By: Johannes Fiegenbaum on 7/29/25, 11:30 AM · Last updated September 16, 2026
Biodiversity became a reporting obligation before most companies built a process for it. Under the European Sustainability Reporting Standards, a company that concludes biodiversity is material has to disclose defined data points, not a narrative about nature. This page covers that step: what ESRS E4 asks for, how nature enters a double materiality assessment, which screening approach fits which company, and what the result needs to survive assurance. For the wider strategic picture, see biodiversity in ESG: frameworks, risks and opportunities.
ESRS E4 is the biodiversity and ecosystems standard inside the European Sustainability Reporting Standards. It is conditional: it applies in full once your double materiality assessment concludes that biodiversity is material, and not before. That conditional is why reporting projects treat nature as optional until late in the cycle, and then run out of time.
Once E4 applies, the standard is specific about what has to appear in the report:
The published standards and the accompanying implementation guidance are available from EFRAG, and the policy targets they serve are set out in the EU Biodiversity Strategy for 2030. Confirm your own scope and first reporting year before planning the work: the Omnibus revision changed who falls in scope and when. Neighbouring rules help, the EU Deforestation Regulation already demands geolocation data an E4 screen can reuse.
Biodiversity does not need its own parallel process. It is a topic inside the double materiality assessment you already run, and it has the same two sides as every other topic. The impact side asks what your operations and value chain do to nature: land taken, water abstracted, pollutants released, species displaced.
The side that gets skipped is the other one. Dependencies ask what nature does for you, and they are the reason biodiversity shows up on the financial materiality axis at all. Those are ecosystem services: pollination, freshwater availability and quality, soil fertility, flood and storm buffering, climate regulation. A beverage producer drawing groundwater from a stressed catchment has a biodiversity dependency long before it has a biodiversity impact story, and it is the dependency that shows up in the cost of water rights.
In practice the screen runs in one direction: list your sites and main purchased commodities, ask which ecosystem services each relies on, then which pressures each exerts. Both answers feed the materiality matrix that already exists. Treating nature as a separate workstream produces two assessments that contradict each other, and an auditor will find the seam. Most of the exposure sits upstream, which is why biodiversity risk in supply chains is usually the larger half.
The tools are not interchangeable, and the choice follows two things: your sector and how much site-level data you already hold.
| Approach | Scope | What you need | What it gives you | Where it stops short |
|---|---|---|---|---|
| ENCORE (sector screening) | Sub-industry level, impacts and dependencies on ecosystem services | Your activities mapped to sectors, no coordinates | A shortlist of which activities are exposed at all | Says nothing about your specific sites |
| WWF Biodiversity Risk Filter (site screening) | Locations and value chain, physical and reputational risk | Coordinates or addresses | A risk score per site and the drivers behind it | Scores are modelled from global layers, not surveyed on site |
| IBAT (protected and key biodiversity areas) | Proximity to protected areas, key biodiversity areas and Red List ranges | Coordinates, plus a paid subscription for commercial use | Evidence for the ESRS test on biodiversity-sensitive areas | Proximity is not impact |
| Footprint models (BFFI, GBS and similar) | Quantified impact expressed in one biodiversity metric | Volume or spend data across the value chain | A comparable number you can track over time | Inherits the uncertainty of the input and hides which site drives it |
| TNFD LEAP and SBTN target setting | A structured process rather than a data product | Cross-functional time and the outputs of the tools above | A defensible sequence from exposure to targets | Produces no data of its own |
A word on the AI-assisted screens now sold with most reporting platforms: they help, and they do not replace expertise. An automatically generated nature screen is a starting point, never an assurance-ready result. The handover point is easy to name. As soon as the screen flags a site as material, a global data layer stops being sufficient and someone has to establish what is actually there, through land-use records, permits, local surveys or an assessment run against the TNFD LEAP approach.
A screening result is not a disclosure. What turns one into the other is documentation of the decision, and this is where most first-year reports are thin. Auditors do not challenge the biodiversity score, they challenge how it was produced: which sites were included, which were left out and why, which thresholds decided materiality, and who signed off.
Write the negative conclusion down as carefully as the positive one: it will be tested against the pressures the standard names. If biodiversity comes out material, plan for site evidence on the flagged locations in the same reporting year, not the next one. The practical next step is small. Assemble a site list with coordinates, land area and land use, then run the sector screen against it. Everything in E4 hangs off that list, and it also feeds the rest of your EU reporting obligations.
If only the VSME standard is in scope, none of this turns into an E4 obligation. The voluntary standard for smaller companies carries no equivalent of the full biodiversity requirement, and there is no double materiality assessment behind it that could switch one on. What it does ask sits in the basic module: whether any site is located in or near a biodiversity-sensitive area, and how much land the company occupies. Both answers come out of the same site list, so the work is the same in kind and much smaller in scope. A larger customer asking for nature data further up the value chain is a contractual request, not a reporting obligation, and it can be answered from that list.
There is no single best tool, there is a right order. Screen at sector level first, then screen the sites that step flags, then quantify only what turned out to be material. Running a footprint model first is the usual way to spend a budget and still not know which site matters.
The trigger is the conclusion of your double materiality assessment, not a threshold in the standard. If biodiversity is material on either the impact or the financial side, E4 applies in full. If it is not, the explanation has to be as traceable as a disclosure would have been.
With coordinates. A site list with location, land area and land use is enough to run a screening tool and to answer the question about proximity to biodiversity-sensitive areas. Site surveys come later, and only for the locations the screen flagged.
ESG and sustainability consultant based in Hamburg, specialised in VSME reporting and climate risk analysis. Has supported 300+ projects for companies and financial institutions, from mid-sized manufacturers to major banks and insurers.
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