Scope 2 Electricity Emissions: Methodology and Grid Emission Factors
Step-by-step method for converting metered electricity consumption into a defensible Scope 2 inventory under the GHG Protocol Corporate Standard with mandatory dual reporting (location-based + market-based per Scope 2 §7.1), a 50-jurisdiction grid-factor reference table backed by live MasterBrain shortcodes, an EAC instrument decision matrix covering REGOs, GOs, RECs, I-RECs and PPAs, residual mix treatment using the AIB European and national residual mixes, the Scope 3 Cat 3 T&D companion calculation, and a forward-looking section on hourly carbon-free energy. Aligned to the GHG Protocol Corporate Standard, GHG Protocol Scope 2 Guidance (2015), UK DEFRA 2026, EPA eGRID 2023 and the AIB 2025 European Residual Mixes.
A methodology page is the execution layer — it takes the boundary definitions from the glossary, the certificate definitions from the EAC reference, and the raw factor dataset from the data layer, and tells you exactly how to translate metered electricity consumption into a defensible Scope 2 inventory. Unlike Scope 1 (where variant misselection dominates), Scope 2’s primary editorial challenge is the dual-method requirement — every reporter holding contractual instruments must publish two parallel inventory totals, and the most common production failure is a market-based “zero” that is not the same kind of zero across frameworks (a bundled REGO is not a contracted PPA, and SBTi V2.0 treats older generators differently). Jump to the decision tree, the 50-jurisdiction factor table, or open the Scope 2 Electricity Calculator.
⚠ Stale-factor risk — UK reporters using DEFRA 2025 in 2026
The UK grid emission factor moved from 0.177 (DEFRA 2025) to 0.131 (DEFRA 2026) — a −26% step change in a single annual release. Part of that is a cleaner grid and part is a change of method: DEFRA’s 2026 methodology paper (paragraphs 3.4 to 3.8) moved the factor onto the more recent Energy Trends statistics, so the 2026 release uses 2025 data where the 2025 release used 2023 data, and 2024 is skipped. DEFRA advises users to decide whether to restate previous years for a consistent time series. Any UK reporter who carried the DEFRA 2025 factor into a 2026 disclosure overstates location-based Scope 2 by about +35% at constant consumption. This methodology uses live MasterBrain shortcodes for grid factor references in the prose and the reference table, so they update with each DEFRA release; the worked examples below are fixed audit-record snapshots, dated in their introduction.
Why Scope 2 Is Structurally Different from Scope 1
Scope 1 is a closed system. Fuel goes in, combustion happens inside the inventory boundary, CO₂ comes out. The reporter owns the meter, the fuel, the asset, and the emission. The factor library is a published lookup against a small set of fuel chemistries. The accounting question is “did you pick the right factor for the right fuel” — most production failures live in variant-selection error, not in any structural ambiguity about the inventory itself.
Scope 2 inverts almost every one of those properties. Electricity arrives at the meter from a grid the reporter does not own, generated by a portfolio of assets the reporter does not control, with a per-kWh emission profile that varies by hour, by season, and by year. The reporter does not own the emission — they own the consumption, and the GHG Protocol Scope 2 Guidance (2015 amendment to the Corporate Standard) defines two parallel methodologies for converting that consumption into a reportable inventory:
- Location-based (LB) — the reporter’s electricity consumption is multiplied by the average emission intensity of the grid that physically delivered it. The factor is published by a national or regional grid authority (DEFRA for the UK, EPA eGRID for the US, and national inventory agencies such as ADEME in France and ECCC in Canada). The accounting question reduces to a single look-up plus a multiplication.
- Market-based (MB) — the reporter’s electricity consumption is multiplied by the emission profile they have contracted for, recognised through energy attribute certificates (REGOs, GOs, RECs, I-RECs), power purchase agreements (PPAs), or supplier-specific tariff disclosures. The portion of consumption not covered by any qualifying contract uses a “residual mix” factor — the average intensity of the grid after removing the generation already claimed by other reporters’ instruments.
The two methods produce different numbers for any reporter holding renewable instruments. The Scope 2 Guidance §7.1 requires that both numbers be disclosed when market-based instruments are held — neither suppresses the other, and “we report market-based only” is non-compliant. This dual-reporting invariant is the defining structural feature of Scope 2 accounting and is enforced in every audit-grade calculation engine, including our own.
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Regulatory Matrix — What Each Framework Requires
Before choosing a method, confirm what each framework you report to actually requires. The five most common Scope 2 disclosure regimes diverge in subtle but material ways, particularly on whether market-based is acceptable as a sole disclosure (it almost never is) and on the GWP basis expected for any per-gas reconstruction (rare for Scope 2 — grid factors are pre-aggregated CO₂e at the publisher’s basis, but the basis still must be disclosed).
| Framework | LB required | MB required | Dual disclosure | EAC quality scrutiny |
|---|---|---|---|---|
| UK SECR | Yes (minimum) | If held | Required when MB instruments are held; LB alone sufficient if none | Light — REGOs accepted at issued face value |
| EU CSRD / ESRS E1 | Yes | Yes if instruments held | Mandatory dual disclosure with explicit residual mix factor citation | Medium — supplier disclosure required, additionality discussion in transition plan |
| CDP Climate Change | Yes (C6.3) | Yes (C6.3) | Both fields required in the C6.3 table; LB and MB carry forward to score | Medium — instrument type asked; bundled vs unbundled distinguished |
| SBTi Corporate Net-Zero | Either (one method) | Either (one method) | One method for base year and progress (V1.3.1 C9) | Rising — V2.0 adds generator age and deliverability limits |
| Singapore NEA | Yes (carbon tax basis) | Limited recognition | LB used for carbon-tax determination; MB voluntary disclosure | N/A — facility-level S1+S2 LB reporting under CCT Act |
Three patterns emerge. First, location-based is required by every framework — even the most market-friendly regime never lets the reporter delete it. Second, market-based scrutiny is rising — a Scope 2 zero from bundled REGOs purchased on the secondary market meets SBTi V1.3.1, but V2.0 limits instruments by generator age and deliverability from February 2027. Third, regulatory disclosure and target-tracking diverge: under V2.0 a REGO from an older generator can satisfy CDP and CSRD compliance yet not support a science-based target. The methodology choice cascades from these distinctions.
Decision tree — which method for which framework
Five questions, in order. Stop at the first answer that matches your context. Re-run the tree per reporting framework — a UK SECR-only reporter takes a different path than the same organisation’s parallel CSRD submission.
Yes — at least one instrument is held. Continue to question 2.
EU CSRD / ESRS E1: Dual mandatory — both methods, explicit residual mix factor citation per ESRS E1-6.
CDP: Dual mandatory — table C6.3 requires both fields populated.
SBTi target tracking: One stated method — report both per the GHG Protocol, track the target on one; see question 4.
No — single-jurisdiction shortcut — but the invariant still applies if any sub-site carries instruments.
Contracted PPA (physical or virtual) for new-build generation — counts in the MB total and fits both SBTi versions, provided the V2.0 deliverability rule is met.
Self-generated on-site renewables — see §9 self-generation.
No — voluntary for organisations not subject to GHG Protocol Scope 3 Standard or CSRD; disclose anyway for inventory completeness.
Two methods, one inventory — the dual-reporting invariant
When market-based instruments are held, both totals must appear in the disclosure. The location-based total is never suppressible — it is the answer to “what would your Scope 2 footprint be without any contractual claims” and serves as the anchor against which market-based progress is measured. An SBTi target uses one stated method for base year and progress; CDP asks for both; CSRD ESRS E1 mandates both with explicit factor citation.
Grid average · always required
Multiply consumption by the published average grid emission factor for the jurisdiction supplying the meter. UK: 0.131 (DEFRA 2026). US national: 0.350 (EPA eGRID 2023). Most other jurisdictions publish no national location-based factor at all — the table below shows that absence rather than filling it. The 50-jurisdiction reference table below shows which jurisdictions have one.
Contractual · required when instruments held
Matched portion (kWh covered by qualifying instruments) × supplier-specific or instrument-implied factor. Unmatched portion × residual mix factor for the jurisdiction (where published) or grid average × untraced premium where not. A market-based zero is not the same kind of zero across instrument classes — see §5 EAC decision matrix.
Residual Mix — The Most-Skipped Section in Scope 2 Reporting
Residual mix is the emission factor for the portion of grid electricity not claimed by any contractual instrument. Conceptually: take the published grid average, subtract the generation associated with all the renewable EACs already retired by other reporters, and what remains is dirtier than the grid average — because the renewables have been “claimed”. A reporter with 50% EAC coverage who uses the published grid average for the unmatched 50% double-counts the renewable generation on their unmatched portion. The residual mix corrects this.
The mathematics of why residual mix exceeds grid average: in any jurisdiction with significant renewable generation, the published grid factor is the volume-weighted average across the full generation portfolio (renewable + fossil + nuclear). When any reporter retires a REGO/GO/REC for, say, 1 MWh of wind generation, that 1 MWh of zero-emission generation is now “owned” by them. For everyone else on the grid still using the grid-average factor, that wind MWh has effectively been removed from their share — the residual generation pool is dirtier. The residual mix factor reconstructs this dirtier pool as a published number.
Three jurisdictions to know:
- AIB European Residual Mixes — published annually by the Association of Issuing Bodies, covering the EU-27 plus UK, Norway, Switzerland, Iceland. The 2025 publication (published 28 May 2026, covering calendar year 2025) ranges from 0.01711 kg CO₂/kWh [GreenCalculus grid.fra.electricity.residual_mix · AIB 2025 'CO2'!C14 (FR) · v2026.284] in France to 0.70147 [GreenCalculus grid.deu.electricity.residual_mix · AIB 2025 'CO2'!C9 (DE)] in Germany and 0.72696 [GreenCalculus grid.pol.electricity.residual_mix · AIB 2025 'CO2'!C29 (PL)] in Poland — usually well above the grid average, because European EAC retirement volumes are substantial. The UK residual mix is 0.28064 kg CO₂/kWh [GreenCalculus grid.gbr.electricity.residual_mix · AIB 2025 'CO2'!C15 (GB)] — about 2× the LB grid factor of
0.131kg CO₂e/kWh. AIB residual mixes are direct CO₂ only. - United States — EPA eGRID does not publish a residual mix. The usual US source is the Green-e Residual Mix published each year by the Center for Resource Solutions. eGRID’s “non-baseload” rates are a different tool, used for marginal-emission analysis, not as a Scope 2 residual.
- Elsewhere — a few national schemes publish one (Australia’s National Greenhouse Accounts give a national residual mix factor of 0.79 kg CO₂e/kWh) [GreenCalculus grid.aus.electricity.residual_mix · DCCEEW NGA 2026], but most jurisdictions have none. Industry practice is to use the location-based grid factor as a residual proxy with explicit audit flag, or apply a conservative untraced premium (typically 1.10× to 1.20× the grid factor). The Scope 2 Electricity Calculator reads the AIB or national residual mix where one is published and applies a 1.15× factor only where none is, with an audit warning saying so.
MasterBrain carries the AIB 2025 residual mixes for 31 European countries and Australia’s national residual mix factor, keyed grid.<country>.electricity.residual_mix. Since 5 October 2026 the Scope 2 calculator reads them for the unmatched portion of a market-based result; before that it approximated every residual mix as grid × 1.15. Where no residual mix is published the 1.15× approximation remains, flagged in the audit trail.
EAC Decision Matrix — REGOs, GOs, RECs, I-RECs, PPAs
The table below is the production reference for which energy attribute certificates count as what under which framework. Six rows cover the dominant instrument types globally; the columns capture framework recognition, the GHG Protocol Quality Criteria position, additionality, residual mix treatment, and audit risk.
| Instrument | Region | Framework recognition | Additionality | Residual treatment | Audit risk |
|---|---|---|---|---|---|
| REGO UK |
United Kingdom (Ofgem) | UK SECR ✓ · CDP ✓ · CSRD ✓ · SBTi V1.3.1 ✓ · V2.0 if under 15 years | Low — bundled REGOs from existing assets | Unmatched portion uses the AIB UK residual mix (0.28064 kg CO₂/kWh) | Medium — older generators fall outside SBTi V2.0 |
| GO EU/EEA |
European Union + EEA (national issuing bodies under AIB) | CSRD ESRS E1 ✓ · CDP ✓ · SBTi V1.3.1 ✓ · V2.0 if under 15 years | Low — same as REGOs; bundled GOs from existing hydro/nuclear common | AIB residual mix per member state | Medium — bundled hydro GOs from Scandinavia particularly scrutinised |
| REC US |
United States (state-level + voluntary markets) | CDP ✓ · GHG Protocol Scope 2 ✓ · SBTi V1.3.1 ✓ · V2.0 if under 15 years | Variable — voluntary RECs typically less additional than compliance RECs | Green-e residual mix (Center for Resource Solutions); eGRID publishes none | Medium — green-e certification raises bar; non-green-e RECs scrutinised |
| I-REC Rest of world |
Asia, Africa, Latin America (I-REC Standard Foundation) | CDP ✓ · GHG Protocol Scope 2 ✓ · SBTi V1.3.1 ✓ · V2.0 if under 15 years | Variable — depends on grid maturity and EAC market depth in jurisdiction | No published residual mix in most I-REC jurisdictions; grid average × untraced premium used | High — emerging-market markets carry higher provenance risk |
| PPA bundled Global |
Direct contract for energy + EACs from a specific project | All frameworks ✓ | High when contracted for new-build generation; medium for existing assets | Per-PPA disclosed factor for matched portion | Low — direct contract trail to specific project |
| PPA unbundled / VPPA Global |
Virtual PPA — financial contract for difference, EACs delivered without physical energy | CDP ✓ · CSRD ✓ · SBTi ✓ | High when new-build; SBTi V2.0 lists virtual PPAs as eligible | Same project-level treatment as bundled PPA | Low — well-documented contractual trail |
The structural pattern: bundled REGO/GO/REC has the lowest cost per MWh and the lowest additionality; contracted PPAs have the highest cost and the highest additionality. SBTi V2.0 separates these by generator age and deliverability from February 2027 — what counts toward CDP scoring or CSRD compliance may not support a V2.0 target. The methodology consequence: a Scope 2 zero achieved through bundled REGOs is a different disclosure from a Scope 2 zero achieved through a contracted VPPA, even though the calculation arithmetic is identical. Reporters should make the instrument basis visible in their disclosure narrative.
The Calculation — Step by Step
The two methods share an identical mathematical structure but apply different factors to different portions of the consumption.
Two subtleties matter at audit. First, when an EAC instrument is held but no supplier factor is disclosed, the matched portion is treated as zero-emission per REGO/GO/REC convention — that is the entire point of the instrument. Second, EFresidual ≠ EFgrid in any jurisdiction with material EAC retirement; using the grid average for the unmatched portion double-counts the renewable generation already claimed by other reporters and is a methodological error specifically called out in CSRD ESRS E1-6.
Country and Subregion Factor Reference — 40 Countries + 10 US eGRID Subregions
Rendered live via the [gc_grid] shortcode, so every cell auto-updates on the next annual release without manual edits to this page. The two value columns are different instruments and are not interchangeable.
Scope 2 is a location-based grid-average factor fit for a GHG Protocol Scope 2 inventory. It is published only where a national body provides one: DEFRA 2026 (UK), ADEME (France), CBS (Netherlands), ECCC (Canada), DCCEEW NGA (Australia), and EPA eGRID 2023 (US national and subregions). Where no such factor exists the cell is empty, and that absence is deliberate — we do not fill it with a figure measured on a different boundary. Most of these are gross-generation basis; Canada is the exception, published on a consumption basis and so not directly comparable with the rest of the column.
Lifecycle is Ember’s full-lifecycle, all-gas intensity — fuel supply chain, plant construction and combustion, on a net-generation basis. It covers 212 countries, which is why it fills rows the Scope 2 column cannot. It is not a Scope 2 factor and must not be reported as one: for the UK it reads 0.217 against DEFRA’s 0.131, and for Canada 0.191 against ECCC’s 0.111. Ember publishes no subregional series, so the ten US eGRID rows are empty in that column. T&D losses are not pre-baked in either column; treat them as a Scope 3 Cat 3 companion per §7.
| Jurisdiction | Scope 2 (kg CO₂e/kWh) | Lifecycle (kg CO₂e/kWh) | Source | Year | Note |
|---|---|---|---|---|---|
| Europe | |||||
| Norway | — | 0.028 | — | — | ~99% hydropower — lowest in MasterBrain |
| Sweden | — | 0.035 | — | — | Hydro + nuclear |
| Switzerland | — | 0.039 | — | — | Hydro + nuclear |
| France | 0.035 | 0.041 | ADEME_BASE_CARBONE_2026 | — | Low — ~70% nuclear |
| Austria | — | 0.117 | — | — | — |
| Finland | — | 0.057 | — | — | — |
| Denmark | — | 0.100 | — | — | — |
| Portugal | — | 0.128 | — | — | — |
| Belgium | — | 0.109 | — | — | — |
| Spain | — | 0.154 | — | — | — |
| United Kingdom | 0.131 | 0.217 | DEFRA_2026 | 2025 | DEFRA 2025. -15% vs 2024. Cleaner grid mix. |
| Netherlands | 0.200 | 0.254 | CBS_ELEKTRICITEIT_2024 | — | — |
| Ireland | — | 0.256 | — | — | — |
| Italy | — | 0.285 | — | — | — |
| Germany | — | 0.330 | — | — | — |
| Poland | — | 0.591 | — | — | Coal-heavy mix |
| North America | |||||
| Canada (national avg) | 0.111 | 0.191 | ECCC_NIR_2026 | — | — |
| United States (national avg) | 0.350 | 0.384 | EPA_EGRID_2023 | 2024 | EPA eGRID 2024. Use regional subgrid for accuracy. |
| Mexico | — | 0.474 | — | — | — |
| United States — eGRID2023 subregions (use these in preference to the national average for higher precision) | |||||
| United States — NYUP (NPCC Upstate NY) | 0.110 | — | EPA_EGRID_2023 | 2024 | Hydro 31% + nuclear 31%. Lowest US subregion. Continental US. — lowest US subregion |
| United States — CAMX (WECC California) | 0.195 | — | EPA_EGRID_2023 | 2024 | Gas 46% + solar 20%. Most of California — declining as solar scales. |
| United States — NEWE (NPCC New England) | 0.246 | — | EPA_EGRID_2023 | 2024 | Gas 53% + nuclear 26%. Six-state ISO-NE footprint. |
| United States — NWPP (WECC Northwest) | 0.288 | — | EPA_EGRID_2023 | 2024 | Hydro 44% + gas 19% + coal 18%. Pacific Northwest. |
| United States — RFCE (RFC East) | 0.272 | — | EPA_EGRID_2023 | 2024 | Gas 50% + nuclear 36%. Mid-Atlantic — PJM East. |
| United States — ERCT (ERCOT All) | 0.334 | — | EPA_EGRID_2023 | 2024 | Gas 47% + wind 23% + coal 16%. Most of Texas. |
| United States — AZNM (WECC Southwest) | 0.320 | — | EPA_EGRID_2023 | 2024 | Gas 44% + nuclear 19% + coal 16%. Arizona/New Mexico. |
| United States — FRCC (Florida) | 0.356 | — | EPA_EGRID_2023 | 2024 | Gas 74% + nuclear 12%. Most of Florida. |
| United States — RFCW (RFC West) | 0.416 | — | EPA_EGRID_2023 | 2024 | Gas 32% + coal 31% + nuclear 28%. Ohio Valley — PJM West. |
| United States — SRMW (SERC Midwest) | 0.566 | — | EPA_EGRID_2023 | 2024 | Coal 59% + nuclear 15%. Highest of the ten subregions in this set. — highest of the ten subregions |
| Asia-Pacific | |||||
| New Zealand | — | 0.093 | — | — | Geothermal + hydro |
| Singapore | — | 0.497 | — | — | — |
| South Korea | — | 0.417 | — | — | — |
| Japan | — | 0.477 | — | — | — |
| Thailand | — | 0.546 | — | — | — |
| Taiwan | — | 0.634 | — | — | — |
| Vietnam | — | 0.463 | — | — | — |
| Australia (national avg) | 0.590 | 0.525 | DCCEEW_NGA_2026 | — | — |
| China | — | 0.526 | — | — | Declining as solar/wind scales |
| Malaysia | — | 0.603 | — | — | — |
| Philippines | — | 0.595 | — | — | — |
| India | — | 0.671 | — | — | — |
| Indonesia | — | 0.681 | — | — | — |
| Middle East | |||||
| UAE | — | 0.468 | — | — | — |
| Saudi Arabia | — | 0.692 | — | — | — |
| Africa | |||||
| Egypt | — | 0.563 | — | — | — |
| Nigeria | — | 0.456 | — | — | — |
| South Africa | — | 0.699 | — | — | Coal-dominant — among highest globally — highest in MasterBrain |
| Latin America | |||||
| Brazil | — | 0.110 | — | — | Hydro dominant |
| Chile | — | 0.291 | — | — | — |
| Argentina | — | 0.343 | — | — | — |
The structural span, measured on lifecycle intensity because it is the only series covering every jurisdiction: from 0.028 kg CO₂e/kWh in Norway (~99% hydropower) to 0.699 in South Africa (coal-dominant) — over a 25× range across the MasterBrain set. Within the United States, the eGRID2023 subregion span is narrower but still material: 0.110 (Upstate NY hydro+nuclear) versus 0.566 (SERC Midwest, coal 59%) — a 5× spread that swamps the precision improvement from any other methodology choice. Always use the eGRID subregion factor in preference to the national average for US sites with subregion-traceable supply — the geography is doing more work than the methodology in any US Scope 2 inventory.
Scope 3 Cat 3 T&D Losses — The Companion Calculation
Approximately 5–10% of every kWh generated is lost between the power station and the meter — heat dissipation in transmission lines, transformer losses, distribution-network resistance. Those losses are physical generation that the reporter caused but does not consume, and the GHG Protocol Scope 3 Standard Category 3 (Fuel- and Energy-Related Activities, “FERA”) allocates them to the buyer as a separate inventory line. The Scope 3 Cat 3 T&D companion is mandatory under the Scope 3 Standard, increasingly expected under CSRD ESRS E1 value-chain disclosure, and routinely required by CDP for full points. The full country-by-country loss factors, the two arithmetic shapes, and the audit checklist are documented in our T&D losses methodology, with the 40-country implementation available in the T&D Losses Calculator.
Two methodology fixed points. First, T&D companion is computed against the location-based grid factor only — physical losses occur on the grid regardless of contractual instruments held. A reporter with 100% PPA coverage still has T&D losses on the physical grid, and they still belong in Scope 3 Cat 3. Second, the loss-percentage-to-factor conversion uses the “delivered kWh” denominator: per kWh consumed at the meter, the upstream grid generated kWh ÷ (1 − loss%) — and the loss is the difference. The (1 − loss%) denominator is the small-but-easy mistake that converts a 5% loss into a 5% headline rather than the correct ~5.3%.
For a US reporter consuming 2,500,000 kWh at the eGRID 2023 national average: T&D factor = 0.34967 × 0.05116 / 0.94884 = 0.01885 kg CO₂e/kWh; T&D companion = 2,500,000 × 0.01885 = 47,125 kg = 47.13 tCO₂e, or 5.4% of the LB Scope 2 total (874.17 tCO₂e). A UK reporter skips the formula: DEFRA 2026 publishes the T&D factor as 0.01299 kg CO₂e/kWh [GreenCalculus transmission_distribution.gbr.electricity · DEFRA 2026 'Transmission and distribution'!E22], about 10% of the grid factor. For most reporters T&D sits in the 5–10% range relative to LB Scope 2 — material enough that omission is visible to any audit reviewer doing a back-of-envelope check.
Worked Examples — Cross-Verified to the Calculator
Three audit-record snapshots at this page’s review date (5 October 2026), computed with calculator engine v1.1.1 on MasterBrain v2026.221 (DEFRA 2026, ADEME 2026, EPA eGRID 2023, AIB 2025). Fixed values throughout. To replicate any example, open the Scope 2 Electricity Calculator and enter the inputs documented in each example header; the results match while those source editions are current.
Reporting year: 2026 | Reporting framework: UK SECR only
Site: London headquarters, single half-hourly meter
Annual consumption: 2,500,000 kWh
Contractual instruments held: None — supplier default tariff, no REGOs, no PPA
Method: Location-based only (compliant — no instruments to drive MB)
T&D companion: Computed for inventory completeness The simplest case. No EAC inputs, no residual mix question, no additionality screening. SECR-compliant single-method disclosure.
LB only. Decision tree question 5: T&D companion required for inventory completeness. The result is a single LB calculation plus a Scope 3 Cat 3 companion line. Both totals appear in the disclosure.
Reporting year: 2026 | Reporting framework: UK SECR + CDP + SBTi tracking
Annual consumption: 2,500,000 kWh (unchanged)
Contractual instruments held: 100% bundled REGOs — purchased on secondary market through energy supplier, retired against 2026 consumption
Supplier-disclosed factor: Not disclosed — REGOs claimed at zero-emission convention
Method: Dual — LB + MB (per Scope 2 §7.1 invariant) The most common production scenario for UK reporters claiming a “renewable” tariff. Demonstrates the Scope 2 §7.1 dual-reporting invariant — LB never disappears.
Reporting year: 2026 | Reporting framework: EU CSRD / ESRS E1 + CDP
Site 1 — London office (UK): 1,800,000 kWh · 50% bundled REGOs from existing wind · supplier factor not disclosed (zero convention)
Site 2 — Lyon R&D centre (France): 1,200,000 kWh · No instruments held · LB only
Site 3 — Texas manufacturing (US): 800,000 kWh · 100% from a new-build solar PPA with bundled RECs · supplier factor 0.0 Multi-jurisdictional portfolio with three different instrument states. Demonstrates the Scope 2 §7.1 invariant at portfolio level: when any site uses MB, all sites contribute their figure to the portfolio MB total — sites without MB inputs carry their LB figure as the conservative default per the calculator engine §8.
0.28064 kg CO₂/kWh, read by the calculator.
| Site | Country | kWh | Method | EAC % | LB tCO₂e | MB tCO₂e |
|---|---|---|---|---|---|---|
| London | UK | 1,800,000 | LB+MB | 50% REGO | 1,800,000 × 0.13096 = 235.73 | (900,000 × 0.0) + (900,000 × 0.28064) = 252.58 |
| Lyon | France | 1,200,000 | LB only | 0% | 1,200,000 × 0.035 = 42.00 | 42.00 (LB carried to portfolio per §7.1) |
| Texas | US | 800,000 | LB+MB | 100% PPA | 800,000 × 0.34967 = 279.73 | (800,000 × 0.0) + (0 × residual) = 0.00 |
| Portfolio totals | 3,800,000 | — | — | 557.46 tCO₂e | 294.58 tCO₂e | |
Self-Generated Renewables — When Does It Reduce Scope 2?
On-site solar PV, on-site wind, and on-site CHP that generates electricity raise a Scope 2 boundary question: when does self-generated electricity reduce Scope 2, and when does it require an EAC retirement to claim the reduction?
The GHG Protocol position (Scope 2 Guidance §7.5 plus the Corporate Standard’s general control rules):
- Self-generated electricity consumed on-site, retained by the generator — never enters Scope 2 in the first place. There is no purchase, no grid import, no inventory line. The reporter does not need to retire EACs against this consumption because there is nothing to “match” — they directly own and consume the generation.
- Self-generated electricity exported to the grid — sold; the buyer’s EAC retirement (or the residual mix consequence) determines whose inventory it appears in. The seller does not get to keep the EAC and the export simultaneously; if EACs are sold along with the energy, they are no longer the seller’s to claim.
- Self-generated electricity consumed on-site with EACs sold separately to a third party — this is the trap. If the reporter has sold the EACs (REGOs/GOs) issued against their on-site generation to another organisation, that other organisation has the renewable claim. The original generator must use the residual mix factor for their on-site consumption, not zero — they kept the energy but not the attribute.
- Self-generated CHP electricity — the electricity portion is treated as above; the heat portion is Scope 1 (combustion of the input fuel) and the methodology overlaps with the natural gas combustion methodology for the fuel input.
The audit question for any organisation claiming Scope 2 reduction from on-site renewables: “did you retain the EACs?” If yes, the on-site consumption is genuinely zero-Scope-2. If no, the on-site consumption uses the residual mix and the reporter has a sold-EAC accounting line elsewhere. Mixing the two — claiming both the on-site reduction and the EAC sale revenue — is a double-count flagged by every reasonable-assurance audit.
Forward-Looking — Hourly Carbon-Free Energy and Granular Certificates
The current Scope 2 methodology operates on annualised matching: a reporter consuming 2.5 GWh in a year and retiring 2.5 GWh of REGOs declares 100% MB coverage even when their actual hourly consumption profile does not match the hourly generation profile of the wind farm whose REGOs they retired. The 100% annual match might in reality reflect a wind farm that overproduces at night when the office is closed and underproduces on still summer afternoons when the office is at peak demand — a structural mismatch that annualised matching cannot see.
Hourly carbon-free energy (CFE) accounting, sometimes called 24/7 CFE, refines this. Instead of matching annual MWh totals, the reporter matches each hour’s consumption against each hour’s generation — and the “match score” is the fraction of hours where renewable generation covered consumption. Google’s published 24/7 CFE methodology, the EnergyTag Standard (released 2022, updated since), and emerging EU Granular Guarantees of Origin frameworks are the production references.
Two reasons to track this even if your current disclosure does not require it:
- SBTi V2.0. V2.0 does not require hourly matching, but Category A companies must report their hourly-matched share in activity pools using 10 GWh or more a year, and an optional recognition programme is planned. A reporter with strong hourly metrics has a stronger story than one with annualised metrics alone.
- EU regulatory pipeline. The European Commission’s 2023 proposal for granular Guarantees of Origin would create an hourly-resolution EAC market across the EU-27, retiring against hourly consumption profiles. The proposal is not yet binding regulation but reporters with European footprint are already preparing for it; a 2026 inventory built on annualised assumptions may face adjustment when the granular regime is enacted.
The methodology consequence today: hourly matching is not yet shortcoded into the MasterBrain or the calculator (no [gc_cfe_match] shortcode exists; flagged for future migration). For organisations with material PPA coverage and an interest in 24/7 CFE, the practical path is to compute hourly match externally (typically using meter-data-aggregator hourly profiles plus PPA generation telemetry) and disclose the match score alongside the annualised MB total. The annualised MB remains the headline disclosure under current frameworks; the hourly score is the forward-looking complement.
Standards Alignment
Six standards govern Scope 2 electricity accounting. Each layer supplies a different input to the same audit-grade output.
| Standard | Role for Scope 2 reporting |
|---|---|
| GHG Protocol Corporate Standard + Scope 2 Guidance (2015) | Defines Scope 2 boundary (purchased electricity), the dual-method requirement (§7.1), the Quality Criteria for market-based instruments (Table 7.1), and the residual mix logic. The methodological foundation. |
| UK DEFRA 2026 | UK grid factor: 0.131 kg CO₂e/kWh. Source for UK SECR. |
| Ember Yearly Electricity 2025 (lifecycle) | Lifecycle carbon intensity for 212 countries, shown in the reference table for context. Not a Scope 2 factor: MasterBrain withdrew it from the location-based key on 19 August 2026. |
| EPA eGRID 2023 | US national average factor (0.350) plus the 10 eGRID2023 subregions. Use subregion in preference to national for any US site with subregion-traceable supply. |
| GHG Protocol Scope 3 Standard | Defines Cat 3 (FERA) — home for the T&D losses companion line. Mandatory for organisations under Scope 3 Standard scope. |
| CSRD / ESRS E1 | EU mandatory disclosure requiring full dual Scope 2 (LB + MB), explicit residual mix factor citation in MB disclosure, value-chain T&D disclosure under E1-6, and transition-plan integration of EAC procurement strategy. |
| SBTi Corporate Net-Zero Standard | Sets the single-method rule for Scope 2 targets (V1.3.1 C9) and, in V2.0, generator age and deliverability limits on instruments. |
What the Calculator Handles vs What You Decide
The Scope 2 Electricity Calculator automates the mechanical steps. This methodology page covers the upstream decisions the calculator cannot make for you.
- Published location-based grid factors for six countries (UK, US, France, Netherlands, Canada, Australia) and all 27 US eGRID subregions; custom factor for any other
- Dual-method calculation (LB + MB) with the §7.1 invariant enforced — LB is never suppressible
- Per-site EAC matching with REGO / GO / REC / I-REC / PPA instrument tagging
- Residual mix factor application to unmatched portion (with audit warning where untraced premium fallback applies)
- Multi-site portfolio mode with up to 5 sites; per-site breakdown table; portfolio totals carrying the §7.1 invariant
- Scope 3 Cat 3 T&D companion calculation against LB factor only (regional loss percentages applied)
- Custom grid factor input for jurisdictions not in the MasterBrain set
- Annualisation toggle for partial-year inputs; reporting period selector (annual / quarterly / monthly / custom)
- Audit mode with full calculation chain, hash for replay, JSON + CSV export with full provenance
- Method selection — LB only vs LB+MB; cascade from instrument holding and reporting framework per decision tree
- Jurisdiction selection — sovereign nation vs US subregion (use subregion for US sites with subregion-traceable supply)
- EAC instrument type and additionality — bundled REGO/GO/REC vs contracted PPA; SBTi V2.0 limits per §5
- Supplier-disclosed factor — disclosed numeric vs zero-emission convention; document source in audit trail
- Residual mix — calculator reads the AIB or national residual mix where published (32 countries); grid × 1.15 elsewhere, flagged
- T&D companion inclusion — required under Scope 3 Standard and CSRD ESRS E1; voluntary otherwise but recommended
- Multi-site aggregation rules — single legal entity vs operationally controlled sites; document the consolidation approach (financial vs operational control) per GHG Protocol §3
- Reporting framework cascade — UK SECR vs CSRD vs CDP vs SBTi target tracking; each may require subtly different supplementary commentary
- Source documentation — utility bills, EAC retirement statements, PPA contracts, supplier annual disclosure for audit retention
Ready to compute? Open the Scope 2 Electricity Calculator →
Audit Checklist — Scope 2 Reasonable-Assurance Pre-Flight
Eight items, in order. Run this list before submitting any Scope 2 disclosure for reasonable-assurance review under ISO 14064-1 or equivalent. Each item maps to a specific failure mode that auditors look for first.
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01
Grid factor freshness. Confirm the grid factor used is the most recently published version for the inventory year being reported. UK reporters: DEFRA publishes annually in June — a 2026 inventory should use DEFRA 2026 (published June 2026). Stale-factor risk is high — see Example A’s 35% sensitivity. The MasterBrain grid registry timestamps every factor with its source publication; replicate that traceability in your own audit trail.
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02
Dual-method completeness (Scope 2 §7.1). If any contractual instruments are held — even one bundled REGO — both LB and MB totals must appear in the disclosure. Suppressing LB on the basis that “we report market-based” is non-compliant. Verify the disclosure pair is intact.
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03
Residual mix factor citation. For any MB calculation with less than 100% EAC coverage, the residual mix factor used on the unmatched portion must be disclosed with provenance. AIB-published value, national residual mix (e.g. Green-e in the US, NGA in Australia), or untraced-premium approximation — name the source. CSRD ESRS E1-6 specifically requires this.
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04
EAC retirement evidence. Every claimed REGO / GO / REC / I-REC must trace to a retirement statement issued by the relevant registry (Ofgem, AIB issuing body, US REC tracking system, I-REC Standard registry). Retirement against the reporting year — not subsequent or prior years. Sample at least 5 instruments per material EAC class for evidence retention.
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05
SBTi target basis. If reporting against an SBTi target, state the Scope 2 method used for it. Bundled REGO/GO from existing assets are valid CDP/CSRD MB inputs; check them against the V2.0 age and deliverability limits before moving to that version.
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06
Scope 3 Cat 3 T&D inclusion. T&D losses are required under GHG Protocol Scope 3 Standard Cat 3 (FERA, T&D sub-component). Computed against LB only, on a separate inventory line — never aggregated into Scope 2. Verify the line is present and correctly classified.
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07
Multi-site portfolio invariant. When any site uses MB, the portfolio MB total must include all sites — sites without MB inputs carry their LB figure as the conservative default per §7.1. Verify the portfolio MB total is the correct sum (not just the sum of MB-declaring sites). The calculator engine §8 enforces this; check it has not been bypassed.
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08
Self-generation EAC posture. For any on-site solar / wind / CHP claim of Scope 2 reduction, confirm whether the EACs were retained or sold. Retained → genuine zero-Scope-2 for that consumption. Sold → residual mix factor applies on the on-site consumption. Double-counting EAC sales revenue and on-site Scope 2 reduction is the highest-risk failure mode in self-generation disclosures.
Methodology Metadata — for GHG Inventory Documentation
Copy verbatim into your GHG inventory methodology statement for ISO 14064-1 transparency compliance. Adjust the method, jurisdiction, and instrument lines to match your inventory choices.
[gc_grid] backed by MasterBrain (verified 2026-10-05).
29.8); check each publisher’s stated GWP basis, including EPA eGRID’s technical guide, before reconciling. Reporters reconciling against an internal AR6 baseline should note this in the methodology statement.
Frequently Asked Questions
If you hold any contractual instruments — even one bundled REGO — yes. The GHG Protocol Scope 2 Guidance §7.1 (the “dual-reporting invariant”) requires both totals to appear in the disclosure when market-based instruments are available. Location-based is never suppressible — it is the answer to “what would your Scope 2 footprint be without any contractual claims” and serves as the anchor against which market-based progress is measured. If you hold no instruments at all, location-based alone is compliant under every framework. The most common production failure is a “we report market-based” disclosure that has deleted the LB anchor — that is non-compliant under GHG Protocol, CSRD ESRS E1 and CDP.
Arithmetically yes; methodologically no. The MB calculation is identical: matched kWh × supplier factor (typically 0 under the REGO/GO/REC zero-emission convention) plus unmatched kWh × residual mix. The numerical output for 100% coverage is zero in both cases. But the nature of the zero differs. A bundled REGO purchased on the secondary market is associated with existing renewable generation that would have generated regardless of the reporter’s purchase — its additionality is low. A contracted PPA for new-build generation directly funds capacity that would not exist without the contract — its additionality is high. CDP, CSRD, and the GHG Protocol all currently accept both at face value. SBTi V1.3.1 sets no additionality test, but V2.0 limits instruments by generator age and deliverability from February 2027. The methodology consequence: disclose the instrument type alongside the MB total — “0 tCO₂e, 100% bundled REGO” tells a reviewer something different from “0 tCO₂e, 100% contracted PPA new-build solar”.
Because the geography is doing more work than any other methodology choice. The US national average is 0.350 kg CO₂e/kWh. The 10 eGRID2023 subregions in the MasterBrain set range from 0.110 (Upstate NY, hydro+nuclear) to 0.566 (SERC Midwest, coal 59%) — a 5× spread. A multi-site US portfolio that uses the national average for all sites is leaving precision on the table that no instrument-level optimisation can recover. Any US site whose physical electricity supply is traceable to a specific NERC subregion should use that subregion’s eGRID factor. The exception is data centres or other operations served by interconnected utilities crossing subregion boundaries — there, the utility’s own published emission factor (if available) or a pro-rata composite is the more defensible choice.
Two defensible approaches. The first: use the location-based grid factor as a residual proxy with an explicit audit flag noting that no published residual mix exists in the jurisdiction. This is the most conservative position when EAC market depth is shallow. The second: apply a conservative untraced-premium multiplier to the grid factor — typically 1.10× to 1.20×, reflecting the renewable share already claimed by other reporters’ EAC retirements. The Scope 2 Electricity Calculator reads the published residual mix where one exists (AIB 2025 for 31 European countries, the NGA factor for Australia) and applies a 1.15× factor only where none is published, with an audit warning. For high-stakes disclosures (CSRD reasonable assurance, SBTi target validation) outside those countries, source a published residual mix — Green-e in the US — and document it.
Scope 3, Category 3 (FERA — Fuel- and Energy-Related Activities, T&D losses sub-component). Always a separate inventory line, never aggregated into Scope 2. The reasoning: Scope 2 is the emissions associated with the electricity the reporter consumes at the meter; T&D losses are the additional generation upstream of the meter that the grid had to produce so that the reporter’s consumption was met after physical losses. The reporter caused the loss but did not consume the lost electricity. Computed against the location-based grid factor only (not market-based) — physical losses occur on the grid regardless of whether the reporter holds REGOs, GOs, or PPAs. Required under GHG Protocol Scope 3 Standard, increasingly expected under CSRD ESRS E1-6 value-chain disclosure, routinely required by CDP for full points. The full country-by-country loss factors, the two arithmetic shapes, and the audit checklist are documented in our T&D losses methodology, with the 40-country implementation available in the T&D Losses Calculator. For a UK reporter, T&D typically sits in the 8–10% range relative to Scope 2 LB.
Only if you retained the EACs. The single audit question for any self-generation Scope 2 claim is: who owns the renewable attribute? If your on-site solar generated EACs (REGOs in the UK, GOs in the EU) and you retained them — i.e. you did not sell them to a third party — your on-site consumption never enters Scope 2 at all. There is no purchase, no grid import, no inventory line. If you sold the EACs to another organisation — perhaps to monetise the renewable revenue — that other organisation now owns the renewable claim against your generation. You kept the energy but not the attribute. Your on-site consumption must use the residual mix factor for the jurisdiction, not zero. Mixing the two — claiming both the Scope 2 reduction and the EAC sale revenue — is a double-count flagged by every reasonable-assurance auditor. Self-generated electricity exported to the grid is sold, full stop; whoever buys the energy and the associated EACs has the claim.
Not yet required for any current disclosure framework, but increasingly worth tracking. Annualised matching — what every framework currently requires — has a structural blind spot: a reporter consuming 2.5 GWh/year and retiring 2.5 GWh of REGOs declares 100% MB coverage even when the wind farm whose REGOs they retired produces at night while the office is closed. Hourly carbon-free energy (CFE) accounting refines this by matching each hour’s consumption against each hour’s generation. Google’s published 24/7 CFE methodology, the EnergyTag Standard, and the European Commission’s 2023 proposal for granular Guarantees of Origin are the production references. For 2026 disclosures: stay annualised, but track hourly internally if you have material PPA coverage. SBTi V2.0 makes larger companies report an hourly-matched share; reporters who can demonstrate strong hourly metrics will have a stronger story. Hourly match factors are not yet shortcoded into the MasterBrain or calculator.
The retention list reflects Scope 2’s dual-method structure. Always: utility bills covering the full reporting year per meter, with kWh totals reconcilable to the disclosed activity data; the published grid factor source citation (DEFRA 2026 workbook reference, the national publisher’s release for other countries, EPA eGRID 2023 release) with version stamp; methodology statement documenting the LB-only or LB+MB choice and the jurisdiction selection. If MB is reported: EAC retirement statements from the relevant registry (Ofgem for REGOs, AIB issuing body for GOs, US REC tracking system for RECs, I-REC Standard registry for I-RECs) covering retirements against the reporting year specifically; PPA contracts with disclosed factor where applicable; supplier-specific factor disclosures; residual mix factor citation with provenance. If T&D is reported: T&D factor or loss-rate source (DEFRA 2026 UK electricity T&D factor, ADEME, or the World Bank national loss rate). For multi-site portfolios: per-site breakdown with the consolidation approach (financial vs operational control) documented per GHG Protocol Corporate Standard §3. Retention period: inventory year plus a re-validation cycle — ISO 14064-1 sets the practical floor at five years for most organisations.
Calculator
Apply this methodology with audit-grade output, dual-method (LB + MB) display, multi-site portfolio mode, automatic Scope 3 Cat 3 T&D companion, published grid factors for six countries and 27 US eGRID subregions plus custom factors, EAC instrument tagging, AIB and national residual mixes, and JSON + CSV export with full provenance: Open the Scope 2 Electricity Calculator →