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Level 2 · Decision guide·EU Voluntary Standard 2026 · Disclosure guides

EUVS KH 28 Environmental B Disclosures

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Who this is for A 10-minute read for reporting teams working through Preparing, controlling and releasing the report, 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 European Commission

Edition written against

Important limitation. This article is educational material, not legal advice or an assurance conclusion. The undertaking …

Published

12 Aug 2026

Knowledge Hub guide

Last reviewed

11 Aug 2026

Short answer

The answer, before the reasoning

B4-B7 do not share one universal applicability test. B4 covers own-operation pollutant emissions that the undertaking must report to authorities under EU or national law, or voluntarily reports under an environmental management system.

B5 applies when a site or location is in or near a biodiversity-sensitive area. B6 covers water withdrawal, and adds water consumption where production processes significantly consume water plus separate consumption at water-stressed sites. B7 asks whether circular principles are applied and includes waste and, for sectors with significant material flows, relevant annual material mass. The B1 site register should be the common data spine, but each disclosure needs its own trigger, source, boundary, unit and review.

How to test B4-B7 applicability and build a site-based evidence map

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Why one “environmental applicability” decision is not enough

Pollution, biodiversity, water and circularity are grouped in the Basic Module, but the reporting trigger differs for each. A company can have no pollutant emissions that it reports to authorities, yet operate next to a biodiversity-sensitive area. It can have low water withdrawal overall, yet one production site in a stressed basin. It can generate waste without operating in a sector with significant material input flows.

A robust reporting process therefore starts with the full site population from B1 and applies four separate tests. The result is not simply “environment applicable: yes/no”; it is a disclosure-by-disclosure record showing trigger, data source, boundary, unit, method, owner, evidence and conclusion.

Quick orientation

Figure 1. B4-B7 require separate applicability tests and outputs.

Quick orientation

Applies to
Undertakings preparing the Basic Module and assessing B4-B7 at each site or relevant operation.
Primary decision
Which disclosure applies, at which locations, using which source records and units.
Key sources
Annex I paragraphs 34-39 and Appendix A definitions; external law/databases as implementation evidence.
Common confusion
Treating all environmental metrics as mandatory, or using a broad materiality judgement instead of the specific trigger in each disclosure.

1. Start with a controlled site register

B1 requires geolocation of sites owned, leased or managed. That register should be the starting population for B5 and the control spine for B4, B6 and B7. Environmental datasets often use different names for the same site, so a unique site ID and coordinates are essential for matching permits, protected-area databases, water basins, waste contractor records and production systems.

In practice

Site field Purpose Control question
Site ID, name and coordinates Stable matching across systems and years Are duplicate names, shared premises and moved locations resolved?
Entity and reporting-boundary status Connects site data to individual or consolidated report Is the site included for the full or part of the period?
Ownership / lease / management Supports B1 completeness and operational responsibility Are landlord-controlled services and shared facilities identified?
Activities and production processes Drives B4, B6 and B7 applicability Did the activity change during the reporting period?
Permit / EMS references Supports the B4 population Which pollutants and authorities are in scope?
Biodiversity and water-context tags Supports B5 and B6 Which database, date and spatial method were used?

2. B4 pollution: follow the reporting obligation or EMS record

B4 requires emissions of pollutants to air, water and soil from the undertaking’s own operations when those emissions must be reported to competent authorities under EU or national law, or are voluntarily reported under an environmental management system. If the information is already public, the undertaking may refer to that document through a URL or hyperlink.

The trigger is therefore not “does the site emit anything?” It is whether the undertaking has a pollutant-emission reporting population under applicable law or its EMS. The legal and environmental teams should identify the authoritative return, pollutant, medium, unit, site, period and authority. A cross-reference should lead directly to the relevant information and remain accessible.

In practice

B4 source What to extract Review control
Permit and legal reporting inventory Authority, law, site, pollutant, medium, threshold/reporting duty Legal/environmental owner confirms current duty and reporting period.
Regulatory return or public pollutant portal Reported quantity, unit, method and publication link Reconcile to the filed return; test link and document version.
Environmental management system register Voluntarily reported pollutant data and method Confirm it is actually reported under the EMS, not merely measured internally.
Laboratory / monitoring data Underlying measured or calculated result Check sampling, conversion, estimate and quality controls.

3. B5 biodiversity: test every site against the defined BSA population

B5 applies when the undertaking has sites or locations in or near a biodiversity-sensitive area. Appendix A includes legally or otherwise effectively protected areas - for example Natura 2000, UNESCO Natural World Heritage and Ramsar sites - and scientifically recognised areas such as Key Biodiversity Areas and relevant IUCN ecosystem or species habitats.

“Near” includes overlap or adjacency. If a site is outside and not adjacent, the undertaking may define an area of influence using activity-specific regulation, science-based recommendations and industry practice. This means a fixed global buffer is rarely defensible for every activity. A quarry, logistics depot, office and water-intensive plant can have very different pathways of influence.

In practice

Step Action Owner / input — Output / control
1 Extract coordinates and site footprint from the B1 register. Property/operations + GIS record. — Controlled site geometry.
2 Select authoritative BSA datasets for each jurisdiction. Biodiversity specialist / official databases. — Dataset register with date and coverage.
3 Test overlap and adjacency. GIS analysis. — Direct spatial result and evidence file.
4 Where needed, define the area of influence. Technical specialist + activity pathways. — Documented buffer/pathway rationale.
5 Validate exceptions and site status. Site owner + reviewer. — Final B5 site/BSA list.
6 Disclose site/location and BSA name. Reporting team. — Traceable B5 disclosure.

4. B6 water: separate withdrawal, discharge and consumption

B6 first asks for total water withdrawal: all water drawn into the undertaking or facility boundary from all sources. Where production processes significantly consume water, it then asks for water consumption calculated as withdrawal minus discharge from those production processes. The undertaking also separately presents water consumed at sites in areas with water stress.

The Annex defines water stress broadly, including availability, quality and accessibility. A practical method may use recognised basin-level tools. The European Environment Agency’s WEI+ indicator, for example, treats values above 20% as stress and above 40% as severe stress. Those thresholds are an external method choice, not thresholds written into B6; the undertaking should record tool, geography, time granularity, date and limitations.

In practice

Metric Working formula / meaning Typical sources — Key risk
Water withdrawal All water drawn into the boundary Water bills, abstraction meters, wells, tanker records, landlord allocations — Omitting non-mains sources or shared-site consumption.
Water discharge Water leaving to surface water, groundwater or third parties Effluent meters, permits, invoices, process balance — Using total site discharge when only production-process consumption is being calculated.
Water consumption Withdrawal minus discharge for significant production processes Process water balance and meter data — Negative or implausible values caused by mismatched boundaries/periods.
Consumption in water-stressed areas Consumption attributable to sites in areas with water stress Site consumption plus basin/context assessment — Using country-level averages that mask local or seasonal stress.

5. B7 circularity: narrative and metrics are distinct

B7 first asks whether the undertaking applies circular-economy principles and, if so, how. Appendix A frames those principles as eliminating waste and pollution by design, circulating products and materials at their highest value, and regenerating nature. The narrative should describe actual operating practices rather than repeating the definition.

The metrics then cover total waste, hazardous/non-hazardous breakdown, the proportion diverted to recycling or preparation for reuse, and - for sectors using significant material flows - annual mass flow of relevant materials used. Energy sources and water should not be silently mixed into a material-flow figure unless the selected method and final text support that treatment.

Figure 2. The B1 site register connects four different environmental evidence streams.

In practice

B7 element Source-to-metric approach Control
Circular principles Map actual design, reuse, repair, recycling, take-back or regenerative practices Evidence the practice; avoid generic commitments.
Waste total and hazard class Waste transfer notes, internal weighing, contractor statements and legal classification Reconcile contractor categories; prevent double counting transfers.
Recycling / preparation for reuse proportion Eligible destination weight divided by total waste under the approved denominator Distinguish recycling, preparation for reuse, energy recovery and disposal.
Relevant material mass flow Purchases, production/BOM and inventory for selected key materials Define relevance, unit, exclusions and sector rationale.

In practice

6. A practical B4-B7 data-source map

Disclosure Primary owner Core systems / evidence — Output control
B4 Pollution Environmental compliance / site HSE Permit register, authority returns, EMS, laboratory data, public portal — Reported pollutant list reconciles to authoritative filing.
B5 Biodiversity Environment / property / biodiversity specialist Site coordinates, protected-area and KBA datasets, GIS analysis, area-of-influence note — All B1 sites tested using documented dataset/date.
B6 Water Facilities / production / environment Bills, abstraction/discharge meters, permits, landlord data, basin tools — Withdrawal-consumption-discharge boundaries reconcile.
B7 Circularity and waste Operations / procurement / waste owner Waste notes, contractor data, purchases, BOM/production records, practice evidence — Waste classes and material-flow denominator are approved.

In practice

7. End-to-end implementation workflow

Step Action Owner / input — Output / control
1 Lock the B1 site population and reporting period. Reporting lead + entity/site register. — Approved site universe.
2 Assign B4-B7 owners and applicability criteria. Environment, operations, legal and finance. — Requirement matrix.
3 Collect source registers and external datasets. Data owners + controlled URLs/versions. — Evidence inventory.
4 Perform site-level applicability tests. Technical owners. — Decision record for each site/disclosure.
5 Calculate metrics with common units and boundaries. Data preparers. — Calculation files and reconciliation.
6 Review public cross-references and limitations. Technical/legal reviewer. — Accessible links and balanced wording.
7 Reconcile with B1, permits, website and customer responses. Publisher / final approver. — Consistent final disclosures.

8. Hypothetical multi-site case

B4 is prepared from the Site 1 legal return; the public filing is cross-referenced only after the link and reporting period are checked. B5 names Site 2 and the Natura 2000 area. B6 reports total withdrawal, production-process consumption and separately the consumption at Site 2 using the documented stress method. B7 explains actual packaging-reduction and reuse practices, reconciles waste contractor categories and reports mass flow for selected significant materials.

The warehouse is not ignored: it remains in the B1 site population and contributes to water and waste totals where applicable. However, the team does not invent a pollutant disclosure for Site 3 when no B4 legal/EMS reporting trigger exists.

9. Illustrative disclosure wording

Evidence needed: B1 site register, permit/EMS mapping, public-return copies, GIS analysis, water-meter and discharge records, stress-tool screenshots or extracts, waste transfer records, contractor reconciliation and material purchase/production data.

10. Common mistakes

1. Applying one environmental materiality flag to B4-B7. Use the specific trigger in each disclosure.

2. Reporting measured pollutants that are outside the B4 reporting population without explaining the basis. Identify whether the source is a legal return or voluntary EMS report.

3. Testing biodiversity only at headquarters. Use every site/location in the B1 population.

4. Using a fixed global “near” distance. Document adjacency or an activity-specific area of influence.

5. Calling withdrawal consumption. Consumption is withdrawal minus discharge for the relevant production process.

6. Using country-level water stress without local review. Prefer basin/site and seasonal evidence where available.

7. Counting energy recovery as recycling. Apply waste definitions and destination evidence.

8. Selecting material flows only because data are easy. Document sector significance and relevance.

Readiness

12. B4-B7 readiness checklist

  • The B1 site population is complete, geolocated and linked to entities and activities.
  • B4 legal and EMS reporting populations are mapped by site, pollutant, medium and period.
  • Public cross-references open directly to the current relevant information.
  • Every site has been tested for BSA overlap, adjacency and, where needed, area of influence.
  • Water withdrawal, discharge and consumption use aligned boundaries and periods.
  • The water-stress tool, geography, date and threshold methodology are documented.
  • Circularity narrative describes operating practices, not only aspirations.
  • Waste classification distinguishes hazardous/non-hazardous and recycling/preparation for reuse from other recovery.
  • Relevant material flows have a defined sector rationale, unit, scope and source.
  • Employee reliefs have been assessed for B6 and B7.
  • A technical reviewer has challenged non-applicability conclusions and source gaps.

Self-check

  1. Could a reviewer reproduce the applicability conclusion for each B1 site?
  2. Does the B4 list reconcile exactly to legal or EMS reporting records?
  3. Can the team explain the difference between B5 location disclosure and a biodiversity impact assessment?
  4. Do water and waste metrics use internally consistent denominators and definitions?

Questions

Questions people ask

Does B4 require every pollutant measured at a site?

B4-B7 do not share one universal applicability test. B4 covers own-operation pollutant emissions that the undertaking must report to authorities under EU or national law, or voluntarily reports under an environmental management system.

What does “near” a biodiversity-sensitive area mean?

“Near” includes overlap or adjacency. If a site is outside and not adjacent, the undertaking may define an area of influence using activity-specific regulation, science-based recommendations and industry practice. This means a fixed global buffer is rarely defensible for every activity.

Is water consumption the same as water withdrawal?

B6 first asks for total water withdrawal: all water drawn into the undertaking or facility boundary from all sources. Where production processes significantly consume water, it then asks for water consumption calculated as withdrawal minus discharge from those production processes.

Does the Standard prescribe a 20% or 40% water-stress threshold?

The European Environment Agency’s WEI+ indicator, for example, treats values above 20% as stress and above 40% as severe stress. Those thresholds are an external method choice, not thresholds written into B6; the undertaking should record tool, geography, time granularity, date and limitations.

Must every company report annual material mass flow?

The metrics then cover total waste, hazardous/non-hazardous breakdown, the proportion diverted to recycling or preparation for reuse, and - for sectors using significant material flows - annual mass flow of relevant materials used. Energy sources and water should not be silently mixed into a material-flow figure unless the selected method and final text support that treatment.

Sources

Primary sources

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