Project Type Guides

Permission for a livestock building and its permit

8 min readBy PlanScope Editorial Team

An intensive livestock unit is decided by ammonia deposition on designated habitats and the environmental permit that runs beside the planning application. Here are the thresholds, the mitigation that works and the order to do the work in.

Livestock building planning permission is rarely the hard part of an intensive unit. The hard parts are ammonia deposition on a designated habitat and the environmental permit that runs alongside the planning application, and both can determine the scheme before a planning officer has formed a view. A poultry shed that looks straightforward on a 40 hectare holding becomes a two year project if there is a Site of Special Scientific Interest 1.5km downwind.

Agricultural notification against full permission

On an agricultural unit of 5 hectares or more, Part 6 of Schedule 2 to the General Permitted Development Order 2015 allows agricultural buildings reasonably necessary for the purposes of agriculture, subject to limits. The ground area covered must not exceed 1,000 m², height is capped, and no part may be within 25m of the metalled surface of a trunk or classified road.

Two restrictions matter more than the rest for livestock. A building used for accommodating livestock, or for storing slurry or sewage sludge, is not permitted within 400m of the curtilage of a protected building. And for significant development, you must apply to the authority to determine whether its prior approval is required for the siting, design and external appearance of the building.

Smaller holdings of between 0.4 and 5 hectares fall under a more limited class with tighter restrictions, and buildings for livestock are largely outside it.

So the practical decision tree is short. Over 1,000 m², within 400m of a protected building, or a proposal that is really an industrial-scale installation rather than a building reasonably necessary for agriculture, and you are applying for full planning permission. The threshold questions are the same ones that arise with a floodlit riding arena, where the test of whether a building is reasonably necessary for agriculture does a lot of work.

Where an environmental permit is also required

Intensive pig and poultry installations above stated capacities need an environmental permit from the Environment Agency under the Environmental Permitting (England and Wales) Regulations 2016. The thresholds are places rather than floorspace.

Installation Permit threshold
Intensive rearing of poultry More than 40,000 places
Pigs over 30kg (production pigs) More than 2,000 places
Sows More than 750 places

The permit and the planning permission are separate consents with separate tests, and neither binds the other. In practice the Agency's assessment of the installation's emissions is the document the planning authority leans on, so running the permit work first, or at least in parallel, avoids a planning refusal on an issue the permit would have answered.

Environmental impact assessment sits over the top. Installations for intensive rearing above higher numerical thresholds fall within Schedule 1 to the Town and Country Planning (Environmental Impact Assessment) Regulations 2017, where assessment is mandatory. Below those, an intensive livestock installation with new floorspace above 500 m² falls within Schedule 2 and needs screening. An Environmental Impact Assessment must be prepared by competent experts under those Regulations, so a licensed or competent professional is legally required and an AI-assisted draft is a starting point for that professional rather than a substitute.

Request a screening opinion in writing rather than assuming the scheme is below the threshold. A screening opinion costs a fortnight and protects the permission from a later challenge.

Ammonia and nitrogen deposition on designated sites

This is where most intensive livestock applications are won or lost. Ammonia emitted from housing, from slurry stores and from land spreading deposits nitrogen downwind, and designated habitats have critical levels and critical loads that are easily exceeded.

The screening approach used by the Environment Agency and Natural England compares the predicted process contribution against the critical level for the habitat. The critical level for ammonia is 1 microgram per cubic metre where lichens and bryophytes are an interest feature, and 3 micrograms per cubic metre for higher plants. Where the process contribution is a small fraction of the critical level, the effect is screened out. Where it is not, detailed modelling and in-combination assessment with other nearby units follow.

The practical consequences for a scheme:

  • Identify every designated site, including local wildlife sites and ancient woodland, within the relevant screening distances before you fix a building position
  • Account for existing units nearby, because in-combination effects are assessed and your neighbour's shed counts
  • Expect to need detailed dispersion modelling where any designated habitat is within a few kilometres
  • Build mitigation into the design rather than offering it later: air scrubbing, covered slurry storage, reduced crude protein diets and low-emission spreading all reduce the contribution

An Air Quality Assessment covering ammonia and dust is normally required, and councils usually expect a suitably qualified author with professional review strongly advised. Where a habitats site is involved, the authority as competent authority may also need to carry out an appropriate assessment, which is a separate and slower process.

Odour and the separation to dwellings

Odour complaints are what turn a consented unit into an enforcement problem, and the planning assessment is about separation, prevailing wind and management.

An Odour Assessment sets out the sources, the emission characteristics, the receptors and the predicted exposure, usually with dispersion modelling for anything beyond a small unit. Councils usually expect a suitably qualified author for this work.

Three design decisions do most of the work. Distance to the nearest dwelling not in the applicant's ownership, which is the figure every objector will quote. Orientation relative to the prevailing wind, which is often south-westerly in England but should be taken from local data rather than assumed. And the ventilation arrangement, because ridge-mounted high-velocity fans disperse very differently from side-wall fans at low level.

Offer a manure and odour management plan with the application. It gives the environmental health officer something to condition and it signals that the operation has thought about the neighbours.

Slurry and manure storage requirements

Slurry storage is a construction standards issue as well as a planning one. The regulations covering silage, slurry and agricultural fuel oil set standards for the design and construction of slurry stores and require notice to the Environment Agency before a new store is built or an existing one substantially altered.

For planning, the questions are capacity, siting and cover. Capacity has to match the housing period and the land available for spreading under the rules on agricultural diffuse pollution. Siting has to respect the 400m separation from protected buildings where permitted development is relied on, and watercourse setbacks in any case. Cover reduces both odour and ammonia loss, and offering a cover is one of the more effective mitigations available.

Show the spreading land in the application where it is within the applicant's control. A unit with inadequate land for the manure it produces invites a sustainability objection the design cannot answer.

Traffic, feed deliveries and stock movements

Agricultural traffic is heavy, infrequent and concentrated. The highway authority will want to know vehicle numbers and types by movement, not an annual total.

Set out feed deliveries, stock in and out including catching teams, manure and litter removal, mortality collection and gas or fuel deliveries, each with a vehicle type and frequency. Then show the access geometry, visibility splays and the swept path for the largest vehicle. On a narrow lane, passing provision and the condition of the carriageway become conditions.

Timing matters as much as volume. Stock catching often happens at night, and a condition restricting hours can conflict with the operational requirement, so raise it before it is imposed.

Landscape siting and building scale

Modern livestock buildings are long, wide and pale, and they sit badly in an open landscape unless the siting does the work. A Landscape and Visual Impact Assessment prepared to the recognised methodology is expected where the site is prominent or near a National Landscape.

What tends to succeed: setting the building against existing farm structures rather than in isolation, using the contours to reduce apparent height, dark recessive roof and wall colours, keeping feed bins behind the building line, and structural planting that reads as a farm boundary rather than a screen. What tends to fail: a single row of trees along one elevation, and a promise to plant after the building is up.

Timeline and the order of applications

The sequence below reflects where the risk sits rather than where the paperwork starts.

  1. Screen for designated habitats and run an initial ammonia screening before committing to a site or a building position
  2. Confirm whether an environmental permit is needed, and open a pre-application discussion with the Environment Agency
  3. Request a formal screening opinion for environmental impact assessment
  4. Commission ammonia modelling, odour assessment and the landscape work together, since all three respond to building position
  5. Settle slurry storage capacity and the spreading plan
  6. Hold a planning pre-application meeting with the layout, the modelling results and the permit position in hand
  7. Submit the planning application, and the permit application in parallel if the programme allows
  8. Expect a determination period measured in months rather than weeks where a habitats assessment is involved

Budget time as well as fees. The ammonia and permit work can take longer than the planning determination, and starting it after the planning application is submitted is the most common programme mistake on these schemes.

Browse the report types on PlanScope to see which reports your site is likely to need before you commission the specialists.

This is general guidance, not legal advice. Check the position with your local planning authority, the Environment Agency or a qualified professional before relying on it. For specialist technical reports, qualified professional input may be required. PlanScope provides AI-assisted draft reports for planning applications. Reports should be reviewed before submission. We do not guarantee planning approval.

Frequently asked questions

Can a livestock building be built under permitted development?

Sometimes, on an agricultural unit of 5 hectares or more under Part 6 of Schedule 2 to the General Permitted Development Order 2015, within the limits on ground area, height and road proximity. But a building for livestock or for storing slurry is not permitted within 400m of the curtilage of a protected building, and larger proposals need prior approval of siting, design and external appearance.

When is an environmental permit required?

Under the Environmental Permitting (England and Wales) Regulations 2016, for intensive rearing of poultry above 40,000 places, production pigs over 30kg above 2,000 places, or sows above 750 places. The permit and the planning permission are separate consents with separate tests, and neither binds the other.

What are the ammonia critical levels?

The critical level for ammonia is 1 microgram per cubic metre where lichens and bryophytes are an interest feature of a designated site, and 3 micrograms per cubic metre for higher plants. Screening compares the predicted process contribution against that level, and in-combination effects with other nearby units are assessed too.

Does an intensive unit need environmental impact assessment?

Installations for intensive rearing above the higher numerical thresholds fall within Schedule 1 to the Environmental Impact Assessment Regulations 2017, where assessment is mandatory. Below those, an intensive livestock installation with more than 500 square metres of new floorspace falls within Schedule 2 and needs screening. Request a screening opinion in writing.

What mitigation reduces ammonia emissions?

Air scrubbing on mechanically ventilated housing, covered slurry storage, reduced crude protein diets, low-emission spreading techniques and careful building orientation all reduce the contribution. Build the mitigation into the design and the modelling rather than offering it in response to an objection, because retrofitted mitigation carries less weight.

Sources and further reading

livestockagricultureenvironmental permitammoniaruralodour

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

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