Noise, Air, Odour and Light

Odour and noise from a crematorium or similar facility

7 min readBy PlanScope Editorial Team

Emissions from cremators sit with the environmental permitting regime, while planning controls location, stack height, traffic and plant noise. What the application has to evidence, and which conditions to expect.

A crematorium application sits across two regulatory regimes, and most of the objections an applicant receives are aimed at the wrong one. Emissions from the cremators themselves are controlled by the local authority as a permitting authority under the Environmental Permitting Regulations 2016, using the national process guidance for crematoria. Planning controls the location, the stack as a structure, the traffic, the noise from plant and vehicles, and the effect on neighbours.

Start with the statutory separation, because it is absolute and it is old. Section 5 of the Cremation Act 1902 prevents a crematorium being built within 200 yards of any dwelling house, except with the written consent of the owner, lessee and occupier, and within 50 yards of any public highway. That has nothing to do with planning policy and it cannot be conditioned away.

The regulatory split between planning and process control

The permit does the work on emissions. A crematorium is a Part B installation, so the local authority issues and enforces the permit, applying the emission limits, monitoring requirements and abatement expectations in the Secretary of State's process guidance note for crematoria. Mercury from dental amalgam is the emission that drives the abatement plant, and the national approach expects operators to abate a proportion of cremations or participate in a burden sharing arrangement.

What that means for the planning application is simple and often misunderstood. The planning authority should not duplicate the permit, and an objection that the cremators will exceed an emission limit is a matter for the permitting regime. The planning authority can and should consider whether the installation can be built and operated in a location where the resulting emissions are acceptable, which is a question about stack height, dispersion and the position of sensitive receptors.

Say this plainly in the supporting statement, with a cross reference to the permit application, and the officer's report usually follows it.

Emissions abatement and stack design

The abatement plant is large, and it is a planning issue because of its size rather than its chemistry. Filtration and mercury abatement equipment needs a building, and the stack has to be high enough for the plume to disperse.

Stack height is determined by dispersion modelling rather than by a rule of thumb, taking account of building downwash from the crematorium itself and from nearby structures, local topography and the height and distance of sensitive receptors. Expect the modelling to produce a height that the architect dislikes. Expect also to be asked whether the stack can be concealed within a tower or chimney feature, which is usually possible and occasionally makes dispersion worse.

The same dispersion reasoning applies to flues on other combustion plant, and the Clean Air Act chimney height approval process runs alongside planning, as we set out in chimney heights, biomass boilers and the Clean Air Act.

Three points to settle before the drawings are fixed:

  1. The modelled stack height, with the model inputs recorded.
  2. Whether the abatement plant can be housed within the main building envelope or needs a separate structure.
  3. The flue route, which on a building with a low pitched roof is harder to resolve than the stack height itself.

Separation distances and receptor sensitivity

The 1902 Act distances are the floor, not the target. In practice the sensitive receptors that matter are dwellings, schools, care homes and allotments, and the assessment should identify them by distance and direction from the stack.

An Air Quality Assessment for a crematorium normally covers the modelled ground level concentrations at those receptors, the predicted contribution against the relevant air quality objectives, and the position within or outside any air quality management area. Where the site is within a management area the authority will expect the assessment to address the local action plan.

Receptor sensitivity cuts both ways. A crematorium next to an industrial estate is a straightforward case. One at the edge of a village, with the nearest dwellings at 210 yards and a primary school 400 m away, needs the assessment to do real work, and the application is better served by a frank discussion of the worst case than by an optimistic set of inputs.

Traffic, queuing and dispersal noise

Noise from a crematorium is almost entirely vehicular and human. Cremator plant, abatement fans and the cooling system produce a steady source assessed under BS 4142:2014+A1:2019 against the background sound level at the nearest residential facade. That part is routine.

The part objectors raise is the pattern of services. A crematorium running services at 45 minute intervals from 9am to 4pm generates arrival and departure peaks, with cars leaving in groups, doors closing and people talking in the car park. None of that is loud. It is noticeable because it is repeated and because it happens at a time of day when a residential street is otherwise quiet.

Three mitigations carry weight with environmental health officers:

  • Car park layout that puts parking away from the boundary with dwellings, with the chapel building acting as a screen
  • A one way internal circulation route that avoids reversing and manoeuvring near the boundary
  • Service intervals long enough that arrivals and departures do not overlap, which also answers the queuing objection

Where monitoring is needed to establish the background level, the duration and position of the measurements decide whether the assessment stands up, and we cover that in unattended noise monitoring, duration, position and validity.

Queuing on the public highway is the objection most likely to attract a formal consultee response. The highway authority will want to see that the internal layout can hold the vehicles associated with two consecutive services without any queue reaching the highway.

Landscape and screening expectations

Crematoria are usually in open or semi rural settings, which brings landscape and visual effects into the assessment alongside the technical work. The memorial garden, the garden of remembrance and the parking are all part of a designed landscape setting rather than afterthoughts.

Officers tend to ask for four things. A landscape scheme that screens the car park and the plant from public viewpoints without screening the chapel itself. Boundary planting that is native and local in character, planted at a size that gives effect within a few years. Lighting designed to the minimum necessary, with the car park and route lighting controlled to avoid light spill into the surrounding area. And a clear separation between the arrival and departure routes so that mourners do not meet the next service.

Lighting deserves its own assessment where the site is in a dark area, because a car park lit to an urban standard in a rural setting is visible for a long way.

Consultee positions

Who responds, and what they usually say:

Consultee Usual focus
Environmental health Plant noise under BS 4142, dispersion inputs, hours of cremation, permit interface
Local highway authority Access geometry, internal capacity for two services, no queuing on the highway
Lead local flood authority Surface water from a large car park, attenuation and discharge rate
Parish or town council Separation from dwellings, traffic through the village, landscape effect
Neighbouring occupiers Emissions, traffic, and the 1902 Act distances

The permitting team within the same authority is worth engaging early even though it is not a planning consultee. A permit officer who has seen the stack height modelling before the planning application is submitted is unlikely to contradict it later.

Conditions typically imposed

Expect most of the following, and propose the wording yourself where you can:

  • Hours during which cremations may take place, and separate hours for services
  • Maximum number of cremations in any day, which controls intensification
  • Plant noise limit expressed as a rating level at a defined facade, with a verification test after installation
  • Stack height and abatement plant to be built as approved and retained
  • Landscape scheme, implementation in the first planting season and replacement of failures
  • External lighting scheme with illuminance limits at the boundary
  • Internal circulation and parking to be laid out before the use starts
  • A travel plan or management plan where services are frequent

A Noise Impact Assessment that proposes its own verification condition is far more likely to be accepted than one that leaves the authority to invent the wording. Draft the condition, state the test method, and name the receptor.

The same framework applies to comparable facilities, including animal crematoria and small waste combustion plant, with the permitting regime and the applicable process guidance note changing. Check which guidance note applies before you model anything.

Enter your postcode on PlanScope to see which environmental documents a facility of this kind is likely to need.

This is general guidance rather than legal advice. Check the position with your local planning authority 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

How far must a crematorium be from the nearest house?

Section 5 of the Cremation Act 1902 prevents construction within 200 yards of any dwelling house without the written consent of the owner, lessee and occupier, and within 50 yards of a public highway. The restriction is statutory and cannot be set aside by planning condition. It is a minimum rather than a planning judgement, so greater separation may still be required.

Does planning control cremator emissions?

Not directly. A crematorium is a Part B installation under the Environmental Permitting Regulations 2016, permitted and enforced by the local authority applying the national process guidance for crematoria. Planning considers whether the installation is acceptable in that location, which turns on stack height, dispersion modelling and the position of sensitive receptors.

What noise assessment is needed?

An assessment to BS 4142:2014+A1:2019 for fixed plant such as abatement fans and cooling, comparing the rating level with the measured background sound level at the nearest residential facade. Vehicle arrivals, departures and car park activity are usually addressed through layout, circulation design and service intervals rather than against a numerical standard.

Will the council limit the number of cremations?

Often yes, by condition, to control intensification and the associated traffic and emissions. A daily maximum and defined hours for cremation and for services are common. Negotiate the figure at application stage with reference to the service interval and the car park capacity, because varying it later needs a further application.

Who should prepare the dispersion modelling?

A suitably qualified air quality specialist. Councils expect modelling by an experienced practitioner, with the inputs, model version, meteorological data and receptor locations recorded so the work can be checked. Professional review is strongly advised, and for specialist technical reports qualified professional input may be required.

Sources and further reading

crematoriumair qualitynoiseenvironmental permittingodour

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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