallback and as LB anchor in dual disclosure. Source for UK SECR.
ISO 14064-1 Reasonable-assurance audit standard. Sets evidence retention and methodology transparency requirements that govern the audit pre-flight checklist in §13.

What the Calculator Handles vs What You Decide

The Scope 2 Electricity Calculator automates the mechanical steps of MB calculation. This methodology page covers the upstream decisions the calculator cannot make for you.

⚙ Calculator handles automatically
  • Tier 1 supplier-specific factor input with audit-trail retention
  • Tier 2 contract-specific factor input for PPA/VPPA matched portion
  • Tier 3 residual mix factor application on the unmatched portion (with audit warning where untraced premium fallback applies)
  • Tier 4 LB fallback at site level when no instruments held; LB carry-forward to portfolio MB per §6.3 invariant
  • Per-site EAC matching with REGO / GO / REC / I-REC / PPA instrument tagging
  • Multi-site portfolio mode with up to 5 sites; per-site tier breakdown; portfolio totals carrying the §6.3 invariant
  • Dual-method calculation (LB + MB) with the §6.3 invariant enforced — LB is never suppressible
  • Audit mode with full calculation chain, hash for replay, JSON + CSV export with full provenance
✎ You must decide before using the calculator
  • Tier selection per kWh — apply the highest-specificity tier for which qualifying evidence exists; never use a lower tier when higher-tier evidence is on hand
  • Instrument basis — bundled REGO/GO/REC vs contracted PPA; per §5 instrument equivalence matrix
  • Additionality posture — Position B impact on SBTi target progress for bundled instruments
  • EAC retention vs sale — for self-generation, retained EACs preserve zero-Scope-2; sold EACs require residual mix on the on-site consumption (failure mode 7.1)
  • Vintage matching — issuance year of EACs must align with consumption year (failure mode 7.4)
  • Cross-border claim verification — issuing-body jurisdiction vs consumption jurisdiction (failure mode 7.3)
  • Residual mix override — calculator default is grid × 1.15 untraced premium; for AIB-published European jurisdictions, input the AIB residual mix value
  • Framework reconciliation — single source-of-truth MB total across CDP, CSRD, and SBTi disclosures; reconcile any framework-specific commentary explicitly (failure mode 7.6)
  • Source documentation — supplier disclosures, PPA contracts, EAC retirement statements with vintage, residual mix citations for audit retention

Ready to compute? Open the Scope 2 Electricity Calculator →

Audit Checklist — Market-Based Reasonable-Assurance Pre-Flight

Eight items, MB-specific (not duplicating the electricity methodology checklist which covers grid factor freshness, dual-method completeness, and T&D inclusion). Run this list before submitting any MB claim for reasonable-assurance review under ISO 14064-1 or equivalent.

Eight MB-specific audit items
  1. 01
    Instrument retirement evidence per claim. Every claimed REGO / GO / REC / I-REC traces to a registry retirement statement. Retirement vintage matches consumption year (failure mode 7.4). Sample at least 5 instruments per material EAC class. Reject any claim backed only by procurement contract without retirement confirmation.
  2. 02
    Tier selection justification per kWh. For each portion of consumption, document which tier was applied and why a higher tier was not. Tier 4 invocations require an explicit note that no Tier 1, 2, or 3 evidence was available; Tier 3 invocations require the published residual mix citation; Tier 2 invocations require contract reference; Tier 1 requires the supplier disclosure document.
  3. 03
    Residual mix source citation with vintage. For Tier 3 applications, cite the AIB European Residual Mixes publication or EPA eGRID residual table by year. Vintage must match inventory year, not publication date. Failure mode 7.2 detection — explicit citation prevents the grid-average substitution error.
  4. 04
    Cross-border claim evidence (failure mode 7.3). Where retired EACs originate from a different jurisdiction than the consumption they cover, document the geographic correspondence framework permitting the cross-border claim. AIB framework permits within EU/EEA/UK with disclosure; outside AIB, single-jurisdiction matching is the audit-grade default.
  5. 05
    Additionality posture disclosure. For SBTi-tracked reporters, the target-progress narrative addresses Position B explicitly. Bundled instruments are flagged; contracted PPAs are flagged with project-level additionality evidence. For ESRS E1 reporters, the transition plan addresses Position C — what proportion of the MB claim is bundled vs contracted, and how that ratio is shifting.
  6. 06
    Version history restatement trigger check. If using a baseline year before January 2015, restate to post-2015 dual-method basis (per Table 9.1). If the 2026 GHG Protocol revision finalises during the reporting cycle, monitor for restatement requirements per the consultation outcome.
  7. 07
    Sold-EAC reconciliation (failure mode 7.1). For any on-site renewable generation, reconcile EAC issuance volume against retirement volume in the reporter’s own registry account. Any EAC issued from on-site generation that does not appear in the reporter’s retirement statement was sold; the corresponding consumption uses residual mix, not zero-emission claim. This is the highest-frequency MB failure in production disclosures.
  8. 08
    Cross-framework reconciliation (failure mode 7.6). The MB total disclosed to CDP, CSRD, and SBTi traces to a single source-of-truth calculation. Framework-specific commentary explains any narrative-level adjustment (e.g. SBTi additionality screening reducing credited fraction) without altering the inventory total. Stakeholders comparing across filings find no unexplained divergence.

Methodology Metadata — for GHG Inventory Documentation

Copy verbatim into your GHG inventory methodology statement for ISO 14064-1 transparency compliance. Adjust the tier, instrument, and framework lines to match your inventory choices.

Methodology GreenCalculus Scope 2 Market-Based Methodology v2.0 (May 2026). greencalculus.com/methodology/scope-2-market-based/. Companion to the Scope 2 Electricity Methodology.
Method basis GHG Protocol Corporate Standard + Scope 2 Guidance (2015 amendment). Dual-reporting per §6.3. Quality Criteria per §6.10. Four-tier supplier hierarchy applied per kWh.
Tier(s) applied [Tier 1 supplier-specific | Tier 2 contract-specific (PPA/VPPA/contracted EAC) | Tier 3 residual mix | Tier 4 LB fallback | T-0 untraced premium]. Per-kWh selection documented in audit trail. Highest-specificity tier applied for which qualifying evidence exists.
Instrument basis [None | REGO bundled | REGO unbundled | GO bundled | REC voluntary | I-REC | PPA bundled | PPA unbundled / VPPA | Self-generation EACs retained]. EAC retirement statements retained per ISO 14064-1 §6 evidence requirements. Vintage matching to consumption year confirmed. Per Table 5.1.
Residual mix [AIB European Residual Mix YYYY | EPA eGRID residual subregion YYYY | T-0 grid average × 1.15 untraced-premium approximation (calculator fallback for jurisdictions without published residual)]. Cited explicitly in MB disclosure per CSRD ESRS E1-6.
Additionality posture [Bundled instruments — limited credit per SBTi 2024 position; full disclosure in transition plan per ESRS E1-1] | [Contracted PPA new-build — full credit per SBTi; transition plan describes procurement strategy]. Cross-framework reconciliation per failure mode 7.6 prevention.
GWP basis Grid and residual factors are pre-aggregated CO₂e at the publisher’s GWP basis: AIB residuals inherit member-state publisher basis; EPA eGRID uses AR5/AR6 mixed by region; supplier and contract-specific factors carry the supplier’s stated GWP basis. Reporters reconciling against an internal AR6 baseline (CH₄ fossil = 29.8) note the basis distinction in the methodology statement.
Disclosure framework UK SECR for regulatory mode. CSRD ESRS E1 for EU mandatory dual disclosure with residual mix citation and transition plan. SBTi Corporate Net-Zero Standard for science-based target tracking with additionality screening for bundled instruments. CDP Climate Change C6.3.
Version history Methodology baseline at January 2015 (Scope 2 Guidance publication). 2023 ESRS E1 disclosure overlay. 2024 SBTi additionality position. 2026 GHG Protocol revision in consultation — implications pending. Per Table 9.1.
Dark green Pinterest pin titled METHODOLOGY · SCOPE 2 MARKET-BASED. Serif pull-quote: “Use the most specific instrument before falling back to the grid.” — GHG Protocol Scope 2 Guidance (paraphrased). A light card shows the four-tier supplier hierarchy: 1 energy contracts and PPAs, 2 certificates (REGO/REC/GO), 3 supplier-specific mix, 4 residual mix. Source bar: GHG Protocol Scope 2 · RE100 · DEFRA 2025.
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Frequently Asked Questions

This is the instrument equivalence problem of §2 in operational form. The arithmetic equivalence is real — at zero supplier or contract factor, both produce the same per-kWh inventory contribution. The disclosure equivalence is fictional. Three reasons it matters: (1) SBTi Corporate Net-Zero Standard target progress increasingly distinguishes bundled (limited credit) from contracted (full credit) under Position B — your inventory reduction may not equal your SBTi-credited reduction; (2) CSRD ESRS E1 transition plan narrative under Position C requires you to disclose your bundled-vs-contracted mix, and stakeholders read this; (3) audit risk profile differs — bundled REGOs from existing assets carry medium audit risk under reasonable assurance review, contracted new-build PPAs carry low audit risk. Reporters who don’t differentiate face stakeholder questions when their CDP and SBTi totals diverge — failure mode 7.6.

Tier 1 is the supplier’s matching at portfolio level; Tier 2 is the reporter’s matching at contract level. Practical case: you take supply from a UK utility on their “Green Origin” tariff. The utility sources REGOs across its portfolio, retires them to back the tariff, and publishes a tariff-specific factor in its annual disclosure (say 0.043 kg CO₂e/kWh as in Worked Example A). Your MB inventory uses that factor — Tier 1. Alternative case: you sign a 10-year virtual PPA with a specific solar developer for 50 GWh/year of contracted output and the associated EACs. You retire those EACs in your own registry account against your own consumption. Your MB inventory treats the matched portion at zero (or whatever the contract factor is) — Tier 2. The legal distinction: Tier 1 you bought a tariff product; Tier 2 you bought a contractual claim over named generation. The audit distinction: Tier 1 evidence is the supplier disclosure document; Tier 2 evidence is the contract plus the registry retirement statement under your account.

Conditionally yes within established cross-border frameworks; typically no outside them. The GHG Protocol Quality Criterion 4 requires geographic proximity of the EAC issuing body to the consumption it covers. Within the AIB framework (EU/EEA/UK), cross-border GO and REGO retirement is permitted with explicit disclosure of the issuing-body jurisdiction in the disclosure narrative — a French operation can retire German GOs, a UK operation can retire Norwegian REGOs, both with disclosure. Outside AIB, single-jurisdiction matching is the audit-grade default — retiring I-RECs from Brazil against EU operations triggers failure mode 7.3 (cross-border instrument mismatch) and is rejected at reasonable-assurance review. Within the US, REC tracking systems (WREGIS, PJM-EIS GATS, etc.) are NERC-subregion-aware; cross-subregion retirement is permitted with disclosure but increasingly scrutinised. Practical rule: match EAC sourcing to consumption jurisdiction within established cross-border frameworks; outside them, stay within jurisdiction.

The two co-exist on different layers. Your CDP C6.3 submission carries the inventory MB total computed under GHG Protocol Position A — bundled REGOs receive face-value treatment, the calculation is unchanged from prior years. Your SBTi target progress narrative — typically reported separately in your annual sustainability report or in CDP C4 — applies Position B: bundled instruments may not credit toward target progress without project-level additionality evidence. The correct disclosure pattern: report the inventory total once, consistently across CDP and CSRD; report the SBTi-credited fraction separately in the target progress narrative with explicit explanation of the additionality screening applied. A 50% inventory reduction may translate to a 20% SBTi-credited reduction if 60% of the reduction is bundled-instrument-driven. This is not an error — it is the deliberate operating model of Position B. Failure mode 7.6 surfaces when the two are not reconciled in the disclosure narrative; analysts compare and find a gap they cannot explain.

The residual mix is the emission factor for the portion of grid electricity not claimed by any contractual instrument — the grid average less the generation already retired via EACs by other reporters. It almost always exceeds the location-based factor in jurisdictions with material EAC retirement, because the renewable share of the grid has been contractually allocated to other reporters and what remains is dirtier than the grid average. The UK 2024 AIB residual mix is approximately 0.488 kg CO₂e/kWh — over 2.7× the LB grid factor of 0.131 kg CO₂e/kWh — because European EAC retirement volumes are large relative to the underlying grid. The structural detection signature in failure mode 7.1: when the corrected MB total exceeds the LB total, the cause is residual mix application, and that almost always traces to a sold-EAC scenario on a site that should have retained its instruments. Worked Example C demonstrates: corrected MB of 1,220.00 tCO₂e exceeds LB of 442.50 tCO₂e because residual (0.488) exceeds grid average (0.177). For the underlying mathematics, see the residual mix section in the electricity methodology.

Tier-specific. For Tier 1 supplier-specific: the supplier’s annual fuel-mix or emissions disclosure document for the reporting year, citing the specific tariff under which supply was taken, with cross-reference to the regulator filing where applicable (Ofgem Fuel Mix Disclosure for the UK, equivalent regulated disclosures in EU member states). For Tier 2 contract-specific: the executed contract or PPA term sheet identifying the generation asset, the contracted volume, and the EAC handling; plus the registry retirement statement under the reporter’s own account covering the reporting year specifically; for VPPAs, the financial settlement evidence plus the EAC delivery statement. For Tier 3 residual: the AIB European Residual Mixes publication citation or EPA eGRID residual mix table citation by vintage year matching the inventory year. For self-generation: registry retirement statements under the reporter’s own account showing all on-site-generated EACs were retained (not sold to third parties — the failure mode 7.1 check). For cross-framework reconciliation (failure mode 7.6): a single source-of-truth MB calculation document with framework-specific commentary appended for CDP, CSRD, and SBTi. Retention period per ISO 14064-1: minimum five years for most organisations.

You can claim the on-site generation as not-imported electricity — your Scope 2 boundary covers only purchased electricity, and self-generated kWh consumed on-site never enters Scope 2 in the first place. But you cannot also claim the renewable attribute as MB zero-emission once you have sold the REGOs. Per §3 contractual claim architecture, energy and attribute are severable. You retained the energy (used on-site) and you sold the attribute (REGOs went to the buyer). The buyer now has the renewable claim against your generation. Your remaining Scope 2 inventory is the grid-imported kWh, plus the on-site consumption must use residual mix factor (because no instruments are retained against it). Worked Example C demonstrates the failure mode 7.1 trap: the reporter tried to claim both on-site reduction and EAC sale revenue. The correct posture is binary — either retain all on-site EACs and claim zero-Scope-2 on the on-site consumption, or sell the EACs and apply residual mix to the on-site consumption. Mixing the two double-counts the renewable benefit between your inventory and the buyer’s inventory, and it is the highest-frequency MB failure auditors detect.

Position monitoring is the current posture — the revision is in consultation, not finalised. Restatement requirements depend on the final scope. Areas of likely revision include hourly carbon-free energy matching (a structural shift from annualised matching that would not necessarily restate prior years but would change forward methodology), residual mix governance (potentially requiring vintage clarifications), and Quality Criteria refinement (potentially affecting bundled-instrument acceptability). The 2015 publication is the analogue — that release required restatement only for trend baselines extending pre-2015 (Table 9.1, restatement column). The 2023 ESRS E1 release required additional disclosure prospectively but not restatement. The 2024 SBTi position required no restatement (target progress only). Reporters with active SBTi targets should monitor the consultation outcome closely; reporters with stable post-2015 baselines are unlikely to face restatement requirements. The changelog will track the revision through publication.

Calculator

Apply the four-tier supplier hierarchy with audit-grade output, dual-method (LB + MB) display under the §6.3 invariant, multi-site portfolio mode with per-site tier breakdown, EAC instrument tagging across REGO / GO / REC / I-REC / PPA, residual mix application with audit warnings on T-0 fallback, and JSON + CSV export with full provenance: Open the Scope 2 Electricity Calculator →

Scope 2 market-based methodology — anchor reference factors (MasterBrain v2025.6, verified 2026-05-10): United Kingdom LB 0.131 kg CO₂e/kWh (DEFRA 2025), AIB UK residual mix ≈ 0.488 kg CO₂e/kWh (hardcoded 2024 vintage, pending [gc_residual_mix] shortcode migration). United States national LB 0.350 (EPA eGRID 2023), residual mix per NERC subregion via EPA eGRID residual tables. Germany LB 0.330, France 0.041, Spain 0.154, Netherlands 0.254 (Ember Yearly Electricity 2025); AIB residuals per member state. Tier 4 LB fallback uses these sovereign factors directly. T-0 untraced premium fallback at grid × 1.15 for jurisdictions without published residual.

Method: GHG Protocol Corporate Standard + Scope 2 Guidance (2015 amendment) — dual reporting per §6.3, seven Quality Criteria per §6.10, four-tier supplier hierarchy applied per kWh of consumption. Companion Scope 2 Electricity Methodology covers the full inventory workflow including LB-only cases and the Scope 3 Cat 3 T&D companion.

Reviewed: May 2026 by Jeremiah Say. Refreshed within 30 days of each AIB residual mix release, EPA eGRID release, DEFRA release, and any GHG Protocol / SBTi position update. The 2026 GHG Protocol Corporate Standard revision is in consultation; this page will be re-versioned within 14 days of publication if methodology changes are finalised.

Corrections: Spotted an error? Email jeremiah@greencalculus.com — corrections welcomed and contributors credited in the public changelog.

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