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GRI 102 Scope 3 Reporting: Categories, Data Hierarchy and Supplier Estimates

A practitioner guide to screening all 15 categories, choosing defensible methods and building a credible improvement plan when value-chain data are incomplete

Who this is for A 23-minute read for reporting teams working through The new Climate, Energy and Biodiversity Standards, and for reviewers testing whether the evidence behind it holds.

Published passport

Current as at 11 August 2026
RK Reviewed by Dr Ross KurinkoLinkedIn Strategic ESG Advisor · IFRS S1 & S2 / GRI / ESRS expert GRI Certified Global Trainer · PhD, University of Cambridge · ESG-AI expert 15+ years on FTSE 100 & Fortune Global 500 disclosures Canary Wharf, London LRA educational guidance · Not issued or endorsed by GRI

Edition written against

Technical status: Source review completed on 1 August 2026. This draft separates source requirements from implementation …

Published

12 Aug 2026

Knowledge Hub guide

Last reviewed

11 Aug 2026

Short answer

The answer, before the reasoning

GRI 102: Climate Change 2025 requires gross Scope 3 emissions to be reported by each of the 15 GHG Protocol categories, together with the consolidation approach, methods, assumptions, emission-factor sources and relevant base-year information. A first-year reporter should therefore screen every category, calculate material or high-priority categories with the best available data, use transparent estimates for the rest, and record a time-bound improvement plan.

Supplier-specific data are valuable only when their boundary, allocation, period and controls are credible; a well-controlled activity-based estimate can be more useful than an untested supplier number.

Technical status: source-grounded publication draft; final human technical review required before release.

Quick orientation

Quick orientation

Applies to
Primary decision
Reporting teams implementing GRI 102, especially first-time Scope 3 reporters
How to calculate every category without waiting for perfect supplier data

What GRI 102 changes for Scope 3 reporting

Disclosure 102-7 moves Scope 3 from a broad total into a category-by-category reporting discipline. The organisation reports gross Scope 3 emissions in metric tonnes of CO2 equivalent, includes the seven greenhouse gases covered by the Kyoto Protocol, provides a breakdown for each of the 15 upstream and downstream categories, and explains its consolidation approach, methodologies, assumptions, calculation tools and emission-factor sources. The disclosure also contains base-year and recalculation information. (GRI 102, Disclosure 102-7.)

The practical consequence is important: the reporting team needs a controlled register for all categories, not merely a single workbook total. Screening remains essential, but its purpose is to identify the calculation depth, data-acquisition priority and quality-improvement plan for each category. It is not a licence to make inconvenient categories disappear from the disclosure.

Rule

Requirement versus implementation practice

Requirement: report Disclosure 102-7 in accordance with its category, boundary, method and base-year requirements. Implementation practice: use staged calculation methods, proxies, sampling and supplier engagement to reach a complete first-year inventory and improve it over time. If information remains unavailable or incomplete: apply GRI 1 Requirement 6 transparently at the relevant disclosure or requirement level.

The operating model: screen all, calculate proportionately, disclose transparently

A defensible Scope 3 project has four linked outputs: a complete category register, a calculation file, a data-quality and controls record, and a disclosure pack. The register is the bridge between GRI 102 and the GHG Protocol. It shows what the category covers for this organisation, what was included or excluded, which method was used, who owns the data, how the result was reviewed and what will improve next year.

Define the organisational and value-chain boundary. Record the consolidation approach selected for Scope 1, Scope 2 and Scope 3 - equity share, financial control or operational control - and apply it consistently. Then map the activities that sit upstream and downstream of the reporting organisation.

Screen every category. Use rough estimates and relevance criteria to identify likely magnitude, influence, transition exposure, stakeholder interest, outsourced activities and sector-specific significance.

Choose the calculation route. Select supplier-specific, hybrid, activity-based average, spend-based or other defensible methods according to the category and data available.

Rate data quality and uncertainty. Assess technological, temporal and geographical representativeness, completeness and reliability. Record boundary and allocation weaknesses separately from numerical uncertainty.

Calculate and challenge. Reconcile activity data to procurement, logistics, HR, asset and financial systems; check units and emission-factor years; investigate movements and outliers.

Disclose the category result and limitations. Explain methods and factor sources, show category-level totals, and use a reason for omission only where information cannot be reported as required.

Approve an improvement plan. Prioritise categories that combine high emissions, low data quality and strong ability to influence the value chain.

Figure 1. Scope 3 category map: screen all 15 categories, then tailor calculation depth and improvement activity.

The 15-category matrix

The matrix below is an implementation aid, not a replacement for the minimum boundaries and detailed calculation guidance in the GHG Protocol. “Typical data” identifies practical starting points. The final method must reflect the organisation’s facts, category boundary and intended use of the information.

In practice

Cat. What it usually covers Typical activity data — Practical calculation route — Frequent boundary trap
1 Cradle-to-gate emissions of purchased goods and services not captured in categories 2-8. Mass, units, service volumes, supplier spend, product specifications. — Supplier-specific or hybrid for priorities; average product/process factors; spend/EEIO for screening or residuals. — Mixing capital goods into category 1; accepting supplier totals without allocation or cradle-to-gate boundary.
2 Cradle-to-gate emissions of capital goods acquired in the reporting period. Asset additions, quantities, mass, construction bills of materials, capital spend. — Same broad methods as category 1; calculate emissions associated with goods acquired, not annual depreciation. — Spreading emissions over accounting useful life or double counting assets in category 1.
3 Upstream fuel and energy emissions not included in Scope 1 or Scope 2, including relevant transmission and distribution losses. Fuel quantities, electricity/heat/cooling consumption, grid loss data. — Activity data multiplied by life-cycle and loss factors; supplier-specific fuel factors where robust. — Including combustion already reported in Scope 1 or electricity generation already in Scope 2.
4 Third-party upstream transport and distribution, including purchased logistics services and relevant storage. Tonnes, distance, mode, fuel, pallets, warehouse energy or logistics spend. — Fuel-based or distance-based; supplier-specific logistics data; spend proxy if other data are unavailable. — Confusing who purchases the service; omitting outbound logistics paid for by the reporting organisation.
5 Third-party treatment and disposal of waste generated in operations. Waste mass by type and treatment route; wastewater volumes. — Waste-specific activity data × treatment factors; supplier data for treatment facilities where available. — Using waste collection invoices without treatment route or assuming all material is recycled.
6 Business travel in vehicles not owned or controlled by the organisation. Air/rail distance, hotel nights, car hire, taxi mileage, travel spend. — Distance or fuel/activity method; travel-provider data; spend proxy for residuals. — Combining employee commuting or company fleet fuel with business travel.
7 Employees travelling between home and work, including teleworking where relevant to the method. Employee survey, mode split, distance, days, workforce location. — Representative survey/extrapolation; average commute factors; targeted primary data for large locations. — Low survey response, no non-response adjustment, or counting company shuttle fuel twice.
8 Operation of leased assets upstream that are not already in the organisation’s Scope 1 or Scope 2 inventory. Floor area, energy, fuel, equipment use, lease register. — Asset-specific energy data; modelled energy intensity; lessor information. — Failing to align lease treatment with the selected consolidation approach.
9 Third-party downstream transport and distribution of sold products not purchased by the reporting organisation. Product mass, destinations, modes, distance, warehousing assumptions. — Distance/activity model; customer or distributor data for priority routes; representative scenarios. — Double counting category 4 or ignoring distribution beyond the first customer.
10 Processing of sold intermediate products by third parties. Quantity of intermediate product, process route, energy/material intensity. — Processor-specific data; process models; industry-average processing factors. — Applying category 10 to final products that require no further processing.
11 Direct use-phase emissions of sold products over their expected lifetime, plus optional indirect use-phase emissions where relevant. Units sold, lifetime, duty cycle, fuel/electricity consumption, leakage rates. — Product engineering model; sales-weighted assumptions; regional energy/fuel factors. — Using current-year operation only rather than lifetime use; weak treatment of product mix and geography.
12 End-of-life treatment of products sold in the reporting year. Product composition, units/mass sold, regional treatment scenarios. — Material-specific treatment factors and weighted disposal/recycling scenarios. — Assuming a single global treatment route or double counting packaging in category 1 and product end of life.
13 Operation of assets owned by the organisation and leased to others, if not already in Scope 1 or Scope 2. Asset register, tenant energy/fuel, floor area, utilisation. — Tenant/asset data; energy-intensity model; portfolio sampling. — Confusing downstream leased assets with upstream leased assets or consolidation treatment.
14 Operation of franchises not already included in Scope 1 or Scope 2. Franchise locations, floor area, energy, fuel, refrigerants, activity drivers. — Franchisee data; representative site models; sampling and extrapolation. — Reporting franchise fees or sales as a proxy without testing operational drivers.
15 Investments not included in Scope 1 or Scope 2, including relevant equity, debt and project finance activities. Investment exposure, counterparty emissions, enterprise value or sector data, asset information. — Asset/counterparty-specific financed-emissions methods; sector estimates and attribution methods. — Treating all treasury assets identically or overlooking the boundary and attribution rules for the portfolio.

How to assess significance without turning screening into exclusion

The GHG Protocol recommends screening Scope 3 activities using rough estimates and considering more than size. Relevant criteria include the expected magnitude of emissions, the organisation’s influence, climate-related risks and opportunities, stakeholder concerns, activities previously performed in-house but now outsourced, sector guidance and other organisation-specific criteria. A category can be strategically important even when its first rough estimate is not the largest.

For GRI 102, keep three decisions separate. First, is climate change a material topic under the GRI material-topic process? Second, what falls within each Scope 3 category and how will it be calculated? Third, where should the organisation invest in better data and action? A category screening score should not be presented as if it were the organisation’s GRI materiality determination.

Rule

A practical prioritisation rule

Prioritise data improvement where three factors overlap: high or potentially high emissions, weak or decision-sensitive data, and meaningful organisational influence. A low-quality estimate in a small, stable category may be acceptable for the first year; a low-quality estimate that drives 40% of the footprint is not.

A defensible data hierarchy

A data hierarchy should guide judgement, not replace it. IFRS S2 and GHG Protocol concepts both point towards more direct, activity-specific, timely, geographically and technologically representative data where practicable. GRI 102 guidance recommends reporting the percentage of emissions obtained through primary data for each category. Yet a supplier number is not automatically high quality: it can use the wrong period, omit upstream stages, apply an inconsistent consolidation approach, allocate emissions arbitrarily or lack review.

Figure 2. A practical Scope 3 data hierarchy and first-year roadmap.

In practice

Level Data form When it is strongest — Minimum controls
1 Supplier or value-chain partner GHG inventory allocated to the purchased product, service or relationship. High-priority categories where the partner has a credible inventory and defensible allocation. — Boundary and period match; method and factor source; allocation basis; review or verification status; no double counting.
2 Supplier-specific activity data calculated with the reporting organisation’s controlled factors. Supplier can provide quantities, energy, materials, distance or waste but not a robust product footprint. — Units and completeness; mapping to factor; factor version; transformation controls; supplier evidence retained.
3 Organisation-controlled activity data with product, process or sector-average factors. Physical drivers are available from procurement, logistics, product or asset systems. — Reconciliation to source systems; appropriate factor geography/technology/year; sampling and extrapolation logic.
4 Spend-based EEIO, revenue, floor-area or other proxy. Rapid screening, broad service categories and residual populations where physical data are unavailable. — Currency and inflation treatment; factor year; category mapping; sensitivity to price movements; explicit uncertainty.
5 Sampling, extrapolation or management estimate. Temporary gap bridge where the population cannot yet be measured. — Population definition; sample representativeness; calculation and reviewer approval; gap log; time-bound replacement plan.

Supplier estimates: what to ask for and how to test them

Do not begin with a generic “send us your carbon footprint” request. Ask for data that correspond to the category, product and reporting boundary. A useful supplier request identifies the product or service purchased, reporting period, quantity or allocation base, organisational and product boundary, gases and GWP values, Scope 1/2/3 components included, emission-factor sources, verification status and known exclusions.

In practice

Test Question for the supplier or data owner Why it matters
Boundary Does the figure cover cradle-to-gate emissions for the supplied product or only the supplier’s operational Scope 1 and 2? A corporate inventory may omit upstream inputs needed for category 1 or category 2.
Allocation How were facility or corporate emissions allocated to our product or contract? Revenue allocation can distort results for products with very different production intensity.
Period Which production year and quantity does the figure represent? A footprint from a different year may not reflect technology, grid or product changes.
Factors and GWP Which databases, emission factors and GWP values were used? Factor vintage and regional fit affect comparability and recalculation.
Completeness Which life-cycle stages, gases, sites or subcontractors are excluded? An apparently precise number can be incomplete.
Assurance / review Was the information independently assured, internally reviewed or generated automatically? Review status is one input to reliability, not a substitute for boundary testing.
Duplication Could this figure overlap with transport, capital goods or another category? Category totals need clear ownership to avoid double counting within the inventory.

Using proxies and emission factors without losing credibility

Secondary data are not a reporting failure. They are a normal part of Scope 3 measurement, especially in a first year. The quality question is whether the proxy is appropriate, consistently applied and transparently disclosed. A physical proxy - tonnes of steel, tonne-kilometres, kilowatt-hours, litres of fuel, waste mass or product use - usually preserves more operational meaning than spend. Spend-based factors can nevertheless be efficient for screening and for service categories where physical activity is genuinely unavailable.

Maintain an emission-factor register with the factor name, publisher, database version, geography, technology, unit, GWP basis, applicable category, date downloaded and owner. Lock the factor set for the reporting cycle. Changes after calculation should be controlled, documented and, where material, trigger a recalculation or restatement assessment.

Rule

Estimate disclosure pattern

Explain what is estimated, the method and principal assumptions, the share of the category covered, the data-quality limitation, and the specific action and timeframe for improving the estimate. Do not hide uncertainty behind a precise number with many decimal places.

What to do when information is unavailable or incomplete

GRI 1 permits the reason for omission “information unavailable/incomplete” for disclosures and requirements where reasons for omission are allowed. The organisation must specify the information that is missing, explain why it is unavailable or incomplete, and describe the steps being taken and the expected timeframe for obtaining it. Under GRI 102 guidance, this route is available where a Scope 3 category cannot be reported as required. It should be a controlled exception, not the default calculation method.

Before using an omission, test whether a reasonable estimate is possible. If a category can be estimated using activity data, a representative factor, sampling or a sector proxy, a transparent estimate will often provide more useful information than a blank cell. The decision should be documented and approved, especially when the missing category could be significant.

Illustrative first-year case

The company does not wait for supplier footprints. It uses mass-based product factors for steel, aluminium and packaging; a spend-based model for residual purchased services; distance and mode data for the known logistics population plus a tested extrapolation for the remainder; and an engineering lifetime-use model for sold equipment, segmented by product type and sales region. It records the percentage of each category based on primary activity data, documents the factors and assumptions, and launches supplier requests for the ten highest-emission material groups.

The result is not “perfect”, but it is complete enough to reveal where action and data improvement matter. The company’s Year 2 plan is to replace spend estimates for priority materials, improve logistics coverage from 60% to 90%, collect verified use-phase assumptions from product engineering and add automated reconciliations to procurement and sales systems.

Hypothetical scenario

Hypothetical example - diversified manufacturer

A manufacturer has reliable Scope 1 and Scope 2 data, procurement spend for all suppliers, physical quantities for metals and packaging, logistics data for 60% of inbound freight, and no supplier product footprints. It sells energy-using equipment in 35 countries. Initial screening indicates categories 1, 3, 4 and 11 are likely to dominate.

Illustrative only. It shows how the decision is made, not wording that can be copied or relied on.

In practice

Weak versus stronger Scope 3 disclosure

Weak wording More useful wording Why the second is stronger
“Scope 3 emissions were 1.2 million tCO2e. Supplier data were unavailable, so industry averages were used.” “Gross Scope 3 emissions were 1.2 million tCO2e. Categories 1, 4 and 11 represented 84% of the total. Category 1 used physical quantities for metals and packaging and spend-based factors for residual services; category 4 covered 60% of tonne-kilometres directly and extrapolated the remainder; category 11 used sales-weighted lifetime energy assumptions by region. Primary activity data supported 68% of the total. The main limitations are supplier allocation data and product-use assumptions. During 2027, the organisation will obtain supplier-specific data for the ten largest material groups and raise logistics coverage to 90%.” It identifies the category mix, methods, coverage, primary-data share, limitations and time-bound improvement actions. It still needs the full GRI 102 category table and source details elsewhere.

In practice

Common mistakes and how to correct them

Mistake Why it happens Reporting risk — Correction
Calculating only “significant” categories and leaving the others invisible. The screening exercise is treated as a reporting boundary decision. The category breakdown is incomplete and users cannot see what was assessed. — Keep all 15 categories in the register; report results, not-applicable conclusions or permitted omissions transparently.
Accepting supplier footprints without boundary testing. The number looks primary and precise. Under-counting, inconsistent allocation and double counting. — Apply a supplier-data acceptance checklist and retain methodology evidence.
Using spend factors for everything. Procurement data are easy to obtain. Results track price inflation and currency more than operational activity. — Use spend for screening and residuals; move high-emission categories to physical or supplier data.
Changing factors during drafting without a controlled recalculation. Different teams update databases independently. Unreconciled totals, inconsistent base years and assurance findings. — Lock factor versions, approve changes and maintain a recalculation log.
Reporting a single total with no category-level methods. The inventory workbook is not designed for disclosure. Users cannot understand sources, quality or improvement priorities. — Build the category register and category-level method notes before writing the report.
Hiding estimates because they are “not accurate enough”. Teams fear that disclosure of uncertainty undermines credibility. Omission of decision-useful information and delayed learning. — Report the best available estimate with specific limitations and a time-bound improvement plan.

Rule

Myth: “A first-year Scope 3 inventory must be supplier-specific to be credible.”

Reality: credibility comes from completeness, appropriate methods, representative inputs, transparent limitations, controls and a visible improvement plan. Supplier-specific data can strengthen an inventory, but only after its boundary and allocation are tested.

Next step

Treat the first inventory as the beginning of a reporting system. Lock the category register, assign data owners, connect improvement actions to supplier engagement and product decisions, and schedule a post-publication review while the evidence is still fresh. The strongest Year 2 improvement plan is based on observed data-quality weaknesses, not a generic promise to “collect more primary data”.

Rule

Internal use

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Questions

Questions people ask

Does GRI 102 require all 15 Scope 3 categories?

GRI 102: Climate Change 2025 requires gross Scope 3 emissions to be reported by each of the 15 GHG Protocol categories, together with the consolidation approach, methods, assumptions, emission-factor sources and relevant base-year information. A first-year reporter should therefore screen every category, calculate material or high-priority categories with the best available data, use transparent estimates for the rest, and record a time-bound improvement plan.

Can an organisation use estimates for Scope 3?

GRI 102: Climate Change 2025 requires gross Scope 3 emissions to be reported by each of the 15 GHG Protocol categories, together with the consolidation approach, methods, assumptions, emission-factor sources and relevant base-year information. A first-year reporter should therefore screen every category, calculate material or high-priority categories with the best available data, use transparent estimates for the rest, and record a time-bound improvement plan.

Is supplier-specific data always the best data?

A first-year reporter should therefore screen every category, calculate material or high-priority categories with the best available data, use transparent estimates for the rest, and record a time-bound improvement plan. Supplier-specific data are valuable only when their boundary, allocation, period and controls are credible; a well-controlled activity-based estimate can be more useful than an untested supplier number.

Should spend-based calculations be replaced immediately?

A physical proxy - tonnes of steel, tonne-kilometres, kilowatt-hours, litres of fuel, waste mass or product use - usually preserves more operational meaning than spend. Spend-based factors can nevertheless be efficient for screening and for service categories where physical activity is genuinely unavailable.

Sources

Primary sources

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