Ecology, BNG and Protected Species

Degradation before the baseline: the 2020 provision

6 min readBy PlanScope Editorial Team

The biodiversity gain rules contain a backstop. Clear habitat without consent after 30 January 2020 and the baseline is measured as it stood before the clearance, not as the site is found.

The biodiversity gain regime contains an anti-avoidance rule, and it is the reason a cleared site is not a clean site. Where activities carried out on land on or after 30 January 2020, without planning permission or another consent the legislation recognises, reduced the biodiversity value of the onsite habitat, the pre-development value is taken to be the value immediately before those activities were carried out. Anyone researching a bng degradation baseline date question is usually doing so because a field has been ploughed, a scrub belt has been flailed, or a hedge has gone, and someone has noticed.

The effect is straightforward and expensive. The metric is run against habitat that is no longer there, and the 10 per cent gain is calculated on top of it.

Why that particular date

30 January 2020 is the date the Environment Bill was introduced to Parliament. From that point the direction of policy was public, and the regime that became mandatory for major development in February 2024 and for small sites in April 2024 was visible to anyone paying attention.

Fixing the backstop at introduction rather than at commencement removes the reward for acting during the gap. Without it, the rational move for a landowner with an unallocated field of species-rich grassland would have been to plough it in 2021 and apply in 2025.

When the earlier baseline applies

Three elements have to line up. Activities were carried out on the land on or after the date. Those activities reduced the biodiversity value of the onsite habitat. And they were not carried out under a planning permission or other recognised consent.

That third element is where the argument usually sits. Ordinary lawful farming operations are not the target of the provision, and a field that has been in an arable rotation for decades is not degraded by being ploughed again. A field of unimproved grassland sprayed off and reseeded in the year before an application is a different conversation, and one the authority's ecologist will want evidence about.

Where the authority concludes habitat was degraded, the earlier value applies to a Biodiversity Net Gain Assessment whether or not the applicant carried out the clearance. The provision attaches to the land.

That has a practical consequence for option agreements and conditional contracts. A promoter taking an option over a field has no way of knowing from the ground whether the vendor flailed a hedgerow in 2022, and the vendor has every incentive not to raise it. Asking the question directly, in writing, and checking imagery for the years since the date, is now part of ordinary land due diligence rather than an ecological refinement.

Reconstructing what was there

Retrospective baselines are built from records rather than from the ground, and the evidence available is better than most applicants expect.

  • Historic aerial imagery, including successive years of commercial imagery, which will often show hedgerow lines, scrub extent and sward character.
  • Publicly available survey data, including terrain and surface models that reveal hedge banks, ditches and former field boundaries.
  • Satellite imagery time series, which can show seasonal vegetation change across several years.
  • Local environmental records centre data, including species records tied to the parcel.
  • Earlier ecological reports, whether from a previous application on the site or from a neighbouring one.
  • Historic Ordnance Survey mapping, for boundaries and woodland extent.
  • Agri-environment scheme agreements, which describe the habitat the land was managed for.
  • Photographs held by neighbours, parish councils or objectors, which surface at exactly the wrong moment if the applicant has not found them first.

The classification that results is necessarily coarser than a field survey. An honest reconstruction states the uncertainty and takes a reasonable view, and an authority will usually accept a precautionary assumption in preference to a dispute.

Illustrative example: a five-hectare parcel presented as arable in a submitted baseline. Aerial imagery from three years before showed two internal hedgerows and a block of scrub that the submitted plan did not record. The reconstructed baseline added hedgerow units and a small parcel of medium distinctiveness habitat, and the on-site gain that had been designed no longer worked. That example is illustrative.

What it does to the arithmetic

A restored baseline raises the number of units the scheme has to deliver, and it does so at the worst point in the calculation.

Higher distinctiveness habitat is harder to recreate, so the difficulty multiplier bites. Habitats that take years to reach target condition carry a temporal discount. Hedgerow units sit in their own account and cannot be made up with area habitat. The practical result is that on-site delivery frequently becomes impossible and the scheme moves to off-site units, or to statutory credits at a price set nationally.

Programme suffers too. Off-site units have to be found, secured and registered on the national site register, and that is not a two-week exercise. On schemes where the land agent expected to buy units locally, the search often widens across the national character area and then into statutory credits, which sit deliberately above market price so that they are a last resort rather than a convenience.

The other consequences of clearing early

The metric is rarely the only problem. Clearance during the bird nesting season risks an offence. Hedgerow removal is regulated separately. Protected species can be present in scrub, buildings and hedgerows, and a protected species survey after the habitat has gone cannot establish what was there, which leaves an applicant unable to rule out an offence rather than able to prove one did not occur.

Then there is credibility. A case officer who believes a site was cleared to game the baseline reads every other document in the submission differently, and objectors will make sure the committee knows.

If the site has already been cleared

Do not present the site as it stands and hope.

  1. Establish the facts. Who cleared what, when, and under what consent if any.
  2. Commission a preliminary ecological appraisal that includes a documented reconstruction of the pre-clearance habitat rather than a survey of the current ground alone.
  3. Go to the authority's ecologist early, with the reconstruction and an explanation, rather than waiting to be challenged.
  4. Model the metric with the restored baseline and find out what it costs before the design is fixed.
  5. Identify off-site units or credits and check availability, because that is the long-lead item.
  6. Say plainly in the submission what happened and how the baseline was derived.

Applicants resist step three and it is the one that helps most. An authority presented with an honest reconstruction and a deliverable gain proposal has something it can approve. An authority that discovers the clearance from an objector's photographs has a reason to refuse.

For purchasers, the lesson is earlier still. Check historic imagery and ask about clearance before exchange, because the higher baseline comes with the land and no warranty reduces the price of the units you then have to buy.

You can browse the report types the scheme will need and start the supporting documents while the ecological position is being reconstructed.

This is general guidance, not legal advice; check the position with your local planning authority or a qualified professional before relying on it. The statutory metric is expected to be completed by a competent person, and an AI-assisted draft is a starting point for that professional rather than a substitute. PlanScope provides AI-assisted draft reports for planning applications. Reports should be reviewed before submission. We do not guarantee planning approval.

Frequently asked questions

What is the degradation provision in the biodiversity gain rules?

It is the backstop that stops a site being cleared to reduce its baseline. Where activities carried out on or after 30 January 2020, without planning permission or another required consent, reduced the biodiversity value of the onsite habitat, the pre-development value is taken as it was immediately before those activities.

Why is the date 30 January 2020?

It is the date the Environment Bill was introduced to Parliament, which put developers on notice that a mandatory gain regime was coming. Fixing the backstop there removes the incentive to clear land during the period between the announcement of the policy and the point at which the duty took effect.

Does the provision apply to lawful clearance?

No. Activities carried out under planning permission, or under another consent the legislation recognises, do not trigger the earlier baseline. Ordinary lawful agricultural operations are treated differently from clearance carried out to reduce a baseline, and the distinction is one the local planning authority will examine on the evidence.

Who has to prove what the habitat used to be?

In practice the applicant. Where the authority considers habitat was degraded after the date, the earlier value applies, and it falls to the applicant to establish either that no degradation occurred or that the clearance was consented. That means assembling imagery, records and survey evidence rather than asserting the site was always poor.

What if the site was cleared by a previous owner?

The provision looks at what happened on the land, not at who owned it. A purchaser can inherit the higher baseline, which is why historic aerial imagery and a site history check belong in due diligence before exchange rather than after. Ask the vendor directly and record the answer.

Sources and further reading

biodiversity net gaindegradationbaselinestatutory metricenforcementecology

This article is general guidance about the planning system in England and, where stated, the rest of the UK. It is not legal or professional advice. Check your local planning authority’s validation requirements and take professional advice for your specific site.

More in Ecology, BNG and Protected Species

View all →
Ecology, BNG and Protected Species7 min read

Local nature recovery strategies and the metric multiplier

A habitat identified in a local nature recovery strategy attracts a higher strategic significance multiplier. That makes the local habitat map a layout document, not a submission document.

Read article →
Ecology, BNG and Protected Species8 min read

Ancient woodland buffers and the evidence behind them

A 15 metre buffer of semi-natural habitat is the starting point, measured from the woodland edge rather than the inventory polygon. The pressures it addresses and the evidence that moves the figure.

Read article →
Ecology, BNG and Protected Species7 min read

SSSI impact risk zones and what they actually trigger

An impact risk zone is a consultation trigger, not a designation. How to check the layer on MAGIC and planning.data.gov.uk, read the development categories, and give Natural England what it needs first time.

Read article →
Ecology, BNG and Protected Species7 min read

When a preliminary appraisal becomes an impact assessment

The appraisal is a constraints document and the assessment judges effects on important features. Which triggers force escalation, how the survey calendar differs, and how to write the brief.

Read article →
Ecology, BNG and Protected Species7 min read

Programming a scheme around bat survey seasons

A preliminary roost assessment can be done in any month, but emergence and re-entry surveys are limited to the maternity season. Survey effort by roost potential, and how to keep the rest of the scheme moving.

Read article →
Ecology, BNG and Protected Species8 min read

The degradation rule and your biodiversity net gain baseline

Schedule 7A to the Town and Country Planning Act 1990 reverts the pre-development biodiversity value to its pre-clearance level where habitat was degraded after 30 January 2020.

Read article →