SR2022 No 4: generic risk assessment – non-hazardous waste recycling with asbestos, hazardous batteries, cable and WEEE storage
Published 18 December 2024
Applies to England
The Environment Agency produces generic risk assessments for all standard rules permits. These list the potential risks and specify the measures (but they are not limited to) required to manage them.
Check this generic risk assessment to understand:
- the potential risks of waste storage, transfer and treatment including sorting, screening, separation, screening, baling, shredding, crushing and compaction
- how to manage the risks effectively
If your proposed activity has the same risks and can you apply for the standard rules permit
Each risk comprises:
- information about the source, pathway and receptor – and the potential harm to that receptor
- a judgement of the level of risk and justification of that judgement
- actions for managing the risk (through permitting) and a residual risk rating after managing it
Risk management involves breaking or limiting the source-pathway-receptor linkage to reduce the risk. If we set minimum distances we explain the basis of the distance, for example by modelling.
We will control the residual risk (after risk management) when we assess compliance.
If you need to check the meaning of any terms we have used (in the context of this risk assessment), see the explanation of terms.
Risk assessment parameters
This generic risk assessment is based on the following parameters.
Parameter 1
These permitted activities:
- acceptance and storage and repackaging of waste (R13, D14 and D15)
- sorting, screening, separation, screening, baling, shredding, crushing and compaction of waste for recovery (R3, R4, R5 and D9)
Parameter 2
The permitted waste types:
- are restricted to those listed in Tables 2.3a and 2.3b of the permit
Parameter 3
Quantity of waste accepted at the facility is restricted to:
- less than 75,000 tonnes each year
- 15,000 tonnes of waste listed in Table 2.3a stored prior to and after processing
- 40,000 tonnes of waste listed in Table 2.3b stored prior to and after processing
- no more than 10 tonnes of intact waste vehicle tyres stored at any one time
- no more than 50 tonnes of hazardous waste shall be stored at any one time
- no more than 10 tonnes of waste batteries shall be stored at any time
Parameter 4
All waste listed in Table 2.3a shall be stored and treated on an impermeable surface with sealed drainage system which meets a design standard.
Waste listed in Table 2.3b may be stored and treated on either hardstanding or on an impermeable surface with sealed drainage system.
Parameter 5
The only point source discharges to controlled waters are clean surface water from the roofs of buildings and from areas of the facility not used for the storage or treatment of wastes. No other direct or indirect discharges are permitted.
Parameters 6 to 7
The activities shall not be carried out within:
- 500 metres of a European site (within the meaning of Regulation 8 of the Conservation of Habitats and Species Regulations 2017) or a Site of Special Scientific Interest, including candidate or proposed sites or Maritime Conservation Zone
- a groundwater source protection zone 1 (SPZ1)
Parameter 8
All waste listed in Table 2.3a of this permit shall be stored and treated in an enclosed building. Covered containerised waste, baled and securely wrapped RDF, and baled wastes post treatment, may be stored either within a building, or in the open.
Parameters 9 to 15
Outdoor treatment of wastes listed in Table 2.3b of this permit must not take place within:
- 50 metres of a National Nature Reserve, Local Nature Reserve, Local Wildlife Site, Ancient woodland or Scheduled Ancient Monument;
- 50 metres of a site that has species or habitats protected under the Biodiversity Action Plan that the Environment Agency considers at risk to this activity;
- 50 metres of any well, spring or borehole used for the supply of water for human consumption (including private water supplies);
- 10 metres of an unculverted watercourse;
- a groundwater source protection zone 1;
- a specified Air Quality Management Area.
Parameter 16
Hazardous waste shall not be mixed, either with a different category of hazardous waste, or with other waste, substances or materials.
Parameter 18 and 19
Asbestos waste must be:
- double bagged, or where necessary, securely wrapped
- kept within clearly identified, segregated, sealed, secure, lockable bulk containers (for example skips) on an impermeable surface with sealed drainage system
Asbestos waste must not be:
- transferred between different bulk containers
- stored loose or in bays
Parameter 20
Batteries shall:
- be kept within a building
- be clearly identified and segregated from other wastes
- stored in secure containers that are leak-proof
Containers must be closed or stored under cover to prevent the accumulation of rainwater.
Lead acid batteries must be stored upright in secure containers that are leak-proof with an impermeable, acid-resistant base.
Lithium-ion batteries that are stored either separately, or as mixed batteries, must be marked as a fire hazard. Lithium-ion traction batteries are excluded.
Parameter 21
WEEE waste shall:
- be kept within clearly identified, segregated, secure containers that are leak- proof and covered to prevent the ingress of water
- stored on an impermeable surface with sealed drainage system
Parameter 22
There are no point source emissions to air. The only exception to this is if monitoring has indicated abatement is required for shredders treating waste containing Persistent Organic Pollutants.
If required, the abatement system must be designed and maintained to ensure the emission does not exceed 5mg/m3 dust.
Parameter 23
Secondary containment follows the recommendations of CIRIA 736 report.
Parameter 24
Separately collected food waste must be:
- stored on an impermeable surface with sealed drainage system
- clearly identified and segregated from other wastes and stored in a dedicated reception, storage, and handling area which is cleaned and disinfected at least weekly
- stored in either within an enclosed building, or within rigid sealed containers, sealed skips or sealed bulk trailers
- removed from site by the end of the working day unless an alternative has been agreed in writing
1. Risk to local human population
1.1 Release of particulate matter (dust) and micro-organisms (bioaerosols)
Dust and bioaerosols travel through the air and can be:
- inhaled, ingested or inoculated
- deposited on garden fruit and vegetables and then ingested
There is a risk of dust and bioaerosols causing:
- respiratory irritation and illness
- gastro-intestinal illness
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as medium
- overall severity of potential consequences as medium
- overall risk rating as medium
The reasons for giving the activity this rating are because:
- permitted waste types are non-hazardous and do not include dusts, powders or loose fibres (except for 20 01 41 wastes from chimney sweeping)
- there is the potential to produce bioaerosols
- treatment activities include transfer, sorting, bulking, separation, screening, baling, shredding, crushing and compaction
- there is potential for exposure to anyone living or working close to the site (excluding operator and employees)
- there is potential for dust generation from the transfer and treatment activities during prolonged dry periods for example summer months
Managing the risk
All waste listed in Table 2.3a of this permit shall be stored and treated in an enclosed building. Covered containerised waste, baled and securely wrapped RDF, and baled wastes post treatment, may be stored either within a building, or in the open.
Outdoor treatment of wastes listed in Table 2.3b of this permit (for example, concrete, bricks, tiles, sand, gravels etc) cannot take place within an Air Quality Management Area.
The permit requires emissions of substances not controlled by emission limits (excluding odour) shall not cause pollution.
The following actions also need taking:
- all appropriate measures shall be followed as documented in the management system
- if required, an emissions management plan must be submitted and a risk assessment review done
- the emissions management plan is implemented if one is required
Taking these actions will control the risk and rate it as ‘low’.
1.2 Waste, litter and mud on local roads
Vehicles entering and leaving the site risk causing:
- nuisance
- loss of amenity
- road traffic accidents
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as medium
- overall severity of potential consequences as medium
- overall risk rating as medium
The reasons for giving the activity this rating are because:
- there is a risk of creating unsafe road surfaces in wet weather
- local residents are often sensitive to mud on roads
Managing the risk
Risk management is the same as risk 1.1 along with:
- waste types that pose a risk of windblown litter are listed in Table 2.3a and must be stored and treated within a building. Covered containerised waste, baled and securely wrapped RDF, and baled wastes post treatment, may be stored either within a building, or in the open
- waste types in Table 2.3b pose a low risk of windblown litter
- appropriate measures are required to prevent and minimise emissions, including mud tracking from site and litter must be documented in the management system
- if required, an emissions management plan must be submitted and a risk assessment review done
- the emissions management plan is implemented if one is required
Taking these actions will control the risk and rate it as ‘low’
1.3 Odour
Odour travels through the air and can be inhaled. There is a risk of causing:
- nuisance
- loss of amenity
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as medium
- overall severity of potential consequences as high
- overall risk rating as high
The reason for giving the activity this rating is because the waste types in Table 2.3a could be odorous.
Managing the risk
To manage the risk the standard rules permit requires:
- storage and treatment of wastes listed in Table 2.3a must be done within an enclosed building, with covered containerised waste, baled and securely wrapped RDF stored either within a building, or in the open
- emissions shall be free from odour at levels likely to cause pollution
- there are additional controls and requirements for food waste storage
- an odour management plan should be produced and implemented if required
Taking these actions will control the risk and rate it as ‘low’.
1.3 Noise and vibration
Noise travels through the air and vibration through the ground. There is a risk of causing:
- nuisance
- loss of amenity for local residents and workplaces
- loss of sleep
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as low
- overall severity of potential consequences as medium
- overall risk rating as medium
The reason for giving the activity this rating is because local residents are often sensitive to noise and vibration.
Managing the risk
To manage the risk the standard rules permit requires:
- emissions are free from noise and vibration at levels likely to cause pollution
- treatment of Table 2.3b wastes must be done within an enclosed building if the facility is within 200 metres of another workplace or residential dwelling
- treatment of Table 2.3a wastes must be done within an enclosed building
- a noise and vibration management plan to be implemented if required
Taking these actions will control the risk and rate it as ‘low’.
1.4 Scavenging animals and birds
Animals and birds travel over land and through the air. There is a risk of causing:
- nuisance
- loss of amenity
- harm to human health from waste carried off-site and from faeces
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as medium
- overall severity of potential consequences as high
- overall risk rating as medium
The reason for giving the activity this rating is because the permitted wastes could attract scavenging animals and birds.
Managing the risk
To manage the risk the standard rules permit:
- allows outside storage of Table 2.3b wastes and these waste types pose a low risk of attracting scavenging animals or birds
- requires Table 2.3a wastes to be stored and treated in a building with the exception of covered containerised waste, baled and securely wrapped RDF, and baled wastes post treatment which may be stored either within a building, or in the open
- can require an emissions management plan and changes to the management system to prevent or control scavenging animals or birds
Taking these actions will control the risk and rate it as ‘low’.
1.5 Pests such as flies
Pests, such as flies can travel through the air or over land. There is a risk of causing:
- nuisance
- loss of amenity
- harm to human health We have judged the:
- likelihood of the hazard affecting the receptor as medium
- overall severity of potential consequences as high
- overall risk rating as medium
The reason for giving the activity this rating is because some of the permitted wastes may attract pests, such as flies.
Managing the risk
To manage the risk the standard rules permit:
- requires wastes in Table 2.3a must be stored and treated within an enclosed building
- the exception to the requirement above is for covered containerised waste, baled and securely wrapped RDF, and baled wastes post treatment which may be stored either within a building, or in the open – these wastes should not attract flies
- can require an emissions management plan and changes to the management system to prevent or control pests, such as flies
Taking these actions will control the risk and rate it as ‘medium’.
2. Risk to local human population and local environment
2.1 Flooding of the site
Water can flood the site during heavy or prolonged rainfall.
There is a risk of waste washed off-site contaminating buildings, gardens and natural habitats downstream.
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as low
- overall severity of potential consequences as medium
- overall risk rating as medium
The reasons for giving the activity this rating are because:
- the majority of permitted waste types are non-hazardous and Table 2.3a waste must be stored and treated within an enclosed building
- covered containerised waste, baled and securely wrapped RDF, and baled wastes post treatment may be stored either within a building, or in the open
- leachate may have a high biological oxygen demand (BOD) and suspended solids
Managing the risk
Standard rules permits are not usually issued in flood risk areas. To manage the risk the standard rules permit requires:
- compliance with the sensitive location exclusions
- a written management system that identifies and documents the process controls to minimise the risk of pollution – includes those arising from operations, maintenance, accidents, incidents and non-conformances
The accident management section of the management system covers:
- assessing the risk of flooding and measures to prevent or reduce the risk
- contingency plans for diversion of waste, if required
- emergency procedures which are clearly communicated to all site operatives
Taking these actions will control the risk and rate it as ‘low’.
2.2 Fire risk
There is a risk of fire on-site from:
- arson and, or vandalism
- spontaneous combustion from uncontrolled decomposition
Fire can cause:
- polluting materials (smoke or fumes) to travel through the air, water or over land
- spillages and contaminated firewater by direct run-off from the site and through surface water drains and ditches
We have assessed the potential harm as:
- respiratory irritation, illness and nuisance to the local population
- injury to staff, firefighters or arsonists and vandals
- air, water or land pollution
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as high
- overall severity of potential consequences as high
- overall risk rating as high
The reason for giving the activity this rating is because there are combustible wastes are listed in Table 2.3a of the permit.
Managing the risk
To manage the risk the standard rules permit requires:
- a written management system that identifies and minimises risks of pollution, including those arising from operations, maintenance, accidents, incidents, non-conformances - therefore includes measures to prevent and control fires, including containment of fire waters
- a site specific fire prevention plan
- a robust waste acceptance procedure
- no burning of wastes
Taking these actions will control the risk and rate it as ‘medium’.
3. Risk to local human population, livestock and wildlife
3.1 Litter on surrounding land and in final material
Litter can travel through the air and then be deposited on land. There is a risk of causing:
- nuisance
- loss of amenity
- harm to animal health
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as low
- overall severity of potential consequences as medium
- overall risk rating as low
The reasons for giving the activity this rating are because:
- local residents are sensitive to litter
- waste types listed in this permit likely to produce litter must be stored and treated in a building
Managing the risk
To manage the risk the standard rules permit requires:
- wastes listed in Table 2.3a are stored and treated in a building. Covered containerised waste, baled and securely wrapped RDF, and baled wastes post treatment, may be stored either within a building, or in the open
- a management system with waste pre-acceptance and acceptance procedures that reduce the risk of accepting unpermitted waste
- compliance with the ‘emissions of substances not controlled by emission limits’ rule, submitting an emissions management plan, if necessary
- operators to follow appropriate measures guidance
Taking this action will control the risk and rate it as ‘low’.
3.2 Gaining unauthorised access to site
There is a risk of direct physical contact with all on-site hazards such as wastes, machinery and vehicles.
There is a risk of causing injury to humans or livestock.
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as low
- overall severity of potential consequences as low
- overall risk rating as low
The reason for giving the activity this rating is because the management system includes procedures for worker and visitor safety.
Managing the risk
To manage the risk the standard rules permit requires:
- activities shall be managed and operated in accordance with all appropriate measures and a documented and implemented management system that stipulates all preventative measures and emergency responses should accidents occur (including site security measures to prevent unauthorised access)
- emergency contact details shall be displayed at the site entrance
- visitors should receive a health and safety induction when visiting and must follow the site operator’s instructions
Taking this action will control the risk and rate it as ‘low’.
4. Risk to surface waters close to and downstream of site
4.1 Risk of pollution causing acute effects
There is a risk of pollution from spillage of liquids, leachate from waste, contaminated rainwater run-off from waste with high organic and ammonia content and suspended solids.
Contamination can travel through direct run-off from site over the land, surface water drains and ditches.
We have assessed the acute effects as follows:
- oxygen depletion
- fish kill
- algal blooms
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as low
- overall severity of potential consequences as low
- overall risk rating as low
The reason for giving the activity this rating are because:
- there is potential for contaminated rainwater run-off from waste operations, especially during heavy rain
- leachate may contain suspended solids or organic matter
Managing the risk
To manage the risk the standard rules permit requires:
- all operations are more than 10 metres from a watercourse and excluded from SPZ1
- non-hazardous and hazardous waste listed in Table 2.3a must be treated in a building with impermeable pavement and sealed drainage. Covered containerised waste, baled and securely wrapped RDF, and baled wastes post treatment, may be stored either within a building, or in the open on impermeable surface and sealed drainage.
- a written management system that identifies and documents the process controls to minimise the risk of pollution – includes those arising from operations, maintenance, accidents, incidents and non-conformances
- all liquids must be in containers with secondary containment meeting CIRIA 736
- run-off is restricted by the ‘emissions of substances not controlled by emissions limits’ rule
- appropriate measures guidance to be followed
- flood risk contingency plan for diversion of waste can be activated
- emergency procedures and contingency plans to be clearly communicated to all site operatives
Taking these actions will control the risk and rate it as ‘low’.
4.2 Risk of pollution causing chronic effects
There is a risk of pollution from:
- liquid spills
- leachate from waste
- contaminated rainwater run-off from waste Contamination can travel by:
- direct run-off from site over the land, through surface water drains and ditches
- indirect run-off through soil
We have assessed the chronic effect as deterioration to water quality.
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as low
- overall severity of potential consequences as low
- overall risk rating as low
The reason for giving the activity this rating is because pollution is likely to be detected quickly and the effects are temporary and reversible.
Managing the risk
To manage the risk, take the actions for risk 4.1 along with:
- all liquids must be in containers with secondary containment
- run-off is restricted by the ‘emissions of substances not controlled by emission limits’ rule
- using drainage plans to separate clean and dirty water
- considering this risk in an accident management plan
Taking these actions will control the risk and rate it as ‘low’
5. Risk to water abstracted from a watercourse
These risks relate to watercourses downstream of a facility and to water for agricultural or potable use.
This receptor is at risk from:
- liquid spills
- leachate from waste
- contaminated rainwater run-off from waste
There is a risk of contaminants travelling through direct run-off from the site across ground surface, via surface water drains and ditches and finally through abstraction. This could have acute effects and cause the closure of abstraction intakes.
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as low
- overall severity of potential consequences as medium
- overall risk rating as low
The reason for giving this rating is due to the potential for contaminated rainwater run-off from waste operations carried out in the open, especially during heavy rain.
Managing the risk
To manage this risk, take the actions set out in risks 4.1 and 4.2.
Taking these actions will control the risk and rate it as ‘low’.
6. Risk to groundwater
Groundwater is at risk from:
- liquid spills
- leachate from waste
- contaminated rainwater run-off from waste
There is a risk of contaminants travelling through soil and groundwater which can then be abstracted from a borehole. This could have a chronic effect resulting in the groundwater requiring treatment or causing closure of a borehole.
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as low
- overall severity of potential consequences as medium
- overall risk rating as low
We have given this rating because of the potential for contaminated rainwater run-off or leachate from waste operations, especially during heavy rain. The consequence is based on the possibility of pollution not being detected for a long time.
Managing the risk
To manage the risk the following actions must be taken:
- the activities shall not be carried out within a groundwater SPZ1
- table 2.3a wastes must be stored and handled within a building – covered containerised waste, baled and securely wrapped RDF, and baled wastes post treatment, may be stored either within a building, or in the open but all table 2.3a waste must be stored and treated on an impermeable surface with sealed drainage system to prevent contaminated run-off
- secondary containment meets CIRIA 736 standards
Taking these actions will control the risk and rate it as ‘low’.
7. Risk to protected sites
Protected sites include:
- National Parks and Areas of Outstanding Natural Beauty
- Marine Conservation Zones
- Sites of Special Scientific Interest
- Special Areas of Conservation
- Special Protection Areas
- Ramsar wetland sites
Protected sites can be at risk from any source and by any pathway.
The risk of harm to protected sites include (but are not limited to) the following:
- nutrient enrichment
- leachate
- contaminated surface water run off
- smothering
- disturbance
- predation
Judgement of risk
We have judged the:
- likelihood of the hazard affecting the receptor as low
- overall severity of potential consequences as low
- overall risk rating as low
The reason for giving the activity this rating is because storing and transferring waste may cause harm to and deterioration of nature conservation sites.
Managing the risk
To manage the risk we require compliance with the standard rules permit, including applying exclusion distances.
Taking this action will control the risk and rate it as ‘low’.
Explanation of terms
Receptor
The things at risk and that need protecting.
Receptors considered include atmosphere, land, surface waters, groundwater, humans, wildlife and their habitats.
A single receptor may be at risk from several different sources and all must be addressed.
Source
The agent or process that has the potential to cause harm.
A contaminant or pollutant (a hazard) that has the potential to cause harm. For example, the activity or operation taking place for which a particular hazard may arise.
Harm
The harmful consequence to the receptor if the hazard is realised.
Pathways
The route or means by which a defined hazard may affect a receptor.
Source-pathway-receptor linkage
There has to be a link between the source, pathway and receptor for there to be a risk.
Likelihood of exposure
This is the likelihood of the receptors being exposed to the hazard. The meaning of the definitions are:
- high – exposure is probable – direct exposure is likely with no or few barriers between the hazard source and the receptor
- medium – exposure is fairly probable - feasible exposure is possible as the barriers to exposure are less controllable
- low – exposure is unlikely – several barriers exist between the hazard source and receptor to reduce exposure
- very low – exposure is very unlikely – effective, multiple barriers are in place to reduce exposure
Overall magnitude of potential consequence
This is the severity of the consequence if the hazard is realised and may cause actual or potential harm.
This will have a high, medium, low or very low rating using attributes and scaling to consider ‘harm’.
Risk rating
We work out the risk rating by combining the likelihood of exposure with the magnitude of the potential consequences.
We assign these ratings:
- high risk – requires additional assessment and active management
- medium risk – requires additional assessment and may need active management and, or monitoring (or both)
- low and very low risks – require a periodic review