Ecology, BNG and Protected Species

Reptile surveys: refugia, visits and the temperature window

7 min readBy PlanScope Editorial Team

Reptile surveys depend on refugia, repeated visits and weather you cannot book. What makes a survey defensible, and what the results mean for the programme.

Reptile survey methodology in England rests on artificial refugia, repeated visits within a narrow season, and weather conditions that cannot be scheduled. Get any of those wrong and the survey does not support a conclusion of likely absence, which means the council will treat the risk as unassessed. On a site with rough grassland, south-facing banks, brash piles or an old railway margin, that is the difference between a decision this autumn and one next summer.

All four widespread British reptiles are protected against killing and injuring under the Wildlife and Countryside Act 1981. That protection applies whether or not the site has any designation.

Why reptiles need a presence or absence survey

Common lizard, slow-worm, grass snake and adder are protected under section 9 of the 1981 Act against intentional killing and injuring. Clearing habitat with a tracked machine will kill animals present, so the offence is a real one rather than theoretical.

Unlike great crested newts and bats, these four are not European protected species, so there is no licence to obtain. That is often misread as meaning there is nothing to do. What it actually means is that the developer carries the whole responsibility, without a licensing regime to confirm that the approach is acceptable.

The trigger is usually a Preliminary Ecological Appraisal identifying suitable habitat. Suitable habitat is not rare: tussocky grassland, scrub edges, hedge banks, brownfield mosaic, compost heaps, log piles and the margins of allotments all qualify. Where the appraisal finds it, a presence or likely absence survey follows.

A Protected Species Survey of this kind must be carried out by a suitably experienced ecologist, and where a European protected species is involved a licensed ecologist is legally required. Any AI-assisted draft is a starting point for that professional rather than a substitute for the survey.

Refugia type, density and placement

Refugia are artificial shelters that reptiles use for basking and cover, and which the surveyor lifts on each visit. Roofing felt and corrugated bitumen sheet are the usual materials, cut to a manageable size, because they warm quickly and hold heat.

Density and placement matter more than material. Published guidance sets a recommended number per hectare of suitable habitat, and the figures should be taken from that guidance rather than from a rule of thumb. What is consistent across every method is the reasoning: enough refugia to sample the habitat properly, distributed across the features that reptiles actually use rather than spread on an even grid.

Place them on south-facing and south-west-facing edges, at the boundary between short and long vegetation, against scrub margins and along linear features. Avoid fully shaded positions and avoid open mown grass. Where the site includes a bank, a rubble pile or a compost heap, cover those specifically.

Refugia need to settle before surveying starts, usually a couple of weeks, so that the vegetation beneath them has died back and animals have found them. Surveying on the day they are laid out produces nothing and wastes a visit.

Number them, map them, and photograph the layout. A survey report that cannot show where its refugia were is difficult to defend at appeal.

Visits and the survey season

The active season runs from around April to October, with the best results in April and May and again in September, when animals bask for longer because ambient temperatures are lower.

Presence or likely absence surveys use a minimum number of visits set by the published methodology, spread across suitable conditions rather than crammed into a fortnight. Where the aim is a population size class rather than presence alone, more visits are needed.

Period Survey value Practical notes
April to May High Peak basking, animals concentrated, best detection
June to August Lower Hot middays reduce refugia use, early starts needed
September High Second peak as temperatures fall
October Variable Weather dependent, tailing off
November to March Not valid Animals in hibernation

Plan the survey into the programme at the point you buy the site, not at the point you submit. Missing the spring window on a site with good habitat costs a season, and the same arithmetic applies to newts, as set out in newt trapping, fencing and the spring window.

Temperature and weather constraints

This is where survey programmes fail in practice. Reptiles use refugia when the air is warm enough to be active but not so warm that they can bask in the open, so the usable conditions are a band rather than a maximum.

Surveys are carried out when air temperature sits within the range the guidance gives, typically a mild spring or autumn morning or a late afternoon in summer. Overcast and still is often better than bright and breezy. Heavy rain, strong wind and hot midday sun all produce nil returns that mean nothing.

Record the conditions for every visit. Air temperature, cloud cover, wind, time of day, the surveyor's name and the result at each refugium. A report with a table of dates and no weather data cannot demonstrate that the visits were valid, and a consultee ecologist will say so.

And accept that visits get abandoned. A survey booked as six consecutive Tuesdays will lose two of them to weather. Build the contingency in.

Turning counts into a population class

Results are expressed as a population size class rather than as an estimate of the number of animals, because refugia counts sample a fraction of the population.

The assessment uses the peak adult count for each species across the visits, compared against thresholds in the published key. Those thresholds differ by species, so a count that indicates a low population of slow-worms may indicate a higher class for adder. Take the figures from the key itself rather than from memory or from an older report.

The class drives the mitigation. A low population on a small site may be handled by habitat manipulation and phased clearance under ecological supervision. A higher class, or the presence of adder, usually means a full capture and translocation exercise with fencing, a destructive search and a monitoring period.

Where the site supports a notable population, that is also a material consideration in its own right and will feed into the Biodiversity Net Gain Assessment and the wider ecological chapter rather than sitting in isolation.

Translocation and receptor site capacity

Translocation is not a licence exercise for these four species, but it is a technical one and it is where most schemes go wrong.

The receptor has to be suitable before animals arrive: the right habitat structure, hibernation features, connectivity, and a management arrangement that keeps it that way for the long term. It has to be secure from the development itself, from future phases, and from being mown flat by a grounds contractor who was never told.

Capacity is the constraint people underestimate. A receptor already holding a population cannot absorb another one without effect, and moving animals into unsuitable or occupied habitat achieves nothing for the animals or for the scheme. The selection questions are covered in reptile receptor sites: selection and capacity.

The capture programme itself runs over a defined number of trapping days in suitable weather, with a set of consecutive nil-capture days before clearance proceeds, a destructive search under supervision, and reptile-proof fencing maintained throughout. None of that is fast.

Conditions that follow from the results

Expect the ecological requirements to be secured by condition rather than left to good intentions. The common set is a method statement to be approved before any clearance, reptile fencing and its maintenance, supervision by a named ecologist, a timetable for capture and translocation, receptor site habitat works completed in advance, and a monitoring and reporting programme over several years.

Read the triggers. A condition requiring the receptor to be created and established before any site clearance can add a full growing season to the programme, and that is entirely reasonable ecologically. It is also something to know before the contractor's start date is agreed.

Where the site is large enough for phased development, agree a phasing plan with the ecologist and the council together, so that clearance, translocation and construction sequence properly across the seasons.

This is general guidance, not legal advice. Check the position with your local planning authority or a qualified professional before relying on it. PlanScope provides AI-assisted draft reports for planning applications. Reports should be reviewed before submission. We do not guarantee planning approval. To see which ecology documents your site is likely to need, enter your postcode on PlanScope.

Frequently asked questions

Do reptile surveys need a licence?

Common lizard, slow-worm, grass snake and adder are protected against killing and injuring under the Wildlife and Countryside Act 1981 but are not European protected species, so no survey or mitigation licence is issued for them. That places the responsibility wholly on the developer and the ecologist. Smooth snake and sand lizard are fully protected and do require licensing.

When can reptile surveys be carried out?

Within the active season, broadly April to October, with the strongest results in April and May and again in September when animals bask for longer. Surveys are invalid between November and March while animals are hibernating. Individual visits also depend on air temperature and weather, so a programme should allow for visits being abandoned and rescheduled.

How many survey visits are needed?

The published methodology sets a minimum number of visits for a presence or likely absence conclusion, with more required where a population size class is the aim. The visits must be spread across suitable conditions rather than compressed into a short period. Record air temperature, cloud, wind and time of day for each one, or the validity of the survey can be challenged.

What is a population size class?

Reptile results are reported as a size class rather than a count, because refugia sample only part of the population. The class comes from the peak adult count for each species compared against published thresholds, which differ between species. The class then drives the mitigation, from supervised phased clearance at the lower end to full capture and translocation at the higher end.

How long does translocation take?

Longer than most programmes allow. The receptor site habitat usually has to be created and established first, which can take a growing season. Capture then runs over a defined number of trapping days in suitable weather, followed by consecutive nil-capture days, a supervised destructive search and a monitoring period. Reptile fencing must be maintained throughout.

Sources and further reading

ecologyreptilesprotected speciessurveysbiodiversity

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.

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