Lighting design for bats and the lux limits that matter
Bat lighting limits are only enforceable if the plane, the point and the maintained condition are stated. What to specify, what to model and what to verify after installation.
External lighting is the measure most likely to undo otherwise sound bat mitigation, and it is the one most often left to a subcontractor after permission is granted. Light falling on a roost access point, a commuting hedgerow or a foraging corridor can amount to disturbance of a European protected species, which is a licensing matter as well as a planning one. The working target on retained features is very low illuminance, expressed in practice as a limit around 1 lux with lower figures where light-averse species are present.
Take the current figure from the joint guidance on bats and artificial lighting rather than from a previous scheme, because the guidance has been revised and the numbers are what conditions get written around.
Why lighting is a licensing issue as well as an amenity one
Bats and their roosts are protected under the Wildlife and Countryside Act 1981 and the Conservation of Habitats and Species Regulations 2017. Deliberate disturbance, and damage to or destruction of a breeding site or resting place, are offences, and illuminating a roost exit can constitute disturbance without anyone touching the building.
That is a separate question from obtrusive light for neighbours, which is assessed against amenity guidance on light trespass, sky glow and source intensity. The two assessments use different limits and different receptors, and a scheme can pass one comfortably while failing the other.
Species respond differently. Slow flying, light-averse species avoid lit areas entirely, which fragments a landscape rather than simply reducing its quality. Faster species will feed around lights, and that is not the benefit it appears to be, because it concentrates insects away from the wider habitat and exposes bats to predation.
Commuting routes, foraging habitat and roost access
Three receptor types need protecting, and they need different treatments.
Roost access points need darkness at and immediately outside the opening, during the emergence and return periods. Commuting routes, typically hedgerows, treelines, walls and watercourses, need a continuous dark corridor, because a single lit gap of a few metres can break a route that is otherwise unlit. Foraging habitat needs low ambient illuminance across the area rather than at a point.
The evidence for which features matter comes from the survey. A Preliminary Ecological Appraisal identifies the features, and activity data from the Bat Survey shows which of them are used and when. Designing a lighting scheme without that data means guessing which hedge to keep dark.
Illuminance limits applied in practice
Conditions and method statements normally express the requirement as a maximum illuminance at a defined plane. Three details make the difference between an enforceable limit and a meaningless one.
- State the plane. Horizontal illuminance at ground level and vertical illuminance at the face of a hedge or a roost access give very different numbers from the same luminaire.
- State the point. A limit at the boundary is not a limit at the roost entrance 6 metres above it.
- State the condition. Maintained illuminance including the maintenance factor, not initial values, since a scheme designed to a limit at initial output exceeds it for most of its life.
Where light-averse species have been recorded, expect the ecologist to ask for a lower figure and for wider dark buffers. That is a judgement for them to make on the survey evidence, and it should appear in the Protected Species Survey reasoning rather than being invented at lighting design stage.
Luminaire selection, optics and colour
The specification points that consistently matter are the ones a lighting designer can deliver without argument.
Use warm spectrum sources, with 2700 kelvin as a common upper limit and lower correlated colour temperatures preferred where sensitivity is high, because short wavelength light disturbs a wider range of species and scatters further. Specify luminaires with no upward light and flat glass optics rather than drop lenses. Mount them as low as the task allows, since a lower column with tighter optics lights the path and not the hedge behind it. Use accessories, meaning shields, louvres and baffles, to cut spill towards the feature, and show them on the schedule rather than describing them.
Position matters as much as product. Moving a column 3 metres and rotating the optic often achieves more than changing the luminaire, and it costs nothing at design stage.
One thing worth being honest about is the limit of what a lighting design can fix. Where a building sits hard against a commuting route and the route runs through the only sensible vehicle access, no luminaire specification will produce a dark corridor. The answer then is a layout change or a different route, decided at masterplanning stage, and an ecologist who says so early is worth more than one who agrees to model it again.
Curfews, dimming and part night regimes
Part night regimes are useful and frequently misapplied. A midnight switch-off does nothing to protect an emergence period that begins around sunset, which is when the roost is most sensitive.
If a time based control is being used to protect bats, the control has to target the sensitive period. Dimming profiles that reduce output during the first hours of darkness, presence detection on paths that are rarely used, and switching off decorative and feature lighting entirely outside occupied hours are all more useful than a late curfew. Say in the strategy what each control is for, because a control that protects energy use and a control that protects a commuting route are different things.
An illustrative example shows how small the fix usually is. A 60 unit scheme retains a hedgerow along its eastern boundary, recorded in the survey as a commuting route used from dusk. The first lighting layout puts 5 metre columns along the parking court with symmetric optics, and the model shows 4 lux at the hedge face. The revision drops the columns to 4 metres, switches to asymmetric optics with a rear shield, and moves three columns 4 metres west. The hedge face reads below 1 lux, the parking court still meets its task requirement, and the luminaire count is unchanged. This example is illustrative.
Modelling and what the drawings must show
Submit a lighting layout with a luminaire schedule giving make independent specification: output, optic, correlated colour temperature, upward light ratio, mounting height, tilt and accessories. Overlay the ecological constraints as a separate layer showing retained features, roost positions and required dark corridors.
Then submit isolux contours at the limits being applied, at the correct plane, including light from windows, glazed entrances, illuminated signage and vehicle headlights where these are predictable. A model that omits the glazed ground floor of the building it sits next to understates the result.
Securing and verifying the scheme
Ask for a condition requiring the lighting scheme, including the isolux drawing and the luminaire schedule, to be approved before installation, implemented as approved, and retained. Add a verification requirement: post-installation measurements at named points, taken after dark at stated locations and heights, submitted within a defined period of first use.
That verification step is what turns a drawing into a delivered outcome. It also catches the common failure, which is a specification substitution made on cost grounds between approval and installation. Where the residual effect on the local population still needs to be judged, the framework for that is the same one used for significance of effects generally.
Surveys, licensing and mitigation design for bats require a suitably licensed ecologist under the Wildlife and Countryside Act 1981 and the Conservation of Habitats and Species Regulations 2017. A drafted lighting and mitigation narrative is a starting point for that professional and never a substitute.
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. For specialist technical reports, qualified professional input may be required.
Frequently asked questions
What lux limit applies to lighting near bats?
The working target on retained features is very low illuminance, commonly expressed as a limit around 1 lux and lower where light-averse species are present. Take the current figure from the joint guidance on bats and artificial lighting rather than an earlier scheme, and have the ecologist set the figure from the survey evidence.
Is a midnight curfew enough to protect bats?
No. Emergence begins around sunset, so a late switch-off does nothing for the most sensitive period. Controls that help are dimming profiles reducing output during the first hours of darkness, presence detection on lightly used routes, and switching decorative and feature lighting off entirely outside occupied hours.
What colour temperature should external lighting use?
Warm spectrum sources, with 2700 kelvin commonly applied as an upper limit and lower correlated colour temperatures preferred where sensitivity is high. Blue rich light disturbs a wider range of species and scatters further in the atmosphere. Specify the correlated colour temperature on the luminaire schedule so it survives value engineering.
How should a lighting condition be worded?
Require the lighting scheme, including the isolux drawing and a luminaire schedule, to be approved before installation, implemented as approved and retained. Add a verification requirement for post-installation measurements at named points and heights, submitted within a defined period of first use, which catches specification substitutions made after approval.
Does bat lighting assessment replace an obtrusive light assessment?
No. Obtrusive light guidance addresses amenity receptors through light trespass, sky glow and source intensity limits, while bat guidance addresses ecological receptors at roost accesses, commuting routes and foraging habitat. The limits and the receptors differ, and a scheme can satisfy one while failing the other.
Sources and further reading
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.