Project Type Guides

Quarry extension planning permission and borrow pits

9 min readBy PlanScope Editorial Team

Mineral applications are determined by the mineral planning authority against the minerals plan. Landbanks, dust and vibration limits, dewatering and restoration decide them.

A quarry extension is determined by the mineral planning authority against the minerals development plan, and the application stands or falls on four things: whether the reserve is needed, whether dust, noise and vibration can be held within the limits in national guidance, whether dewatering can be carried out without harming water resources, and whether the site can be restored to something the authority will accept in 25 years' time. A borrow pit follows the same logic on a shorter timescale, with restoration tied to the construction project it serves.

The mineral planning authority is not always the council you expect. In two-tier areas it is the county council, not the district, so the validation list, the fee, the officer and the committee are all different from the ones a housing scheme would meet.

Who determines a mineral application

Minerals and waste are county matters. In a two-tier area the county council is the mineral planning authority. In a unitary area, a metropolitan borough or a London borough, that authority holds the function itself. Inside a National Park, the National Park authority determines mineral applications.

This has practical consequences beyond the address on the form. The development plan you are arguing against is the adopted minerals and waste local plan, which sits alongside the district local plan rather than inside it. The validation checklist is a minerals checklist. The case officer is usually a minerals and waste specialist who has read a hundred restoration schemes, which raises the standard of the evidence considerably and also means a well-prepared application gets a fairer hearing than it would from a generalist.

Pre-application engagement is worth paying for here. Mineral authorities deal with a handful of applications a year and will usually give a detailed scoping response.

The policy case: landbanks and allocated reserves

Start with whether the mineral is needed, because that is the first question the officer's report will answer.

The minerals chapter of the National Planning Policy Framework asks mineral planning authorities to plan for a steady and adequate supply of aggregates and to maintain landbanks of permitted reserves, with at least seven years for sand and gravel and at least ten years for crushed rock. Those landbank figures, and the Local Aggregate Assessment that calculates them, are the arithmetic your application plugs into. If the authority's landbank is short, the need case is straightforward. If it is comfortable, you are arguing about the distribution of supply, the specific quality of the mineral, or the continuity of an existing operation and its workforce.

Check whether the extension area sits within an allocated site or a preferred area in the adopted plan. An allocation shifts the argument from principle to detail. An unallocated extension to an existing quarry is still a common and frequently approved proposal, and the arguments that carry it are the existing plant and infrastructure already on site, the absence of a new access and the fact that the alternative is a new greenfield quarry somewhere else.

Mineral Safeguarding Areas work the other way: they protect reserves from being built over by other development, and they are worth checking for any adjoining land you might want later.

A borrow pit is a different case again. It is temporary extraction to supply a specific construction project, justified by the haulage and carbon that would otherwise be spent importing material, and permitted for the duration of the works with restoration on completion. Make the link to the project explicit in the description of development and in the Planning Statement, because a borrow pit that outlives its project becomes an unauthorised quarry.

Dust, noise and blasting

National guidance sets numbers here, which makes the assessment unusually concrete.

Planning practice guidance on minerals gives noise limits for mineral workings expressed as an hourly equivalent continuous level at noise-sensitive properties, with a daytime ceiling of 55 decibels free field, lower limits for evenings and nights, and an allowance for temporary operations such as soil stripping and bund construction at up to 70 decibels for a limited number of weeks each year. Build the Noise Impact Assessment around those limits and around the background levels you measure, and present the temporary operations separately with their proposed duration.

Blasting is assessed on ground vibration measured as peak particle velocity at vibration-sensitive buildings, with guidance setting a level that should not be exceeded in 95 per cent of blasts and a higher absolute ceiling for any individual blast. Air overpressure and flyrock are managed through blast design rather than through planning limits. Most objections to blasting are about perception rather than damage, and the answer is a monitoring regime with published results and a direct line for complaints.

Dust assessment follows the Institute of Air Quality Management guidance on mineral dust, which separates the assessment of dust soiling from that of health-related particulate concentrations and works from source, pathway and receptor. An Air Quality Assessment covering haul road watering, sheeting, wheel washing, stockpile management, conveyor enclosure and a trigger-based suspension of operations in dry windy conditions is what the environmental health officer wants to see.

Water: dewatering, licensing and private supplies

Hydrogeology is where mineral applications most often fail, and it is also where the assessment work is most specialist.

Working below the water table means dewatering, and dewatering needs a water abstraction licence from the Environment Agency as well as planning permission. The two consents run in parallel and the Environment Agency will comment on the planning application as a consultee, so inconsistency between the two submissions is noticed. The assessment has to deal with the predicted cone of depression, effects on nearby abstractions including private water supplies, effects on groundwater-dependent wetlands and any designated sites, discharge of pumped water and its quality, and the position under the water environment regulations.

Private water supplies deserve particular care. A single farmhouse borehole within the predicted drawdown is enough to generate an objection that will not go away, and the usual answer is a monitoring and contingency scheme with a commitment to provide an alternative supply, secured by agreement rather than by condition.

Where the proposal affects an ordinary watercourse or a main river, separate consents apply, in the same way that works to a river bank need their own permissions alongside planning permission. Ground conditions, slope stability and face angles belong in a Geotechnical Assessment prepared to Eurocode 7.

Lorry movements and the highway network

Mineral traffic is heavy, repetitive and visible, and it generates more objections than any other aspect of a quarry application.

Quantify it honestly. Annual tonnage divided by payload gives loads, loads give two-way movements, and a seasonal and daily profile gives peaks. Present that alongside existing flows on the access road and the junction capacity assessment in the Transport Assessment. Where the extension does not increase output, say so plainly and support it with the permitted tonnage on the existing permission.

Routing is the mitigation that matters. A routing agreement under section 106, directing lorries to the strategic network and away from villages and schools, with a driver code of conduct, signage and a complaints log, is normal practice and is far more persuasive than a condition nobody can monitor. Expect a cap on daily or annual lorry movements, wheel washing, sheeting and a requirement to keep the public highway clean.

Landscape, bunds and phasing

A quarry is a hole, and the visual effect comes mostly from what sits around it: screening bunds, stockpiles, plant, lighting and the working face itself.

Phase the working so that each phase is screened by the one before it and restoration follows extraction rather than waiting for the end of life. Progressive restoration is the strongest landscape argument available, because it allows you to show the authority a sequence in which the disturbed area at any moment is a fraction of the total. Soil stripping and storage need their own section, with separate handling of topsoil and subsoil, maximum bund heights and a commitment not to trafficking stored soils.

The Landscape and Visual Impact Assessment should follow the third edition of the Guidelines for Landscape and Visual Impact Assessment, with viewpoints agreed with the authority and winter visualisations. Where the site sits in or near a National Landscape, the major development test in national policy becomes the governing issue and the application needs to confront it directly.

Night working and lighting are often the quickest concession to offer. A quarry that works daylight hours only has a much simpler case.

Restoration, aftercare and bonds

Restoration is the condition the authority cares about most, and it is the one that will still be live long after everyone involved has moved on.

Schedule 5 to the Town and Country Planning Act 1990 allows restoration conditions and aftercare conditions, with an aftercare period of five years as standard. The restoration scheme has to state the afteruse, the final landform with contours, soil placement depths, planting and seeding specifications, water management and the management regime through aftercare. Agriculture, forestry, amenity and nature conservation are the recognised afteruses, and nature conservation afteruses have become the default because they also carry the biodiversity gain the development needs.

On biodiversity, the gain condition under the Environment Act 2021 applies, with the statutory metric completed by a competent person and a biodiversity gain plan approved by the authority before development begins. Restoration to habitat can deliver the uplift on site, and the thirty-year management requirement sits comfortably alongside an aftercare scheme. Get the ecologist and the restoration designer in the same room early, because a landform designed for agriculture is expensive to redesign for habitat.

Financial guarantees come up regularly and national guidance treats restoration bonds as justified only in exceptional circumstances. Expect the authority to ask, and expect to argue.

Old permissions carry their own review process: permissions granted decades ago are subject to periodic review of mineral planning permissions, which updates conditions to modern standards. If the existing site is approaching a review, deal with the extension and the review together rather than sequentially.

The conditions that will be imposed

Expect conditions covering the permitted extraction area and depth, a phasing plan with plans for each phase, hours of operation and separate blasting hours and frequency, noise limits at named monitoring locations with a monitoring and reporting regime, a dust management scheme with suspension triggers, lorry movement caps and routing, wheel washing and highway cleaning, water monitoring at identified boreholes with contingency triggers, soil handling and storage, lighting, archaeological watching briefs where relevant, and a restoration and aftercare scheme with a five-year aftercare period.

Negotiate the monitoring regime rather than resisting it. A quarry with published monitoring data and a responsive complaints procedure has a far easier relationship with its authority at review, and the cost is trivial against the value of the reserve.

For specialist technical reports, qualified professional input may be required, and the hydrogeology, blasting and acoustic work on a mineral application is specialist by any standard. This is general guidance rather than legal advice, so check the position with your local planning authority or a qualified professional before relying on it.

You can browse the 66 report types by category to see which parts of a mineral evidence base can be drafted and which need a specialist author.

PlanScope provides AI-assisted draft reports for planning applications. Reports should be reviewed before submission. We do not guarantee planning approval.

Frequently asked questions

Who determines a quarry application?

The mineral planning authority. In two-tier areas that is the county council rather than the district, and in unitary, metropolitan and London borough areas the authority holds the function itself. Inside a National Park the National Park authority determines mineral applications. The development plan is the adopted minerals and waste local plan.

What noise limits apply to mineral workings?

Planning practice guidance on minerals sets limits expressed as an hourly equivalent continuous level at noise-sensitive properties, with a daytime ceiling of 55 decibels free field and lower limits for evenings and nights. Temporary operations such as soil stripping and bund construction are allowed a higher limit for a restricted number of weeks each year.

Does a quarry extension need an Environmental Impact Assessment?

Quarries and open-cast mining where the surface of the site exceeds 25 hectares fall within Schedule 1 to the Environmental Impact Assessment Regulations 2017, so an Environmental Statement is mandatory. Smaller proposals fall to Schedule 2 screening, where the sensitivity of the receiving environment and cumulative effects with existing workings matter.

What consents are needed for dewatering?

Working below the water table needs a water abstraction licence from the Environment Agency alongside planning permission, and the Agency will also comment as a planning consultee. The assessment must address the predicted drawdown, effects on nearby abstractions including private water supplies, groundwater-dependent habitats and the quality of discharged water.

How long does aftercare last?

Schedule 5 to the Town and Country Planning Act 1990 allows aftercare conditions with a standard aftercare period of five years following restoration. The restoration scheme itself should state the afteruse, final contours, soil placement depths, planting specifications and the management regime through the aftercare period.

Is a borrow pit treated differently from a quarry?

It is temporary extraction supplying a specific construction project, justified by avoided haulage, and permitted for the duration of those works with restoration on completion. Tie it explicitly to the project in the description of development, because a borrow pit that outlives its project becomes an unauthorised quarry.

Sources and further reading

mineralsquarryborrow pitrestorationproject guideseia

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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