Ecological Surveys

Ecological Surveys

Ecology establishes the framework within which development can proceed, shaping planning outcomes from the outset.

Local planning authorities require robust ecological evidence where development may affect habitats or protected species. Early assessment identifies site constraints highlighting any seasonal or policy requirements.

We conduct the surveys necessary to address those constraints. Reporting is structured and defensible, resulting in clear evidence to support timely planning decisions.

Which Ecological Surveys Do I Need?

A Quick Guide

Most planning applications that affect greenfield land, buildings, trees or water features trigger ecological survey requirements.

Use the guide below to identify the survey stage most likely to apply to your scheme.

Preliminary Ecological Appraisal (PEA)

When: preparing a planning application or where boundaries include vegetation or mixed habitats.

Purpose: establish the ecological baseline early.

Timing: year-round.

Botanical Surveys

When: grassland, wetland or species-rich vegetation influences BNG or design.

Purpose: confirm species composition and habitat distinctiveness. 

Timing: May – September.

Habitat Action Plans (HAP)

When: long-term habitat management or enhancement is required by planning conditions.

Purpose: structure post-planning habitat delivery and BNG stewardship.

Timing: year-round once baseline data exists.

Species Action Plans (SAP)

When: protected or priority species are recorded or predicted.

Purpose: formalise mitigation, enhancement and monitoring actions.

Timing: year-round (plans informed by seasonal survey data).

Trees visible across a wide landscape, illustrating baseline environmental features relevant to an Environmental Impact Assessment.

Environmental Impact Assessment (Ecology)

When: schemes meet EIA thresholds or affect designated habitats.

Purpose: provides the ecology chapter for Environmental Statements.

Timing: Season-dependent — scope early to avoid delays.

Ecological Clerk of Works (ECoW)

When: development enters construction and ecological conditions, licences or RAMS apply. 

Purpose: oversee site activity so ecological requirements are followed in practice, not just on paper. 

Timing: year-round. 

Your Next Step

If you are uncertain which survey applies, we can review your proposal and advise on the appropriate next step.

Ecological Surveys FAQs

What is an ecology survey?

An ecology survey assesses how a proposed development interacts with habitats and protected species. It establishes the ecological baseline required for a planning application and determines whether further surveys or assessments are necessary.

Most projects begin with a Preliminary Ecological Appraisal (PEA), which identifies site constraints and defines the appropriate next steps.

You may need an ecology survey for planning permission where development could affect habitats or protected species. Local planning authorities require ecological evidence to validate applications and assess environmental impact.

Depending on the scale and sensitivity of the project, this may include a PEA, targeted protected species surveys, a Botanical Survey, or an Ecological Impact Assessment (EcIA).

An ecology survey typically begins with a Preliminary Ecological Appraisal (PEA), including habitat mapping and assessment of protected species potential.

Where required, this may progress to:

  • Targeted species surveys

  • A Botanical Survey

  • An Ecological Impact Assessment (EcIA) for larger or more complex schemes

Each stage is defined by site evidence and planning requirements.

An Ecological Impact Assessment (EcIA) is required where development is likely to result in significant ecological effects. It evaluates impacts, proposes mitigation measures and supports planning decision-making on larger or environmentally sensitive projects.

An Ecological Clerk of Works (ECoW) provides on-site ecological supervision during construction. This ensures works comply with planning conditions, method statements and protected species requirements.

ECoW support reduces risk during site operations and helps contractors meet environmental obligations.

What is a Botanical Survey?

A Botanical Survey records plant species and habitat composition within a site. It may be required where habitat quality, Biodiversity Net Gain calculations or designated plant communities are relevant to planning.

Species Action Plans (SAP) and Habitat Action Plans (HAP) set out long-term management measures to protect or enhance ecological features. They may form part of mitigation strategies or planning conditions where biodiversity enhancement is required.

The cost of an ecology survey depends on site size, habitat type and whether additional assessments such as a Botanical Survey, EcIA or protected species surveys are required. Early ecological input helps define requirements clearly and manage cost.

Ecology survey reports, including PEAs and EcIAs, are generally considered valid for up to two years, provided site conditions have not materially changed. Planning authorities may request updated surveys where necessary.

Ecological surveys provide the evidence required for planning validation and decision-making. They identify environmental risks early, inform mitigation design and support Biodiversity Net Gain requirements.

Without appropriate ecological evidence, applications may be delayed or subject to additional information requests.

Japanese Knotweed Identification and Removal

Japanese Knotweed Identification & Removal

Planning-ready Japanese knotweed reports that confirm presence, clarify liability and enable proportionate removal — delivered nationwide by qualified specialists. 

Do you need a Japanese knotweed report?

You may need a Japanese knotweed report if the plant has been recorded on your property or a neighbouring site, or if an insurer, lender or planning authority requires formal evidence of identification, extent or management. 

These reports provide the independent documentation needed for legal, mortgage, or planning purposeswith clear next steps for remediation. 

Most clients tell us early clarity here prevented prolonged lender delays and avoided unnecessary escalation. 

Japanese Knotweed with flowers to demonstrate in training session

What is Japanese knotweed?

Japanese knotweed is one of the UK’s most invasive plants, introduced from Japan for ornamental use in the 19th century. 

It spreads rapidly through underground rhizomes, growing up to 10 cm per day during the growing season. Its roots can penetrate structures, drains and cavity walls, creating significant management challenges. 

Although it’s not illegal to have knotweed on your property, landowners have a legal responsibility to prevent it spreading onto neighbouring land under the Wildlife & Countryside Act 1981 (Schedule 9) and relevant local authority policies. 

Unchecked growth can: 

  • cause damage to buildings, drains and hard surfaces 
  • delay planning or property transactions 
  • lead to enforcement or legal action 
  • reduce property value by 5–15 % depending on severity 
Japanese Knotweed

What is a Legal Report: Japanese Knotweed?

Legal Knotweed Report provides formal identification, mapping, and legal context for any infestation. 

It evidences presence, source and spread, and defines the remedial actions required under law or policy. 
Reports are structured for CPR Part 35 compliance when used in litigation or insurance cases, or as advisory documents for planning and conveyancing. 

Our legal and technical reports often lead directly to remediation through our specialist partners at Japanese Knotweed Expert, ensuring continuity from evidence to action nationwide. 

Quick check: 
Send your postcode, site plan or photographs for a fast, accurate recommendation. 

Surveyor from Japanese Knotweed Expert inspecting vegetation for Japanese knotweed and Points to Roots symptoms.

Legal Compliance & Planning risk

Authorities, lenders and courts rely on qualified evidence under:

  • Civil Procedure Rules (CPR) Part 35 
  • Wildlife & Countryside Act 1981 (Schedule 9) 
  • Environment Act 2021 
  • Anti-Social Behaviour, Crime and Policing Act 2014 (Community Protection Orders) 
  • National Planning Policy Framework Section 15 

Failure to document or manage knotweed correctly can result in:

  • mortgage refusals or reduced valuations 
  • planning delays or enforcement notices 
  • neighbour disputes or civil claims 
  • increased removal costs due to regrowth 

Early alignment with these standards ensures your authority, lender or insurer receives clear, compliant evidence from the first submission — no second rounds required. 

What We Deliver

Service Purpose Outcome
Initial Site Survey Confirm presence and extent of infestation. Fast confirmation and mapped evidence.
Formal Identification & Mapping Record species, boundaries and growth potential. Independent, photographic documentation.
Legal Report (CPR Part 35 or advisory) Present findings for legal, mortgage or planning use. Structured, defensible report ready for submission.
Remediation Plan & Verification Define safe and proportionate treatment or removal steps. Clear pathway from evidence to eradication.
Expert Witness Support (if required) Provide independent opinion for disputes or litigation. Compliant testimony and cross-examinable evidence.

That’s how evidence stays proportionate, liability stays contained, and your project keeps moving. 

How it Works

Scope & Confirm Instruction

Send your location and brief description of the issue. We confirm the correct report type and timescale..

Site Inspection & Evidence Collection

A qualified consultant inspects, photographs and maps the infestation, recording associated risks.

Report & Next Steps

You receive a planning- or court-formatted report, with mapped data and remediation pathway through our Japanese Knotweed Expert partners.

Timing & delivery

Each day gained here protects programme stability and prevents legal or transactional delay. 

Nationwide coverage across England, Scotland and Wales 

Inspection Availability

Year-round

Report Turnaround

Typically within 24 hours

Survey Booking

Within 7 working days

What You Receive:

  • Independent on-site identification and mapping 
  • Legal compliance check and liability summary 
  • Proportionate remediation plan 
  • CPR Part 35 or advisory format report 
  • 24-hour turnaround from inspection 
  • Full coordination with Japanese Knotweed Expert for removal 

Evidence lenders, planners and courts trust. 
Reasoning that keeps your project or transaction moving. 

Why Clients Choose ProHort:

  • Integrated ecological, legal and environmental expertise 
  • Reports accepted by lenders, solicitors and insurers 
  • 24-hour reporting with national coverage 
  • Partnership with Japanese Knotweed Expert for seamless remediation 
  • Transparent communication and defensible reasoning 

Compliance & professional standards

Reports produced in accordance with: 

• CPR Part 35 and RICS practice standards 

• Wildlife & Countryside Act 1981 (Schedule 9) 

• Environment Act 2021 

• NPPF Section 15 

• ProHort Quality Assurance and peer review protocols 

Each report is structured for traceability, proportionality and defensible reasoning. 

Your Next Step

Need a P35 Expert Witness Report in relation to Japanese Knotweed? Contact us today:

Phone: 0800 494 7479 
Email: [email protected] 

Case Note

A buyer’s solicitor requested a knotweed assessment before mortgage approval. The inspection confirmed limited growth on a boundary and no structural impact. A 12-month treatment plan was agreed through Japanese Knotweed Expert, and the sale completed without delay.

Japanese Knotweed FAQs

Do I need a Japanese knotweed report?

Yes — if the plant has been recorded on or near your property, or a lender, solicitor or planner has requested formal evidence.

Yes. Reports can be formatted to CPR Part 35 standards for litigation, or advisory for planning and property transactions.

Reports are typically turned around within 24 hours of inspection.

Surveys are usually available within 7 working days from your initial call.

Will you arrange removal or treatment?

Yes — we coordinate with our specialist partners at Japanese Knotweed Expert for proportionate remediation.

Can this affect property value or mortgage offers? 
Yes — uncontrolled knotweed can reduce property value by 5–15 %, and many lenders require evidence of a treatment plan before approving finance. 

Yes — with consent, we provide reports directly to your representatives for transparency and speed.

Yes — services available across England, Scotland and Wales.

Related Services

Biodiversity

Biodiversity Net Gain

Effective Biodiversity Net Gain delivery is determined at the earliest stages of scheme design.

By working with you from the outset, we can reduce the need for additional Biodiversity Net Gain (BNG) units and support a cost-effective approach. Actions taken before baseline assessment, including habitat clearance, can negatively affect unit calculations and lead to increased mitigation requirements.

 

Our team clarifies what is required, when it is needed and how it integrates with your wider scheme, keeping progress proactive rather than reactive. The result is a thorough, evidence-led report that stands up to local planning authorities and supports approval at first submission.

What Biodiversity Survey Do I Need?

A Quick Guide

The majority of planning applications trigger formal Biodiversity Net Gain requirements.


Use the guide below to match your site conditions to the survey most likely to apply.

Biodiversity Net Gain (BNG) Assessment

When: development must achieve or evidence ≥ 10 % gain.

Purpose: quantify ecological change and define uplift routes.

Timing: baseline year-round.

Biodiversity Gain Plan (BGP)

When: after baseline/BNG assessment, once layout and habitat proposals are broadly fixed.

Purpose: set out how required BNG units will be delivered, managed and secured.

Timing: usually post-permission, pre-commencement to discharge BNG conditions.

Biodiversity Enhancement Plans

When: where planning policy or a planning condition requires biodiversity improvements as part of the development.

Purpose: explain what ecological enhancements will be delivered, how they will be put in place and how they will be maintained over time.

Timing: usually submitted with the planning application or approved by condition before development begins.

Habitat Management and Monitoring Plan (HMMP)

When: once BGP or BNG strategy is agreed and habitats are defined.

Purpose: detail how habitats will be managed, monitored and reported on for a duration of 30 years.

Timing: typically required alongside or shortly after the BGP for condition discharge.

Your Next Step

Do you require a BNG assessment, or related service? Call us today to book in one of our licenced ecologists.

Biodiversity FAQs

What is Biodiversity Net Gain in planning?

Biodiversity Net Gain (BNG) is a statutory planning requirement in England that requires most developments to deliver at least a 10% increase in biodiversity value compared to the site’s baseline condition. It is measured using the Government’s Biodiversity Metric and must be secured for a minimum of 30 years through approved habitat creation or enhancement.

Biodiversity Net Gain applies to most planning applications submitted under the Town and Country Planning Act in England. The requirement is triggered at the point of planning permission and must account for all habitats affected by the proposal, including distinct habitat types and their condition. A Biodiversity Gain Plan must then be approved before development can lawfully commence.

Developers must demonstrate a minimum 10% net gain in biodiversity units compared to the pre-development baseline. This requires a metric calculation, clear habitat proposals and a secured management commitment for at least 30 years. The gain must follow the statutory mitigation hierarchy and be formally approved by the local planning authority.

The Biodiversity Metric is a standardised calculation tool published by the Government. It measures the biodiversity value of a site based on habitat type, condition, distinctiveness and area. The metric is used to quantify losses and gains in biodiversity units and determine whether the 10% requirement has been achieved.

BNG units are the quantified measure of biodiversity value calculated using the Biodiversity Metric. They represent the ecological value of habitats before and after development. Planning approval requires the post-development unit total to exceed the baseline by at least 10%.

What is a Biodiversity Gain Plan (BGP)?

A Biodiversity Gain Plan is the formal document submitted to the local planning authority to demonstrate how a development will achieve the required 10% biodiversity net gain. It sets out the baseline metric calculation, proposed habitat delivery, and how gains will be secured for at least 30 years. Development cannot lawfully commence until the Biodiversity Gain Plan has been approved.

A Habitat Management and Monitoring Plan outlines how newly created or enhanced habitats will be established, maintained and monitored over the required 30-year period. It defines management actions, performance indicators and reporting intervals to ensure biodiversity gains are delivered in practice, not just on paper.

A Biodiversity Enhancement Plan sets out practical measures to improve ecological value within a site. On smaller developments or where full BNG does not apply, it may be required as a planning condition. The plan focuses on achievable, site-specific enhancements such as habitat creation, native planting or integrated features for protected species.

Certain developments are exempt, including householder applications, some self-build projects, and sites impacting very small areas of habitat below defined thresholds. However, exemptions are specific and should be confirmed early, as most standard development proposals remain subject to BNG.

If sufficient biodiversity gain cannot be delivered within the red line boundary, off-site biodiversity units can be secured from an approved provider. These units must be formally allocated and legally secured before development proceeds. Statutory credits are available only where on-site and off-site options are not feasible.

Landscape Architecture

Landscape Architecture

Landscape decisions influence planning outcomes and long-term site value.

Strategic landscape architecture integrates visual impact assessment, 3D design modelling and detailed scheme preparation to support both planning approval and successful delivery. LVIA establishes visual context and sensitivity. 3D landscape design communicates intent clearly. Landscaping schemes translate strategy into buildable detail.

We structure landscape input around policy, context and programme requirements from the outset. The result is a coherent landscape strategy that strengthens consent and enhances development quality.

What Service Do I Need?

A Quick Guide

The right landscape service depends on project stage and planning requirement.


Use the guide below to identify the assessment or design support most relevant to your scheme.

Landscaping Visual Impact Assessment (LVIA)

When: required when development affects views, landscape character or sensitive receptors.

Purpose: tests visual change and landscape effects for planning.

Timing: start early in design; viewpoints must be agreed before modelling.

3D Landscape Design

When: useful when proposals need clear visual communication for planners or clients.

Purpose: shows layout, materials and planting in realistic 3D form.

Timing: best at concept stage or during pre-application discussions.

Landscaping Schemes

When: needed for applications involving external works, planting or visual mitigation.

Purpose: provides the plans and planting detail that support validation and condition discharge.

Timing: typically required before validation or at early design freeze.

Your Next Step

Define your landscape strategy early to strengthen both planning outcome and design quality.

Landscape Architecture FAQs

What is a Landscape and Visual Impact Assessment (LVIA)?

A Landscape and Visual Impact Assessment (LVIA) evaluates how a proposed development may affect landscape character and visual amenity. It considers site context, sensitivity and magnitude of change to inform planning decisions.

LVIA is commonly required for sensitive, large-scale or visually prominent schemes.

An LVIA may be required where development could significantly alter landscape character or visual receptors, particularly in open countryside, designated landscapes or elevated sites.

Local planning authorities determine the requirement, often referencing national guidance and local policy.

An LVIA typically includes:

  • Baseline landscape character assessment

  • Visual receptor identification

  • Viewpoint photography and visualisations

  • Assessment of magnitude and significance of effects

  • Mitigation and design response

The report supports robust, defensible planning submissions.

3D landscape design models how proposed landscaping will look and function before construction. It improves communication between architects, planners and clients, supporting design clarity and stakeholder engagement.

3D modelling strengthens both planning submissions and delivery coordination.

Yes. 3D visualisations can help illustrate landscape mitigation, spatial layout and visual integration, supporting clearer understanding by planning officers and consultees.

While not always mandatory, it often strengthens submissions.

What is a landscaping scheme in planning?

A landscaping scheme is a detailed planting and hard landscape proposal prepared to discharge planning conditions or deliver approved mitigation.

It includes species schedules, planting plans, specifications and implementation details aligned with planning approval.

Yes. Landscaping schemes often contribute to Biodiversity Net Gain delivery by defining habitat creation, planting composition and long-term management proposals.

Design decisions can influence both ecological value and visual integration.

An LVIA focuses specifically on landscape and visual effects.
An Environmental Impact Assessment (EIA) is a broader statutory process that may include landscape, ecology, noise, traffic and other disciplines.

LVIA can form part of an EIA where required.

Landscape input is most effective at the earliest design stages. Early strategy informs layout, visual mitigation and policy alignment before design becomes fixed.

Late-stage assessment can limit flexibility and increase redesign risk.

Strategic landscape design enhances visual integration, strengthens planning defensibility and improves long-term site quality.

Clear landscape strategy can:

  • Reduce visual impact concerns

  • Support policy compliance

  • Improve placemaking

  • Strengthen consent prospects

  • Enhance market appeal

Landscape architecture supports both approval and long-term development value.

Training

Training

Get the practical knotweed expertise clients expect.
Clear, practical training in the identification, assessment and management of Japanese knotweed for property, surveying and remediation professionals. Delivered nationwide by in-house experts.

When sites get pressured, competence matters.

Whether you’re surveying land, advising clients, or protecting a project’s value, you need to recognise knotweed early and act with confidence.

Our training gives you the edge: clear identification, practical methods, and the right language for lenders, planners and clients. You’ll know what to look for, what to record, and how to move a project forward without hesitation.

Align Your Training With Real-World Demands

Most situations that involve knotweed follow predictable pressure points.


Join our CPD training to keep ahead of any Knotweed issues.

Japanese Knotweed Training Courses

Who It’s For: professionals who want to spot knotweed fast and stay ahead of risk. Speak with confidence on site, in reports, and in front of clients.

Purpose: Learn the essentials that set you apart: fast ID, smart treatment choices, and clear, credible advice – the authority clients expect.

Timing: year-round.

Your Next Step

Not sure where to start? Speak to our team and get a clear recommendation.

Japanese Knotweed Training FAQ

What does the Japanese Knotweed training course cover?

Japanese Knotweed training covers identification throughout the seasons, treatment options, legal responsibilities and practical reporting. Courses combine classroom and real-world content designed to improve confidence and skills in recognising and managing knotweed.

These courses are ideal for surveyors, property professionals, estate agents, contractors and land managers who need practical understanding of invasive plant identification, assessment and implications for property, land use and compliance.

Yes. The training is CPD-accredited by a recognised Continuing Professional Development certification body, ensuring it meets professional development standards and supports ongoing competence.

Completing a CPD course deepens your ability to identify Japanese knotweed, understand treatment options, and apply legal and reporting best practice. It helps enhance professional confidence, competence and industry awareness.

Japanese Knotweed CPD courses provide strong practical understanding but do not qualify delegates to issue guarantee-backed knotweed survey reports or treatment plans. High-risk cases still require specialist survey qualifications.

How long are the training courses?

Courses vary in length and format. Options typically include full-day, half-day or online modules, each designed to deliver core identification, treatment, reporting and legal content at different depths.

Yes. In-person Japanese Knotweed training often includes practical demonstrations such as spraying and injection techniques under expert supervision, along with guidance on preparing client-facing reports.

Training enhances the ability to confidently recognise knotweed, understand liability and legal implications, and engage with surveyors, lenders and planners with informed awareness of risks and reporting practices.

Yes there are  online Japanese Knotweed training courses, delivering core identification and management modules in a flexible format suitable for remote learning.

Continuing Professional Development (CPD) training ensures professionals stay up to date with industry standards and best practice in identifying, assessing and discussing Japanese Knotweed, helping reduce uncertainty and support appropriate decision-making.

Bat Surveys

Bat Surveys

Effective bat risk management begins with early assessment, keeping planning approval on track from the outset.

Bats are legally protected, and where buildings, trees or structures may offer roosting potential, local planning authorities require survey evidence.

We carry out Preliminary Roost Assessments to establish roosting potential and record evidence of presence. Where bats are confirmed, we prepare mitigation strategies that meet statutory requirements while allowing the project to progress. Measures are evidence-led and proportionate, ensuring protection is delivered without unnecessary cost. This provides the survey evidence required for informed planning decisions.

What Bat Survey Do I Need?

A Quick Guide

Most planning applications involving roof works, conversions, demolition or tree removal trigger bat survey requirements.

Use the guide below to identify the survey stage most likely to apply to your project.

Preliminary Roost Assessment (PRA)

When: buildings, bridges or mature trees show roost potential, or lighting and demolition could affect bats.

Purpose: Assess buildings and trees for roost potential.

Timing: Year-round 

Next Steps: If no evidence of bats is found and the building or structure is not suitable for bats, a PRA is all that’s required.

If evidence of bats is found or if the building or structure has roost potential, further emergence surveys will be needed

Bat Emergence Survey

When: The results of the PRA will determine how many emergence surveys are needed.

Purpose: If there is evidence of bats or if the building or structure has bat roost potential.

Timing: May to August

Your Next Step

Do you require a bat survey? Call us today to book in one of our expert ecologists.

Bat Survey FAQs

Do I need a bat survey for planning permission?

A bat survey for planning permission is required where development may affect buildings, trees or structures with potential bat roosting features. All bat species in the UK are protected under the Wildlife and Countryside Act 1981 and the Conservation of Habitats and Species Regulations 2017. Local planning authorities require survey evidence where roosts may be impacted before determining an application.

A bat survey becomes a legal requirement where development has the potential to disturb or damage a bat roost. It is an offence to damage or destroy a bat roost, even if bats are not present at the time. Survey evidence is therefore required to demonstrate compliance with wildlife legislation before works proceed.

Developers, architects, homeowners and contractors may need a bat survey where works involve roof alterations, loft conversions, demolition, extensions, barn conversions or tree removal. If a structure could support roosting bats, survey evidence is typically required at planning stage.

A Preliminary Roost Assessment is the first stage of a bat survey. It involves a daytime inspection of a building, tree or structure to assess roosting potential and record any direct or indirect evidence of bat presence. The findings determine whether further bat emergence surveys are required.

A bat emergence survey involves dusk and/or dawn monitoring to observe bats entering or leaving a structure. These surveys confirm presence, roost type and usage levels. They follow recognised ecological guidance and are required where roosting potential or evidence has been identified during a Preliminary Roost Assessment.

What time of year are bat surveys carried out?

Preliminary Roost Assessments can be undertaken throughout the year, although winter inspections may be limited by reduced visibility of evidence. Bat emergence surveys must be carried out during the active bat season, typically between May and September, in accordance with survey guidance.

A Preliminary Roost Assessment is usually completed in a single site visit. If bat emergence surveys are required, multiple visits are undertaken during the appropriate seasonal window to meet recognised survey standards.

Bat survey validity depends on site context and planning authority expectations. In most cases, survey reports are considered valid for up to two years, provided site conditions and surrounding habitat have not materially changed.

If a bat survey confirms the presence of bats, a mitigation strategy must be designed to avoid or minimise impacts. In some cases, a European Protected Species licence from Natural England may be required before works commence. Survey findings determine the appropriate mitigation pathway.

The cost of a bat survey depends on the size and complexity of the site and whether only a Preliminary Roost Assessment is required or further bat emergence surveys are necessary. Early assessment helps define scope clearly and align survey requirements with programme and budget.

Habitat Action Plans

Habitat Action Plans

Focused ecological frameworks that secure, enhance and monitor key habitats — aligning your development with biodiversity policy and keeping planning predictable across the UK. 

Do you need a Habitat Action Plan?

If your development affects important habitats  such as grassland, woodland, wetland or riparian corridors, your planning authority may require a Habitat Action Plan (HAP). 
These plans demonstrate exactly how habitats will be protected, enhanced and managed to meet Biodiversity Net Gain and policy objectives. 

What is a Habitat Action Plan?

A HAP sets out the actions needed to protect, restore and enhance habitats during and after development. 
It links site-specific ecology to planning conditions, showing planners how biodiversity objectives will be delivered and monitored over time. 

Trigger points — signs your site needs a HAP

These indicators suggest your site might require more than a basic walkover and may attract LPA scrutiny:

  • habitats of medium or high distinctiveness recorded in your PEA or BNG 
  • areas identified as S41 priority habitats or within Nature Recovery Networks 
  • mitigation or enhancement conditions applied to multiple parcels 
  • post-development management obligations lasting beyond one season 
  • complex sites where multiple habitat types interact (e.g. grassland–wetland mosaics) 

Under the Environment Act 2021NERC Act 2006 (S41) and NPPF Section 15, LPAs must ensure developments conserve and enhance priority habitats. A HAP demonstrates this duty has been addressed transparently, giving planners confidence that ecological gains will be delivered.

What We Deliver

We keep guidance clear and planning-ready — supporting predictable project delivery. 

Service Component Purpose Outcome
Species Review Identify target species and ecological context Defined scope for actions
Impact Assessment Evaluate risks to populations Evidence for proportionate response
Mitigation Design Develop avoidance and reduction measures Legal and planning compliance
Enhancement Strategy Add long-term biodiversity value Quantifiable uplift for BNG
Implementation Plan Set methods, timing and responsibility Predictable delivery sequence
Monitoring Framework Track effectiveness over time Transparent reporting for LPAs
Reporting & Sign-off Produce planning-ready documentation Defensible submission evidence

How it Works

Our process is designed to remove friction and keep decisions moving. 

Scope & Baseline

We review your PEA/BNG data and confirm which habitats require protection or enhancement.

Action Planning

We set out practical habitat creation and management measures linked to construction and maintenance phases.

Implementation & Monitoring

We define timelines, responsibilities and measurable success criteria to maintain compliance through condition discharge.

Each report follows CIEEM and Natural England methodology, ensuring evidence stands up anywhere in the UK. 

Timing & Programme Integrations

 Habitat Action Plans can be produced year-round once baseline data is available, but the surveys that inform them are seasonal.

botanical survey icon

Botanical Surveys

April - September

bird surveys

Bird Surveys

Year-round for scoping; nesting activity March–August

Reptile Surveys

Only April, May and September

Bat Surveys

PRA: Year-round Emergence: May - August

GCN survey

GCN Surveys

eDNA April – June / activity mid-March – June​

Early instruction secures the survey window and keeps ecology off the critical path. 

That’s how project control is maintained.  

Why planning officers request HAPs

A robust HAP resolves ecological risks early and strengthens planning credibility. 

Without one, projects risk: 

  • conditions being deferred or refused 
  • further consultation with statutory bodies 
  • extended determination timelines 
  • enforcement pressure at post-construction stage 

HAPs support compliance with: 

  • Environment Act 2021 (mandatory BNG and habitat enhancement) 
  • NERC Act 2006 S41 (priority habitats and species) 
  • Wildlife & Countryside Act 1981 
  • NPPF Section 15 (conserve and enhance the natural environment) 
  • Local Nature Recovery and Biodiversity Policies 

Its purpose is simple: provide clear, auditable evidence that your project supports biodiversity while keeping the programme stable.

Our Approach

We integrate habitat planning with design, construction and long-term management from day one.

Preparing your HAP alongside design mitigates revisions later and ensures survey evidence flows straight into management delivery.

Our planning-ready HAP includes: 

  • baseline habitat data and condition assessment 
  • mitigation, creation and enhancement actions 
  • delivery responsibilities and sequencing 
  • long-term management and monitoring strategy 
  • measurable outcomes for BNG and policy tracking

Our ecologists follow CIEEM standards and DEFRA Metric 4.0 guidance, mapping actions directly to planning milestones so you always know what needs to happen, when and why. 

How this supports your project

A well-timed HAP turns mitigation into measurable uplift – strengthening your planning submission and preventing late redesign.

 It supports your project by:

  • clarifying habitat responsibilities before design lock-in 
  • aligning ecological actions with planning milestones and programme sequencing 
  • meeting policy duties under the NPPF, Environment Act 2021 and local biodiversity strategy 
  • defining realistic enhancement measures early, before they become conditions that push scheduling 
  • providing habitat-level evidence that integrates with BNG, SAPs, CEMP and EIA ecology 
  • preventing rework by showing how habitats will be protected, enhanced and monitored through the full development cycle 
  • providing long-term management planning that satisfies both planners and contractors 
  • removing uncertainty for design teams, landscape leads and project managers 

Early clarity maintains schedule stability. Later discovery creates delay. 
This is where foresight pays off. 

Case Insight

A regeneration scheme included degraded grassland and drainage habitats within a wider nature-recovery corridor. The HAP established phased creation, adaptive management and annual monitoring, achieving measurable uplift within the BNG metric. Planning conditions were discharged in one stage, keeping the development aligned with both ecological and programme targets. That’s how proactive habitat planning safeguards delivery.

Your Next Step

Get the ecological clarity that keeps your design on track. 

Phone: 0800 494 7479

Email: [email protected]

Areas We Cover

We cover many areas across England and Wales. Click below to find out more.

HAP FAQ - Planning and Programme Clarity

What is a Habitat Action Plan?

A Habitat Action Plan is a structured ecological document that sets out how habitats will be created, enhanced, or restored on a site. It defines clear objectives, practical methods, and measurable outcomes to ensure biodiversity improvements are delivered in line with planning requirements.

A Habitat Action Plan is typically required where a development proposes habitat creation or ecological enhancement. Local Planning Authorities often request a HAP to demonstrate how biodiversity improvements will be implemented and maintained as part of a planning application or condition.

A planning compliant Habitat Action Plan will usually include:

  • A baseline habitat summary
  • Target habitat types and condition objectives
  • Detailed habitat creation and enhancement methods
  • Planting specifications and establishment guidance
  • Ongoing management requirements
  • Success criteria and monitoring approach

This ensures the plan is clear, deliverable, and measurable.

A Habitat Action Plan is prepared through a structured ecological process. This involves assessing the existing site, identifying suitable habitat enhancements, defining practical implementation methods, and setting measurable outcomes. The document must be technically robust and aligned with planning policy to be accepted.

The purpose of a Habitat Action Plan is to provide a clear and enforceable strategy for delivering biodiversity improvements. It ensures that habitat creation and enhancement are not simply proposed, but are achievable, measurable, and capable of long term success.

No.

A Habitat Action Plan is site specific and linked to a particular development. A biodiversity action plan is typically broader and may relate to regional or national conservation priorities.

A HAP focuses on practical delivery within a defined site boundary.

A well prepared Habitat Action Plan provides clarity and confidence to planning officers that ecological enhancements can be delivered successfully. It demonstrates compliance with local and national policy and reduces the risk of delays or requests for further information.

Section 41 of the Natural Environment and Rural Communities Act 2006 lists habitats and species of principal importance in England.

A Habitat Action Plan often considers these priority habitats and species when designing ecological enhancements, ensuring alignment with national biodiversity objectives and planning policy.

Do all developments need a Habitat Action Plan?

Not all developments require a HAP.

However, where habitat creation, enhancement, or ecological mitigation is proposed or required by planning policy, a Habitat Action Plan may be requested to support the application or discharge conditions.

A Habitat Action Plan must be sufficiently detailed to demonstrate how habitats will be delivered in practice. This includes clear methodologies, appropriate species selection, timing of works, and realistic management requirements. High level or vague plans are unlikely to be accepted.

Yes.

Habitat Action Plans are commonly used on smaller residential schemes where ecological enhancements are required but full Biodiversity Net Gain processes may not apply. They provide a proportionate and practical way to demonstrate biodiversity improvement.

If a Habitat Action Plan is required and not submitted, planning applications may be delayed, refused, or conditioned pending further ecological information. Providing a clear and policy aligned HAP early helps avoid unnecessary delays.

A Habitat Action Plan should be prepared by a qualified ecologist with experience in habitat creation and planning policy. This ensures the document is technically robust, policy compliant, and capable of being implemented on site.

Implementation follows the methods set out within the plan, including habitat preparation, planting, and management actions. Clear guidance within the HAP ensures contractors and stakeholders understand how to deliver the required ecological outcomes.

A Habitat Action Plan sets measurable targets and defines how success will be achieved through appropriate design, correct species selection, and structured management. Where required, monitoring ensures habitats establish properly and continue to deliver ecological value.

Related Services

Arboricultural Surveys

Arboricultural Surveys

Tree-related decisions made without professional assessment can reshape development plans.

Arboricultural surveys, including BS 5837 tree surveys, provide evidence to inform design, protect retained trees, and support planning applications. They define constraints before layouts are fixed — creating space for practical solutions without costly redesign.

Clearing trees before assessment can increase Biodiversity Net Gain unit requirements and associated cost. Early BS 5837 evidence ensures tree decisions are integrated into both design and BNG calculations from the outset.

Where trees have already been removed, retrospective BS 5837 assessment is not possible. Historic data may assist in limited circumstances, but planning authorities typically require current arboricultural evidence. Requirements vary by local authority, and BS 5837 surveys are often requested alongside BNG submissions.

Whether preparing a submission or refining a layout, arboricultural clarity prevents avoidable redesign. We define what is required and when.

Protect the design. Control cost. Keep planning moving.

Which Arboricultural Surveys do I need?

A Quick Guide

Most development sites involving existing trees will require some form of arboricultural assessment. The type of survey depends on what you are proposing and how trees may influence the design or construction process.

Use the guide below to identify the survey most likely to apply to your project.

Tree Survey for Planning (BS 5837)

When: your site contains trees or hedgerow trees, and you require BS 5837 evidence for planning or pre-application purposes.

Purpose: establish baseline data and root protection areas (RPAs) before planning layout lock-in.

Timing: Year-round.

Arboricultural Impact Assessment (AIA)

When: proposed works may affect retained trees or their RPAs, or the LPA requests an AIA alongside your BS 5837 survey.

Purpose: evaluate impacts, define protection, and provide proportionate mitigation.

Timing: Year-round.

Tree Health Survey

When: a tree appears unsafe, declining or damaged, or you need risk-based duty-of-care evidence.

Purpose: assess condition, structural integrity and management needs.

Timing: Year-round.

Tree Damage Survey

When: roots or branches may be affecting boundaries, paving or structures.

Purpose: confirm cause, extent and mitigation for tree-related damage.

Timing: Year-round

Subsidence Reports

When: buildings show movement on shrink–swell soils or insurers/engineers request root-related evidence.

Purpose: identify causal species, soil influence and realistic remedial options.

Timing: Year-round.

Mortgage & Insurance Tree Reports

When: a lender or insurer flags tree-related risk or requests formal verification.

Purpose: deliver fast, lender-compliant evidence with actionable findings.

Timing: Year-round.

TPO Applications & Appeals

When: protected trees require works, the council needs supporting evidence, or you’re responding to a refused consent.

Purpose: supply robust justification and manage submissions or appeals effectively.

Timing: Year-round.

Your Next Step

Share your proposal and we will confirm the appropriate arboricultural survey and sequencing in line with local planning requirements.

Arboricultural Surveys FAQs

What is the purpose of a tree survey?

A tree survey assesses the condition, quality and development constraints of trees on or adjacent to a site. For planning applications, a BS 5837 survey provides the evidence needed to show how trees will be retained, protected and considered within the design. It identifies Root Protection Areas (RPAs), which define how far tree roots extend and where construction must be controlled.

In planning terms, arboricultural refers to the professional assessment and management of trees in relation to development. Arboricultural reports evaluate tree condition, quality, root protection areas and how proposed works may affect them, in accordance with British Standard BS 5837.

 

A BS 5837 tree survey is typically required where development may affect existing trees. Local planning authorities request this survey to understand which trees should be retained, how they are categorised (A, B, C or U) and what protection measures are needed before granting permission.

Tree surveys are not automatically required by law. However, they are commonly required by local planning authorities where trees influence development proposals. They may also be requested by lenders or insurers in property transactions.

The cost depends on site size, the number of trees and the type of report required. A planning-related BS 5837 survey differs from a subsidence or mortgage report in scope. Early review of your proposal ensures the correct report is prepared without unnecessary work.

What is an Arboricultural Impact Assessment (AIA)?

An Arboricultural Impact Assessment explains how proposed development will affect existing trees. It forms part of the BS 5837 process and sets out which trees will be retained, which may be removed, and how protection measures will be implemented during construction.

Some trees are protected by a Tree Preservation Order (TPO) or are located within conservation areas. In these cases, written consent from the local authority is required before works are carried out. Professional advice confirms whether protection applies and what procedure must be followed.

A subsidence tree report assesses whether tree roots may be contributing to structural movement or damage. These reports are prepared to support insurers, engineers or legal representatives and must be based on clear, evidence-led assessment.

Mortgage and insurance tree reports assess tree condition and proximity to buildings to help lenders or insurers understand potential structural risk. They provide independent arboricultural evidence during property transactions or claims.

BS 5837 surveys should be undertaken by qualified arboricultural professionals experienced in tree assessment and planning submissions. Reports must comply with British Standards and meet local planning authority expectations.

Bat Emergence Survey

Please note: Bat emergence surveys are now out of season. We are currently taking bookings for surveys beginning in May 2026. Flexible payment options, including Direct Debit, are available to help spread the cost. Book now to secure your survey slot.

Dusk Emergence Bat Survey

Planning-ready evidence where roost potential exists.

Clear, compliant dusk emergence surveys carried out across England & Wales — delivered with structured methodology, predictable timelines and transparent reporting. 

Do you need a Dusk Emergence Survey?

You will usually need an emergence survey if: 

  • Your PRA identified low, moderate or high roost potential 
  • Your planning officer requested a bat presence/absence assessment 
  • Your site includes older buildings, farm buildings, schools, churches, barns or structures with ageing rooflines 
  • You are planning demolition, conversion, roof replacement, significant repairs, or tree removal 
  • You need evidence within the bat survey season (May–August) to avoid planning delays 






This is for testing until we set up Google Maps Distance Matrix API.







Rood cladding potential for bat roost
A sun set with an outline of birds

What is a Dusk Emergence Survey?

A dusk emergence survey (sometimes called a “bat emergence survey”) is a seasonal survey carried out at sunset to identify whether bats are emerging from a building, tree or structure. 
It provides the definitive presence/likely absence evidence planning officers require after a Preliminary Roost Assessment (PRA) identifies bat roost potential — even at low potential. 

A dusk emergence survey answers the critical question: 

“Are bats using this structure as a roost?” 

This determines planning risk, licensing needs, mitigation and how your project proceeds. 

Potential Roost Features
(early indicators you need a dusk emergence survey)

Before planners sign off demolition, roof works or tree works, they look for any potential roost features that could indicate bat use.

These features are often subtle and easily missed without a proper assessment; but they’re the exact cues that trigger LPA requests for emergence surveys.

These indicators almost always attract LPA scrutiny: 

  • Loft voids, ridge tiles, lifted tiles or mortar gaps 
  • Cavity walls, cladding gaps or soffit entry points 
  • Mature or veteran trees with cavities or lifted bark 
  • Buildings within edge-of-settlement, woodland or water-rich landscapes 
  • PRA classification of low, moderate or high roost potential 
  • Planning officer emails referencing “bat emergence surveys” 

Before listing the triggers, we introduce the relevance. After the list, we clarify the impact. 

What this means for your project: 
If any apply, submitting planning without emergence evidence usually results in validation queries or a forced wait until next summer. 

What We Deliver

We provide a robust, planning-ready report with clear interpretation and next steps. 

Service Purpose Outcome
Dusk Emergence Survey(s) Confirm bat presence / likely absence at a roost feature Clear evidence for planning validation
Activity Level Assessment Understand wider flight paths, foraging or commuting Data informing design and lighting
Endoscope Inspection (where safe) Direct inspection of accessible features Rapid confirmation if possible
NVA / Infra Red Cameras Improves detection of bats in low light Increased survey accuracy
Anabat Recorder & Echo Meter Touch 2 Pro Identify species by listening to calls Accurate species identification
Planning-Ready Report Structured evidence for LPAs Clear summary, impacts, risks & next steps
Mitigation / Licensing Strategy Only required if bats are confirmed Practical, proportionate and predictable

Every recommendation is explained in practical terms, so you know exactly what each step means for your build schedule. 

How it Works

Our process is designed to remove friction and keep decisions moving. 

PRA & Positioning

Review PRA findings and confirm survey locations.

Observe at Dusk

Record emergence using detectors and visual monitoring.

Analyse & Report

Interpret activity and define proportionate next steps.

Timing & Survey Windows

Missing the summer emergence window normally means waiting until next year. 


We schedule early to secure your position and protect your programme

PRA Survey

Year-round

Dusk Emergence Surveys

Seasonal: May – August

Activity Surveys

May–August

Why Planning Officers Request Bat Emergence Surveys

Emergence surveys sit at the heart of UK bat legislation and planning policy. 
Where roost potential exists, LPAs cannot validate or determine applications without correct seasonal evidence. 

Missing or inadequate dusk emergence surveys can lead to: 

  • Validation delays 
  • Requests for additional seasonal evidence 
  • Stop-work notices if bats are discovered during works 
  • Enforcement for disturbing a roost (strict liability offence) 
  • Licence requirements and scheduling constraints 
  • One-year delays if the seasonal window is missed 

Relevant legislation: 

  • Conservation of Habitats & Species Regulations 2017 
  • Wildlife & Countryside Act 1981 
  • National Planning Policy Framework (NPPF) 
  • Local authority ecology and validation policies 

Our commitment: 
We deliver PRA surveys to recognised UK standards, strict legal expectations, and planning-authority requirements.

Our Approach

We understand the scrutiny that comes with ecology and meet it with clarity, accuracy and planning-focused delivery. 

What happens during a Dusk Emergence Survey? 

A typical emergence survey includes: 

  • A team of trained ecologists positioned around the structure 
  • Sunset-timed observation using heterodyne or full-spectrum bat detectors 
  • Behavioural recording (emergence, swarming, commuting) 
  • Activity mapping around the site 
  • Repeat surveys where required under guidance or LPA policy 

We follow recognised UK protected-species survey standards and maintain meticulous data quality throughout. 

Why homeowners, planners and developers choose ProHort:

  • Nationwide capability across England and Wales 
  • Programme-led scheduling 
  • Reports designed for LPA scrutiny 
  • Straight, practical communication 
  • Specialists in development-focused ecology 
  • Transparent interpretation — no vague language 
  • High trust and high clarity, reinforced at every stage 

How to Interpret Your Report

Many clients, especially homeowners, are unsure what “negligible”, “low”, “moderate” or “high” means in practice. 

Your report explains: 

  • Whether bats were present 
  • What “likely absence” means legally 
  • Whether any parts of your project can proceed now 
  • Whether timing restrictions apply 
  • Whether a licence is required (only if a roost is confirmed) 
  • How to plan works safely and legally 

We also add summaries, so you understand exactly what the outcome means for your build, budget and schedule. 

Case Insight

A detached property scheduled for loft conversion was flagged for low roost potential in the PRA. One dusk emergence survey confirmed likely absence, and planners validated the application without requesting further surveys. The homeowner proceeded with the build, fully compliant and without seasonal delays.

Your Next Step

Get the clarity that keeps your design on track. 

Phone: 0800 494 7479

Email: [email protected]

Areas We Cover

We cover many areas across England. Click below to find out more.

FAQ - Dusk Emergence Surveys

What is a dusk emergence bat survey?

A dusk emergence bat survey is undertaken at sunset to confirm whether bats are roosting within a building, structure, or tree.

Ecologists observe the site as bats emerge to forage, allowing identification of species, roost location, and activity levels. This provides the evidence required by Local Planning Authorities when assessing planning applications.

Fees are determined by the level of survey effort required following the Preliminary Roost Assessment (PRA).

For most residential developments, emergence survey programmes typically range from:

£1,200 – £2,500 + VAT

This generally includes two surveyors attending site across two to three dusk survey visits during the active season.

Where higher roost potential or multiple structures are involved, additional survey visits or surveyors may be required.

Survey costs are primarily influenced by:

  • Roost potential identified during the PRA
  • Number of required survey visits
  • Number of surveyors per visit
  • Seasonal timing and survey availability
  • Building size, layout, and access complexity

Survey requirements follow recognised ecological guidance and cannot be reduced without risking planning refusal.

The number of surveys depends on the level of roost suitability identified:

  • Moderate suitability: typically two surveys
  • High suitability: typically three surveys

These surveys must be spaced appropriately across the survey season to meet planning and best practice requirements.

Additional survey visits may be required where:

  • High roost potential is identified
  • Multiple buildings or structures are present
  • Complex roof structures or access points exist
  • Higher levels of bat activity are anticipated

The exact level of survey effort is confirmed following the Preliminary Roost Assessment.

Bats typically emerge shortly after sunset.

Surveyors begin observations at sunset and continue for approximately 1.5 to 2 hours after sunset, which is when peak bat activity usually occurs.

Each survey visit lasts approximately 2.5 to 3 hours, including set up time before sunset and observation after sunset.

Multiple visits are often required to provide robust and reliable survey data.

Bat emergence surveys are seasonally constrained and can only be undertaken between May and August, with optimal survey conditions between June and August.

Surveys outside this period are not considered valid for planning purposes.

Can bat surveys be carried out in the rain?

Surveys must be undertaken in suitable weather conditions.

Heavy rain, strong winds, or low temperatures can significantly reduce bat activity and may invalidate survey results. In these cases, surveys are rescheduled to ensure reliable data is collected.

In many cases, yes.

Works such as roof replacement, loft conversions, or demolition can impact potential bat roosts. If a Preliminary Roost Assessment identifies suitability for bats, further surveys such as dusk emergence surveys may be required to support planning or lawful works.

Bat surveys are not automatically required for every project, but they are a legal requirement where bats may be affected by development.

Bats are protected under UK law, and Local Planning Authorities must ensure impacts are properly assessed before granting permission.

No. Bat surveys must be undertaken by qualified and experienced ecologists.

They must follow recognised survey methodologies to be accepted by Local Planning Authorities and to comply with wildlife legislation.

Bat emergence surveys can influence project timelines due to seasonal restrictions.

If surveys are required outside of the survey season, your application may need to be delayed or submitted with conditions attached. Early instruction is recommended to avoid delays.

If bats are confirmed, the findings will inform a mitigation strategy. This may include:

  • Timing works to avoid disturbance
  • Retaining or enhancing roost features
  • Installing bat boxes or integrated roosting features
  • Applying for a European Protected Species licence, where required

This allows development to proceed in compliance with legislation.

A planning-ready report typically includes:

  • Survey dates, timings, and methodology
  • Weather conditions during surveys
  • Bat species identification
  • Roost location and activity levels
  • Impact assessment
  • Recommendations for mitigation or licensing

This report supports planning submission and decision-making.

Bat survey requirements are guided by ecological best practice and enforced by Local Planning Authorities.

For example, guidance from authorities such as:

often requires bat surveys where development may impact protected species. Requirements vary depending on site and proposal.

Related Services

eDNA Testing for Great Crested Newts

Great Crested Newt (GCN) Surveys &
eDNA Testing for Planning

Fast, planning-ready GCN assessments with predictable timelines, seasonal clarity and practical advice aligned to your programme. 

Do you need a GCN Survey?

You may need a GCN survey if your site: 

  • contains a pond or seasonal waterbody 
  • lies within 250m of a pond 
  • includes grassland, scrub, hedgerows or woodland edges 
  • has rubble piles, log stacks or damp refuge features 
  • was flagged during a PEA for suitable terrestrial habitat 

Because GCN are a European Protected Species, planning authorities require clear evidence wherever habitat risk is identified. Early checks protect timelines, avoid seasonal delays and shape proportionate next steps. 

Gloved hand gently holding a great crested newt, indicating the presence of a protected species.

Early Signs an GCN Survey is Needed

  • Pond on-site or within 250m 
  • PEA flagged GCN suitability 
  • Grassland, hedgerows, scrub, woodland edges 
  • Rubble piles, log stacks, terrestrial refuge 
  • LPA requested a GCN assessment if site is in a GCN risk zone 
  • Large footprints near waterbodies or ditches 

If any apply, a GCN survey is usually required. 

WhatsApp-Image-2025-11-19-at-14.00.14_c39fdc9f

What We Deliver

Service Purpose Outcome
GCN eDNA Testing Fast presence/likely absence screening Clear positive/negative result
Habitat Suitability Index (HSI) Early risk scoring Practical suitability rating
Presence/Likely Absence Surveys Alternative to eDNA Testing Robust evidence for planning
Population Surveys Gives an estimate of the population size Data for mitigation/licensing
Mitigation & Licensing If impacts are unavoidable Planning-ready solutions

How it Works

Scope & Schedule

Send the site location and timeframe. We confirm whether eDNA is eligible or if seasonal surveys are required.

Fieldwork

eDNA sampling (April–June) or multi-visit presence/absence surveys depending on need

Reporting

Planning-ready reports, clarity for planners, and next steps for your programme.

Timing & Survey Windows

Missing the eDNA window usually means waiting until the next survey season. Early booking protects your timeline. 

eDNA Testing

Mid April – June

Presence/ Likely Absence Surveys:

Mid March – Mid June

Population Surveys

Mid April – June

Licensing

Seasonally Dependent

What You Receive:

  • eDNA results (positive/negative) 
  • HSI scoring 
  • Presence/absence or population data 
  • Planning-ready reporting 
  • Clear mitigation/licensing guidance 
  • Reliable timelines and next steps 

Evidence for planners. Clarity for project teams. 

Why Developers Choose ProHort:

  • Programme-first scheduling 
  • Planning-focused reporting 
  • Straight, practical recommendations 
  • Reliable survey capacity 
  • Support through licensing where required 

Legal Compliance & Planning risk

GCN surveys are required under UK law when suitable habitat exists. Missing or incorrect evidence can lead to: 

  • Planning refusal or validation delays 
  • Stop-work notices 
  • Enforcement penalties for disturbing GCN 
  • Licence requirements late in the programme 
  • Seasonal delays (eDNA and survey windows are fixed)

Relevant legislation includes:

  • Conservation of Habitats and Species Regulations 2017 
  • Wildlife & Countryside Act 1981 (Schedule 5) 

ProHort ensures your evidence is clear, proportionate and aligned to your build schedule. 

Your Next Step

Need GCN or eDNA surveys? Let’s confirm your route and secure your survey window. 

Phone: 0800 494 7479 
Email: [email protected] 

Areas We Cover

We cover many areas across England and Wales. Click below to find out more.

Case Note

A residential site within 120 m of a pond booked eDNA sampling early. Results returned in 9 days. The negative finding removed the need for multi-visit surveys, keeping planning submission on the original timeline.

GCN Survey FAQs

What is eDNA testing for great crested newts?

Environmental DNA, commonly referred to as eDNA, is a survey method used to detect the presence of great crested newts by analysing water samples from ponds. As newts shed DNA into the water through skin cells, mucus, and waste, laboratory analysis can confirm whether the species is present without needing to physically capture or observe individuals.

eDNA surveys are seasonally constrained and can only be undertaken between mid April and the end of June. This period aligns with the breeding season when great crested newts are most likely to be present in ponds, ensuring reliable detection results for planning purposes.

Yes. eDNA testing is widely accepted by local planning authorities as a valid method of presence or likely absence assessment for great crested newts, provided it is carried out in accordance with recognised guidelines.
For validation requirements, you should always refer to your local authority guidance, for example:
https://www.planningportal.co.uk/

A licence is not required to undertake eDNA sampling itself. However, surveys must be carried out by a competent ecologist, and any follow up surveys or mitigation works involving great crested newts may require a licence from Natural England.

eDNA testing is highly reliable when undertaken within the correct seasonal window and following standard methodology. It is designed as a presence or likely absence tool, meaning it can confirm whether newts are present, but it does not provide population size or distribution data.

If a positive result is returned, further surveys will typically be required. This often involves traditional presence surveys, such as torchlight surveys or bottle trapping, to establish population size and inform any mitigation strategy required for planning.

A negative eDNA result is generally accepted as evidence of likely absence. This can allow planning applications to proceed without the need for further surveys, provided there are no other ecological constraints identified on site.

The process involves collecting multiple water samples from around the perimeter of a pond using sterile equipment. These samples are then combined and sent to a laboratory for analysis. The survey is quick, non intrusive, and does not disturb habitats or wildlife.

How long does it take to receive eDNA results?

Once samples are submitted to the laboratory, results are typically returned within a few working days. This makes eDNA one of the fastest methods available for assessing great crested newt presence in support of planning.

Not all ponds require testing. A Preliminary Ecological Appraisal or site assessment will determine whether ponds are suitable for great crested newts and whether eDNA testing is required to support a planning application.

eDNA can replace initial presence surveys, but it cannot replace population assessments. If newts are detected, traditional survey methods are still required to inform mitigation, licensing, and development design.

Several factors can influence results, including water quality, pond disturbance, seasonal timing, and sample handling. This is why surveys must follow strict protocols to ensure results are valid for planning submission.

eDNA testing is suitable where ponds are present within or near a development site and there is potential for great crested newts. It is commonly required for residential, commercial, and infrastructure projects where ecological constraints may apply.

Great crested newts are a protected species under UK law, and planning authorities require evidence that development will not harm them or their habitats. eDNA testing provides a robust and efficient way to inform planning decisions and avoid delays.

While standard eDNA testing for planning focuses on great crested newts, the method can be adapted to detect other species. However, separate testing protocols are required depending on the species being targeted.

Related Services

---