Solar farms across the UK are home to a remarkable variety of wildlife. National surveys coordinated by Solar Energy UK have recorded 94 bird species, 29 butterfly and bumblebee species, and 8 mammal species across 124 solar sites. Over 50% of surveyed solar farms host red-listed birds including skylark, yellowhammer, linnet, corn bunting, and nightingale. Brown hares, a species of conservation concern, are found on around 40% of sites, while the small heath butterfly and cinnabar moth have been recorded at multiple locations.
Research from the RSPB and University of Cambridge confirms that well-managed solar farms support up to three times more birds than intensive arable farmland. Lancaster University studies show bumblebee populations up to four times higher on sites managed as wildflower meadows. These findings reflect the fundamental change that occurs when land shifts from intensive agriculture to the low-disturbance environment of a solar farm, free from pesticides, fertilisers, and regular ploughing for 25-30 years.
This guide catalogues the wildlife found on UK solar farms, explains why these sites support diverse species, identifies which animals benefit most, and addresses concerns about potential negative impacts on certain wildlife like bats. Whether you are a conservation professional, a landowner considering solar development, or simply curious about what lives among the panels, this guide provides the complete picture.
Quick Overview
| Bird species recorded | 94 species (Solar Habitat 2025) |
| Red-listed birds observed | 20% of species; 50%+ of sites |
| Average birds per solar farm | 86 individuals (up to 238) |
| Butterfly and bumblebee species | 29 species; ~3,000 individuals |
| Mammal species | 8 species recorded |
| Sites surveyed (2025) | 124 solar farms |
Birds on Solar Farms
Survey Findings
| Metric | Solar Habitat 2025 Data |
|---|---|
| Solar farms surveyed | 63 (bird surveys) |
| Total species recorded | 94 |
| Individual birds counted | ~7,500 |
| Average per site | 86 birds |
| Maximum at one site | 238 birds |
| Species range per site | 9-39 species |
Conservation Status of Birds Found
| Status | Share of Species | What It Means |
|---|---|---|
| Red-listed | 20% | Most endangered; urgent conservation concern |
| Amber-listed | 28% | Medium conservation concern |
| Green-listed | 52% | Not of conservation concern |
Red-Listed Birds on Solar Farms
| Species | Prevalence | Notes |
|---|---|---|
| Skylark | Common; ~50% of sites | Ground-nesting; iconic farmland bird |
| Yellowhammer | Common; ~50% of sites | Hedgerow specialist; seed-eater |
| Linnet | Common; 50%+ of sites | Small finch; beautiful song |
| Starling | Regular | Feeding flocks; invertebrate-eater |
| Corn bunting | Occasional | East Anglia; declining heavily |
| Cirl bunting | Rare | UK’s rarest resident farmland bird; Devon only |
| Nightingale | Rare | Possible breeding at one site |
| Spotted flycatcher | Occasional | Summer visitor; insect-eater |
Amber-Listed Birds
| Species | Habitat Use |
|---|---|
| Grey wagtail | Near water features; ponds |
| Whitethroat | Hedgerows; scrub |
| Wren | Dense vegetation; margins |
| Willow warbler | Scrub; hedgerows |
| Dunnock | Hedgerows; ground layer |
Why Solar Farms Support Birds
| Factor | Benefit for Birds |
|---|---|
| No pesticides | Abundant invertebrate prey |
| Undisturbed ground | Safe nesting for ground-nesters |
| Hedgerows | Nesting sites; food; shelter |
| Seed-rich vegetation | Winter food source |
| Fenced perimeter | Reduced predator access |
| Low human disturbance | Breeding success improved |
Bird Abundance by Habitat Type
| Habitat | Predicted Birds per 4ha |
|---|---|
| Solar farm (mixed habitat) | 31.5 birds |
| Solar farm (simple habitat) | 17 birds |
| Arable farmland | 11.9 birds |
Mammals on Solar Farms
Species Recorded
| Species | Prevalence | Conservation Status |
|---|---|---|
| Brown hare | 40% of sites; most common | Species of conservation concern |
| Roe deer | Regular | Common |
| Fallow deer | Occasional | Common |
| Muntjac deer | Occasional | Common (non-native) |
| Badger | Regular | Protected |
| Fox | Regular | Common |
| Rabbit | Common | Common |
| Common shrew | Present but under-recorded | Common |
| Field vole | Present but under-recorded | Common |
| Water vole | Rare; where ponds present | Endangered |
| Weasel | Occasional | Common |
Brown Hares
| Aspect | Details |
|---|---|
| Prevalence on solar farms | 40% of surveyed sites; most common mammal |
| Conservation status | Species of Principal Importance (NERC Act 2006) |
| Population trend | UK population declined 75%+ since 1960s |
| Why solar farms suit them | Low disturbance; diverse vegetation; safe from agricultural machinery |
| Survey note | “Solar farms offer ideal habitats for this declining species” |
Small Mammals
| Species | Habitat | Notes |
|---|---|---|
| Field vole | Tussocky grassland | Key prey for owls and kestrels |
| Bank vole | Hedgerows; margins | Likely present; under-recorded |
| Wood mouse | Margins; hedgerows | Likely present; under-recorded |
| Common shrew | Ground layer; dense vegetation | Recorded at some sites |
| Harvest mouse | Tall grass; margins | Potential; requires survey |
Why Small Mammals May Be Under-recorded
| Factor | Explanation |
|---|---|
| Survey timing | Daytime surveys miss nocturnal species |
| Visibility | Small mammals hidden in vegetation |
| Survey methods | Standard monitoring doesn’t include trapping |
| Likely reality | Small mammal populations probably higher than recorded |
Invertebrates on Solar Farms
Survey Findings
For a deep dive on the pollinator side of solar farm biodiversity, see our guide to pollinator-friendly solar farms – which covers bumblebee and butterfly management in more detail.
| Metric | Solar Habitat 2025 Data |
|---|---|
| Butterfly and bumblebee species | 29 |
| Individual insects counted | ~3,000 |
| Total invertebrate species | 47 |
| Groups recorded | Butterflies, bumblebees, moths, dragonflies, solitary bees |
Butterflies
| Species | Status | Notes |
|---|---|---|
| Meadow brown | Common | Most frequently recorded species |
| Small heath | Species of Principal Importance | Found at 10+ sites; declining nationally |
| Ringlet | Common | Grassland specialist |
| Gatekeeper | Common | Hedgerow edges |
| Common blue | Common | Where bird’s-foot trefoil present |
| Small skipper | Common | Grassland; margins |
Bumblebees
| Finding | Source |
|---|---|
| 4x higher density on wildflower-managed sites | Lancaster University |
| 2x higher foraging and nesting | Compared to wildflower margins only |
| Benefit to surrounding crops | Enhanced pollination within 1km radius |
| Future refuge potential | Could support populations under land-use change |
Moths
| Species | Status | Notes |
|---|---|---|
| Cinnabar moth | Species of conservation concern | Recorded at 7+ sites |
| Six-spot burnet | Common | Day-flying; grassland |
| Various nocturnal moths | Mixed | Under-recorded; night surveys rare |
Dragonflies and Damselflies
| Species | Status | Notes |
|---|---|---|
| Norfolk hawker | Rare; protected | Recorded where ponds present |
| Scarce chaser | Rare | Associated with ponds |
| Common darter | Common | Where water features exist |
| Blue-tailed damselfly | Common | Pond margins |
Why Solar Farms Support Invertebrates
| Factor | Benefit |
|---|---|
| No pesticides | Insect populations not suppressed |
| Wildflowers | Nectar and pollen sources |
| Varied vegetation structure | Different niches for different species |
| Undisturbed soil | Ground-nesting bees can establish |
| Ponds | Aquatic invertebrates; dragonflies |
| Log piles | Beetle habitat; overwintering sites |
Reptiles and Amphibians
Reptiles
| Species | Status | Solar Farm Habitat |
|---|---|---|
| Slow worm | Protected | Margins; log piles; compost heaps |
| Grass snake | Protected | Margins; near ponds; egg-laying sites |
| Common lizard | Protected | South-facing banks; log piles |
| Adder | Protected | Possible on heathland-adjacent sites |
Amphibians
| Species | Status | Solar Farm Habitat |
|---|---|---|
| Great crested newt | European Protected Species | Ponds; terrestrial habitat within 500m |
| Smooth newt | Protected | Ponds; damp margins |
| Common toad | Species of Principal Importance | Breeding ponds; terrestrial habitat |
| Common frog | Protected | Ponds; wet margins |
Great Crested Newts on Solar Sites
| Aspect | Details |
|---|---|
| Legal protection | Wildlife and Countryside Act; Conservation of Habitats Regulations |
| Pre-construction surveys | Required if ponds within 500m |
| Solar farm benefit | Undisturbed terrestrial habitat; new ponds can be created |
| Case study example | One site described as potential “newt haven” |
| District Level Licensing | Strategic approach available in England |
Why Solar Farms Suit Reptiles and Amphibians
| Factor | Benefit |
|---|---|
| No ploughing | Hibernation sites undisturbed |
| Varied microclimates | Basking spots; shaded areas |
| Pond creation | Breeding habitat for amphibians |
| Log piles | Shelter; egg-laying for grass snakes |
| Tussocky margins | Cover from predators |
Bats: A Mixed Picture
Research Findings
| Study | Finding |
|---|---|
| University of Bristol (2023) | Bat activity lower at solar farm sites than control sites |
| Bat Conservation Trust | Collecting evidence on impacts; research ongoing |
| Potential concern | Panels may disrupt foraging; confusion with water |
Why Bats May Avoid Solar Farms
| Theory | Explanation |
|---|---|
| Smooth surface confusion | Bats may mistake panels for water |
| Reduced insect availability | Possible; though other studies show more insects |
| Habitat fragmentation | Panels may interrupt flight paths |
| Acoustic interference | Possible echolocation disruption (unconfirmed) |
Mitigation for Bats
| Measure | Purpose |
|---|---|
| Dark corridors | Unlit flight paths through/around site |
| Hedgerow connectivity | Maintain linear features for commuting |
| Insect-friendly planting | Boost prey availability |
| Tree retention | Roosting opportunities |
| Buffer zones | Distance from known roosts |
Automated Monitoring
| Development | Details |
|---|---|
| Trial site | Westmill Solar Park, Oxfordshire |
| Lead | Lancaster University |
| Monitoring | Automated detection of bats, birds, invertebrates |
| Benefit | More frequent data than annual surveys |
Case Studies
Sawmills Solar Farm, Devon: Cirl Buntings
| Aspect | Details |
|---|---|
| Species | Cirl bunting (UK’s rarest resident farmland bird) |
| Range | Only found in small area of South Devon and Cornwall |
| Outcome | Successfully attracted to solar farm |
| Management | Targeted habitat creation for species requirements |
South Devon Solar Farm: Butterflies
| Aspect | Details |
|---|---|
| Finding | 40-fold increase in butterflies observed |
| Management | Wildflower meadow; conservation grazing |
| Timeframe | Several years post-installation |
East Anglian Fens Study
| Aspect | Details |
|---|---|
| Study | RSPB/University of Cambridge (2025) |
| Sites | 6 solar farms; 23.2km of transects |
| Finding | 3x more birds on mixed-habitat solar vs arable |
| Species | Corn bunting, yellowhammer, linnet observed |
Wildlife Monitoring
Standardised Approach
| Aspect | Details |
|---|---|
| Framework | Standardised Approach to Monitoring Biodiversity on Solar Farms |
| Developer | Solar Energy UK; Lancaster University |
| Purpose | Consistent methodology; comparable data |
| Uptake | 124 sites reported data in 2025 |
Survey Methods
| Group | Method |
|---|---|
| Birds | Breeding Bird Survey transects; point counts |
| Butterflies/bees | Transect walks in suitable weather |
| Plants | Quadrat surveys (1m²) |
| Mammals | Incidental records; camera traps emerging |
| Reptiles | Artificial refugia surveys |
Future Monitoring Developments
| Development | Status |
|---|---|
| Automated acoustic monitoring | Being trialled for bats, birds |
| Camera traps | Increasing use for mammals |
| eDNA | Potential for pond surveys |
| Research-intensive sites | Proposed for more detailed study |
Management for Wildlife
High-Value Practices
If you’re a farmer or landowner considering whether to host a solar farm, see our guide to solar panels for farms – it covers lease terms and the wider agricultural context alongside biodiversity management.
| Practice | Wildlife Benefit |
|---|---|
| Wildflower meadow creation | Pollinators; seed-eating birds |
| Hedgerow planting | Nesting birds; mammals; connectivity |
| Pond creation | Amphibians; dragonflies; water birds |
| Conservation grazing | Varied sward; dung invertebrates |
| Tussocky margins | Small mammals; reptiles; ground-nesters |
| Log piles | Invertebrates; reptiles; fungi |
Management Categories and Wildlife
| Category | Invertebrate Richness | Bird Richness |
|---|---|---|
| Category 2 (strong focus) | Highest | Highest |
| Category 3 (some consideration) | Medium | Medium |
| Category 4 (basic only) | Lower | Lower |
Seasonal Considerations
| Season | Wildlife Activity | Management Notes |
|---|---|---|
| Spring | Bird nesting; amphibian breeding | Avoid disturbance; delay cutting |
| Summer | Peak invertebrates; fledglings | Allow flowering; minimal mowing |
| Autumn | Seed set; migration; dispersal | Conservation grazing can begin |
| Winter | Overwintering; limited activity | Maintain cover; sheep grazing |
Concerns and Considerations
Potential Negative Impacts
| Concern | Evidence | Mitigation |
|---|---|---|
| Bat activity reduction | Bristol study shows lower activity | Dark corridors; hedgerow connectivity |
| Construction disturbance | Temporary during build | Seasonal timing; ecological supervision |
| Panel reflection | Possible confusion for some species | Anti-reflective coatings available |
| Fencing barriers | May block some mammal movement | Gaps for small mammals; badger gates |
Sites to Avoid
| Site Type | Reason |
|---|---|
| SSSIs | Already high nature value |
| Important bird areas | Critical for specific species |
| Ancient woodland | Irreplaceable habitat |
| Species-rich grassland | Already biodiverse |
| Active breeding sites | Rare species; protected |
Pre-Construction Surveys Required
Water-based solar projects face a different set of ecological questions from the ground-mount sites covered here. Our guide to floating solar farms covers the wildlife and habitat implications for reservoirs and other water bodies.
| Survey | When Required |
|---|---|
| Great crested newt | Ponds within 500m |
| Bat roost assessment | Trees/buildings affected |
| Breeding bird survey | All sites |
| Reptile survey | Suitable habitat present |
| Badger survey | All sites |
Frequently Asked Questions
Basic Questions
| Question | Answer |
|---|---|
| Do solar farms harm wildlife? | Well-managed solar farms support more wildlife than intensive farmland |
| What animals live on solar farms? | 94 bird species, 8 mammals, 29 butterfly/bee species recorded |
| Are rare species found on solar farms? | Yes; 20% of bird species are red-listed; cirl buntings at one site |
| Do bats use solar farms? | Research shows lower activity; mitigation recommended |
Management Questions
| Question | Answer |
|---|---|
| What management is best for wildlife? | Wildflower meadows; hedgerows; conservation grazing; ponds |
| How is wildlife monitored? | Standardised surveys; 124 sites reported in 2025 |
| Can wildlife surveys be required? | Yes; BNG requires 30-year monitoring |
Summary
| Wildlife Group | Key Finding |
|---|---|
| Birds | 94 species; 3x more than arable; 20% red-listed |
| Mammals | 8 species; brown hare on 40% of sites |
| Butterflies/bees | 29 species; 4x more bumblebees with good management |
| Reptiles/amphibians | Benefit from undisturbed habitat; pond creation helps |
| Bats | Potential concern; lower activity recorded; mitigation needed |
| Overall | Well-managed solar farms support significant wildlife populations |
Solar farms across the UK are proving to be important refuges for wildlife, particularly in landscapes dominated by intensive agriculture. The Solar Habitat 2025 report documented 94 bird species, including red-listed skylark, yellowhammer, linnet, and even the rare cirl bunting and nightingale. Brown hares, a species of conservation concern that has declined by over 75% since the 1960s, are found on 40% of surveyed solar farms. Nearly 3,000 butterflies and bumblebees representing 29 species were recorded, with bumblebee densities up to four times higher on well-managed sites.
The key to wildlife success on solar farms is management rather than the panels themselves. Sites managed as wildflower meadows with hedgerows and conservation grazing support far more species than those maintained as simple turf grass. The RSPB/Cambridge study found that mixed-habitat solar farms supported nearly three times as many birds as nearby arable farmland. This reflects the fundamental shift from intensive agriculture to a low-disturbance environment free from pesticides, fertilisers, and annual ploughing.
Not all wildlife responds equally to solar farms. While most groups benefit, research from the University of Bristol suggests bat activity may be lower at solar farm sites, possibly due to panel reflections confusing echolocation. This highlights the importance of mitigation measures including dark corridors, hedgerow connectivity, and maintaining links to known roosts. Ongoing automated monitoring trials at sites like Westmill Solar Park will help build understanding of these effects.
With over 50% of surveyed solar farms now hosting red-listed birds and clear evidence linking biodiversity-focused management to wildlife abundance, solar farms are emerging as accidental nature reserves. As the Biodiversity Net Gain requirement embeds long-term monitoring and habitat management into planning conditions, this wildlife potential is increasingly being realised by design rather than by accident.
The biodiversity case for solar farms is strongest when paired with active habitat management – wildflower meadows, hedgerows, ponds, conservation grazing. For a farmer or landowner, this isn’t a bolt-on; it’s part of why a solar lease can be more nature-positive than continuing with intensive arable or dairy on marginal land.
If you’re evaluating community-scale solar or considering investment in a project, our guide to community solar projects covers how ownership models affect management choices – cooperatives and community-benefit societies often prioritise biodiversity outcomes more than purely commercial developers.