Does PUWER apply to my business?

If your business uses any kind of equipment at work, from a drill or a delivery van to a photocopier or a kitchen mixer, the short answer is almost certainly yes. PUWER, the Provision and Use of Work Equipment Regulations 1998, applies to the vast majority of workplaces in Great Britain. This guide explains who has to comply, what counts as work equipment, the few situations where PUWER does not apply, and what you should do next.

What is PUWER?

PUWER is the common name for the Provision and Use of Work Equipment Regulations 1998 (SI 1998/2306). The regulations have been in force since 5 December 1998 and sit under the Health and Safety at Work etc. Act 1974. Their purpose is simple: work equipment must be suitable for the job, safe to use, properly maintained, and used only by people who have been told and trained how to use it safely.

The Health and Safety Executive (HSE) enforces PUWER and publishes the supporting Approved Code of Practice and guidance, known as L22 (Safe use of work equipment, fourth edition).

The short answer: who does PUWER apply to?

PUWER places duties on anyone who owns, operates or has control over work equipment. In practice, it applies to:

  • Employers whose employees use work equipment, whether the business owns the equipment or not
  • Self-employed people who use work equipment in their own work
  • Anyone who controls how work equipment is used, such as managers and supervisors
  • Businesses that provide equipment for others to use at work, including hire companies

The size of your business makes no difference. A sole trader with a ladder and a power tool has PUWER duties just as a manufacturer with a hundred machines does. What changes is how much you need to do to manage the risk.

Worker checking use of concrete hammer machinery as part of a PUWER inspection
Work Equipment

What counts as “work equipment”?

The definition is deliberately wide. Work equipment means any machinery, appliance, apparatus, tool or installation used at work, whether exclusively or not. That includes:

  • Hand tools: hammers, knives, screwdrivers, power drills and saws
  • Machinery: lathes, presses, conveyors, packaging machines and woodworking equipment
  • Mobile equipment: forklift trucks, pallet trucks, dumpers and ride-on mowers
  • Access equipment: ladders, stepladders and mobile platforms
  • Catering equipment: slicers, mixers, ovens and fryers
  • Office equipment: photocopiers, shredders, guillotines and even office chairs
  • Laboratory and workshop equipment: fume cupboards, centrifuges, compressors and benches

If your workers bring their own tools or equipment to work and you allow them to use it, PUWER applies to that equipment too. Equipment you hire or borrow is covered in the same way as equipment you own.

When does PUWER not apply?

There are only a few limited exceptions:

  • Equipment used by members of the public, such as a customer using a self-service machine, is not covered by PUWER, although other health and safety duties still apply to you.
  • Domestic work in a private household: equipment used by a domestic worker, such as a cleaner, in a private home is not covered unless it was supplied by their employer or by the worker as a self-employed person.
  • Workplaces outside Great Britain’s regime: PUWER covers England, Scotland and Wales. Northern Ireland has its own equivalent regulations, and the Isle of Man and the Republic of Ireland have separate legislation. If you operate across more than one jurisdiction, each site needs checking against its own rules.

If you are unsure whether you fall inside an exception, the safest approach is to assume PUWER applies and manage your equipment accordingly.

What does PUWER require you to do?

PUWER sets out general duties that apply to all work equipment, plus extra requirements for particular types such as mobile equipment and power presses. The core requirements are:

  1. Suitability. Equipment must be suitable for its intended use and for the conditions it will be used in.
  2. Maintenance. Equipment must be kept in efficient working order and in good repair. Keeping a maintenance log is strongly recommended.
  3. Inspection. Where safety depends on how equipment is installed or where it deteriorates over time, it must be inspected by a competent person and the results recorded.
  4. Specific risks. Where equipment poses particular risks, its use, repair and maintenance must be restricted to people trained to do the job.
  5. Information and instructions. Users and supervisors must have clear health and safety information and, where appropriate, written instructions.
  6. Training. Everyone who uses work equipment, and those who manage or supervise them, must be adequately trained.
  7. Dangerous parts. Access to dangerous moving parts must be prevented or controlled, for example with guards, interlocks or trip devices.
  8. Controls and isolation. Start, stop and emergency stop controls must be clearly marked, accessible and effective, and equipment must be able to be isolated from its energy source.
  9. Stability, lighting and markings. Equipment must be stable, adequately lit, and carry the markings and warnings needed for safe use.

Equipment supplied for use at work must also meet the relevant product-safety requirements, which is normally shown by UKCA or CE marking.

PUWER and other regulations

PUWER rarely works alone. Depending on your equipment, other regulations may apply in addition:

Where more specific regulations apply, you still need to meet the general PUWER requirements as well.

What happens if you do not comply?

HSE inspectors can issue improvement or prohibition notices, and serious breaches can lead to prosecution with unlimited fines for businesses and, in some cases, imprisonment for individuals. Beyond enforcement, poorly maintained or unsuitable equipment is a leading cause of workplace injuries, and a breach of PUWER will weigh heavily against you in any civil claim or insurance dispute.

Practical steps: how to check and achieve PUWER compliance

If you have worked out that PUWER applies to your business, a sensible approach looks like this:

  1. Make an equipment register. List everything your people use, including hired, borrowed and employee-owned items.
  2. Risk assess each item. Consider how it is used, by whom, where, and what could go wrong. Focus most effort on higher-risk equipment.
  3. Check suitability and safeguards. Confirm guards, controls, emergency stops and markings are in place and working.
  4. Set up maintenance and inspection routines. Agree frequencies based on the manufacturer’s instructions and your risk assessment, and keep written records.
  5. Train and instruct your people. Record who has been trained on what, and refresh training when equipment or tasks change.
  6. Review regularly. Revisit your register and assessments after incidents, near misses, new purchases or changes to the work.

A competent person, internal or external, should carry out inspections where PUWER requires them. A health and safety consultant can also audit your arrangements, spot gaps and help you build a proportionate system that works in practice.

Frequently asked questions

Does PUWER apply to offices?

Yes. PUWER applies to all work equipment in all workplaces covered by the Health and Safety at Work etc. Act, including offices. The risks are usually lower, but items such as shredders, guillotines, trolleys, stepladders and even chairs are still work equipment.

Does PUWER apply to self-employed people?

Yes. Self-employed people must make sure the equipment they use for their own work is safe and suitable.

Does PUWER apply to hired or leased equipment?

Yes. If you use hired equipment, you are responsible for how it is used and for making sure it is suitable. The hire company also has duties as a provider of work equipment.

How often does PUWER equipment need to be inspected?

PUWER does not set a fixed frequency. Inspection intervals depend on the equipment, how and where it is used, and how quickly it deteriorates, so they should come from your risk assessment and the manufacturer’s instructions. Lifting equipment is different, because LOLER sets specific thorough examination intervals.

Is there a difference between PUWER and LOLER?

Yes. PUWER covers all work equipment, while LOLER applies specifically to lifting equipment and lifting operations. Lifting equipment is subject to both.

Do I need a PUWER certificate?

There is no such thing as a general PUWER certificate. What you need is evidence that your equipment is suitable, maintained, inspected where required, and used by trained people, backed by good records.

Not sure where your business stands?

If you would like help working out how PUWER applies to your equipment, carrying out a PUWER risk assessment or setting up an inspection and maintenance system, get in touch with our team for a no-obligation conversation.

If you require help identifying legislation applicable to your workplace, please contact one of our team.

This article is general guidance for businesses in Great Britain and is not legal advice. Check the current regulations and HSE guidance for your circumstances.

HSE Safety Formulas and Calculations: A Practical Guide

Why safety is a numbers game

You can only improve health and safety performance if you measure it consistently, and the same handful of formulas underpins almost every serious safety dashboard. This guide walks through the 37 calculations and explains what each one tells you, and shows what it is used for.

The formulas fall into ten groups: injury rates, workforce exposure, audit and compliance, risk, emergency readiness, behavioural observations, contractors, leading and lagging indicators, additional rates, and the mindset that ties them together. Numbers do not make a workplace safe by themselves. Used well, they show where the gaps are, whether controls are working, and where to spend time and money next.

Before you calculate: pick your basis and definitions

Two companies can report very different accident rates for the same performance simply because they use different multipliers or definitions. Settle three things before you compare any number.

  • The multiplier. Rates are scaled so that small and large organisations can be compared fairly.
  • The definition of each case type. What counts as a lost time injury, a recordable case or a restricted work case varies between organisations, clients and regulators.
  • The denominator. Hours worked is the most accurate exposure measure. Headcount or estimated hours are weaker substitutes.
MultiplierTypical useWhat it represents
200,000 hoursUS OSHA-style rates such as TRIR and DARTAbout 100 full-time employees working a year
1,000,000 hoursLTIFR, frequency rate, near-miss rate, and many international client and industry reportsOne million hours of exposure
100,000 workersUK HSE national statistics, which are expressed per 100,000 employees rather than per hoursA standardised workforce size

Always follow the basis your client, industry body or reporting system specifies, and state the basis next to every figure you publish.

1. Safety performance: injury and incident rates

These eight rates turn raw injury counts into comparable figures. They are the core of most client and board safety reports.

Frequency Rate (FR) shows how often lost time injuries (LTIs) occur per million hours worked. Use it to track whether injuries are becoming more or less common over time.

  • FR = LTIs x 1,000,000 / Man-hours worked

Severity Rate (SR) shows how many working days are lost per million hours. It tells you how serious injuries are, not just how many there are. Divide SR by FR (on the same basis) to get the average days lost per lost time injury.

  • SR = Lost workdays x 1,000,000 / Man-hours worked

Lost Time Injury Frequency Rate (LTIFR) is the most widely quoted headline measure in contractor pre-qualification and tender questionnaires.

  • LTIFR = LTIs x 1,000,000 / Hours worked

Total Recordable Incident Rate (TRIR) counts every recordable case, not only those that cost working days. It gives a fuller picture of injury performance than LTIFR and is standard in US-linked and oil and gas supply chains.

  • TRIR = Recordable cases x 200,000 / Hours worked

DART Rate covers cases involving days away from work, restricted work or job transfer. It highlights injuries serious enough to change what a person can do at work.

  • DART = DART cases x 200,000 / Hours worked

Lost Workday Case Rate (LWDC) counts only cases where the person was away from work, which makes it a narrower, stricter measure than TRIR.

  • LWDC = LWDC x 200,000 / Hours worked

Incident Rate applies the same approach to all incidents, so it can include damage-only events and other non-injury incidents depending on how you define an incident.

  • Incident Rate = Number of incidents x 200,000 / Hours worked

Near-Miss Rate measures how many near misses are reported per million hours. Unlike the other rates, a higher figure here is often a good sign, because it suggests people are reporting events that could have caused harm.

  • Near-miss Rate = Near misses x 1,000,000 / Man hours worked
HSE safety formulas and caluculations
Health and safety calculations and formulas

2. Man-hours and workforce: measuring exposure

Every rate in the previous section depends on one number: hours worked. Get this wrong and every other figure is wrong with it.

Man-hours worked is the total exposure for a period. Use actual hours, including overtime and agency or temporary labour, and exclude leave and sickness.

  • Man-hours = Workers x Working hours x Working days

Average workforce converts total hours back into an equivalent number of full-time people. It is useful when headcount changes during the year, for example on a project that ramps up and down.

  • Average workforce = Total man-hours worked in the period / Standard working hours per person in the period


Safe man-hours % shows the proportion of hours worked without a recordable or lost time injury. It is a positive, easy-to-communicate measure for site boards. Many organisations instead report a running total of safe man-hours since the last lost time injury, so check which version your audience expects.

  • Safe man-hours % = Safe man-hours / Total man-hours x 100


Absenteeism % measures the share of available working days lost to absence. It is a workforce health indicator rather than a pure safety measure, but a sustained rise can point to fatigue, stress, poor welfare or underlying health problems worth investigating.

  • Absenteeism % = Absent man-days / Available man-days x 100

3. Audit and compliance: are the controls actually in place?

Six compliance percentages share one structure: what was found compliant, divided by what was checked, multiplied by 100. They show whether your management system is working in practice, not just on paper.

MetricFormulaWhat it tells you
Audit compliance %Compliant points ÷ applicable points × 100Overall conformity with the audit protocol or standard
PPE compliance %Compliant workers ÷ workers checked × 100Whether PPE rules are followed in the field
Permit to work (PTW) compliance %Compliant permits ÷ permits audited × 100Quality and discipline of high-risk work control
CAPA closure %Closed actions ÷ total actions × 100Whether corrective and preventive actions are actually completed
Training compliance %Trained employees ÷ applicable employees × 100Coverage of mandatory and role-specific training
Inspection compliance %Completed inspections ÷ planned inspections × 100Whether the inspection programme is being delivered

Three habits make these figures more trustworthy:

  • Define “applicable”. Exclude items that genuinely do not apply, and record why.
  • Report sample size. A PPE result based on 8 workers is not the same as one based on 80.
  • Track overdue actions separately. A high CAPA closure rate can hide a handful of serious actions that have been open for months.

4. Risk management: scoring and comparing risk

Risk calculations let you rank hazards, justify the controls you choose and show that those controls made a measurable difference.

Risk score multiplies the likelihood of harm by its severity, usually on a 5 × 5 matrix. It lets you prioritise: a score of 20 needs attention before a score of 6.

  • Risk score = Likelihood x Severity

Residual risk is the risk that remains after controls are in place. It is scored the same way, using the likelihood and severity you expect with the controls working. If residual risk is still high, you need further controls, or you need to stop the activity.

Risk reduction % shows how much the controls achieved compared with the starting position. It is useful evidence in risk assessments, management reviews and client reports.

  • Risk reduction % = Initial risk – Residual risk /Initial risk x 100

Worked example. A manual handling task is scored at likelihood 4 and severity 4, giving an initial risk of 16. After introducing a mechanical aid and training, likelihood falls to 2 while severity stays at 4, so residual risk is 8. Risk reduction is (16 − 8) ÷ 16 × 100 = 50%.

Remember that a risk score is a judgement made visible, not a measurement. Use the same scoring criteria every time, and have more than one competent person agree the scores for significant risks.

5. Emergency and fire safety: how ready are you?

Three measures test whether your emergency arrangements work when it matters. They are most useful when taken from real drills and real events, not estimated.

Emergency response time is the gap between notification of an emergency and the start of an effective response. Shorter is better, and trends across drills show whether response is improving.

  • Response time = T effective response – T notification

Evacuation time is how long it takes for everyone to reach the assembly point after the alarm sounds. Compare it with the target in your fire risk assessment and emergency plan, and look at what slowed people down: blocked routes, unclear signage, people with mobility needs, visitors or contractors who are unfamiliar with the site.

  • Evacuation time = T assembly complete – T alarm

Fire extinguisher coverage compares the extinguishers you need with those you actually have in place and in working order.

  • Extinguisher coverage % = Available and compliant extinguishers / Required extinguishers x 100


The number required should come from your fire risk assessment, using recognised guidance on selecting and siting portable extinguishers. Anything below 100% is a gap to close, and “compliant” should include being in the right place, correctly signed, and in date for servicing.

6. Safety observations and behaviour: what the front line is telling you

Observation programmes generate a lot of data. Four simple percentages turn it into something you can act on.

MetricFormulaWhat it tells you
Observation closure %Closed observations ÷ total observations × 100Whether issues raised are being fixed, which drives trust in the programme
Unsafe act %Unsafe acts ÷ total observations × 100How often people are seen working in an unsafe way
Unsafe condition %Unsafe conditions ÷ total observations × 100How often the workplace itself is found to be unsafe
Repeat observation %Repeat observations ÷ total observations × 100Whether the same problems keep coming back

Read them together rather than in isolation:

  • A high unsafe act % with a low unsafe condition % points towards supervision, training, workload or culture.
  • A high unsafe condition % points towards maintenance, housekeeping, equipment and design.
  • A high repeat observation % is a warning that actions are closing on paper without fixing the root cause.
  • A low closure rate suggests workers will stop reporting, because nothing seems to happen.

Be careful not to treat a falling unsafe act percentage as proof of improvement. It can also mean observers are less thorough, or that people behave differently when they know they are being watched. Check the trend against near-miss reports and inspection findings.

7. Contractor safety: holding the supply chain to the same standard

Contractors often carry a large share of the risk on a site, and clients increasingly ask for contractor-specific figures. Three measures cover the basics.

Contractor incident rate applies the TRIR approach to contractor workers only, using their own recordable cases and their own hours. Keeping it separate stops good employee performance from masking contractor problems, or the reverse.

  • Contractor incident rate = Contractor recordable cases x 200,000 / Contractor hours worked

Contractor compliance % shows how many of your site requirements contractors are meeting, such as method statements, competence evidence, permits, insurance and inspection of work equipment.

  • Contractor compliance % = Compliant contractor requirements / Applicable requirements x 100

Induction compliance % checks that everyone on site has been inducted before starting work. Anything below 100% means someone is working without knowing the site rules, emergency arrangements or hazards.

  • Induction compliance % = Inducted workers / Total mobilised workers x 100

On construction projects, the Construction (Design and Management) Regulations 2015 place duties on clients, principal designers and principal contractors that relate directly to these measures, including site inductions and checking contractor competence. Contractor figures are also a practical way to evidence that duty-holders are managing the people they bring onto site.

8. Leading and lagging indicators: look ahead as well as back

Safety performance is the combination of leading indicators, which measure the effort you put into preventing harm, and lagging indicators, which measure the harm that has already happened. Relying on lagging indicators alone is like driving by looking only in the rear-view mirror.

Leading indicators (proactive)

  • Safety inspections completed
  • Training hours delivered
  • Safety observations made
  • Toolbox talks held
  • Audits completed
  • Mock drills carried out
  • Near-miss reports submitted
  • CAPA closure

Lagging indicators (reactive)

  • Fatalities
  • Lost time injuries
  • Recordable injuries
  • Lost workdays
  • Occupational illnesses

Lagging indicators matter because they are the outcomes you are ultimately trying to prevent, and many are legally reportable. Their weakness is that they are often too few to be statistically meaningful, especially in a small or medium-sized business. A year with zero injuries may reflect good control or simply good luck.

Leading indicators fill that gap by showing, month by month, whether the activities that prevent harm are actually happening. Most of the percentages in sections 3, 6 and 7 are leading indicators. A good dashboard pairs each lagging result with the leading measures most likely to influence it.

9. Additional formulas: recordable rates and environmental performance

Four environmental measures that matter for sustainability reporting and ISO 14001-style environmental management can also be considered.

Total Recordable Incident Rate (TRIR), expanded. This is defined as fatalities plus lost time injuries plus restricted work cases. Be aware that the full OSHA definition of a recordable case also includes medical treatment beyond first aid, so confirm which cases your client counts.

  • TRIR = (Fatalities + LTIs + Restricted work cases) x 200,000 / Hours worked

Days Away, Restricted or Transferred (DART). This adds up cases where someone was away from work, on restricted duties or moved to a different job. Count cases, not days.

  • DART = (Days-away + Restricted + Transferred cases) x 200,000 / Hours worked

Environmental incident rate tracks spills, uncontrolled releases, permit breaches and similar events against hours worked, so you can see whether environmental control is improving as the workload changes.

  • Environmental incident rate = Environmental incidents x 200,000 / Hours worked

The last three are intensity measures. They divide resource use by output, which shows efficiency rather than just total consumption. If production doubles and energy use rises by 50%, intensity has improved even though the total went up.

MetricFormulaExample unit
Energy consumption rateEnergy used ÷ outputkWh per unit produced
Water consumption rateWater used ÷ outputm³ per unit produced
Waste generation rateWaste generated ÷ outputkg per unit produced

Choose an output measure that suits your business, such as units produced, tonnes processed, turnover, or hours of service delivered, and keep it the same from year to year so trends are meaningful.

10. The HSE mindset: from numbers to decisions

The formulas only matter if they feed a cycle of improvement which has six steps:

  1. Identify hazards and risks.
  2. Assess and prioritise them.
  3. Control them by putting safeguards in place.
  4. Measure performance with the formulas in this guide.
  5. Analyse gaps and trends.
  6. Improve controls and build a stronger safety culture, then go round again.

Five practical points keep the numbers honest:

  • Fix your definitions. Write down what counts as an LTI, a recordable case, a near miss and an incident, and apply it consistently.
  • State your basis. Say whether a rate is per 200,000 or 1,000,000 hours, and which period it covers.
  • Protect data quality. Late reporting, missing hours and inconsistent classification distort every rate.
  • Use numbers to decide, not just to report. Each metric should prompt a question about what to do next.
  • Combine data with walking the site. Numbers show where to look, and conversations with the workforce explain why.

Turning the numbers into better safety

Good safety measurement is consistent, clearly defined and tied to action. Start with the few metrics that match your risks, such as hours worked, a recordable injury rate, near-miss reporting, action closure and training compliance, and build from there.

If you require help identifying legislation applicable to your workplace, please contact one of our team.

Health, Safety and Environmental Incidents: Types and How to Respond

How a business responds in the first hour after an incident often decides whether it becomes a minor setback or a prosecution, a prohibition notice or a pollution clean-up bill. A clear, rehearsed response protects people and the environment first, and protects your legal position second.

An incident is any unplanned event that causes, or could have caused, harm to people, property or the environment. That covers far more than injuries. Near misses, spills, equipment failures and uncontrolled releases all count, and each is a warning that your controls did not work as intended.

This guide explains the main types of health, safety and environmental incidents, what to do when each one happens, who you may have to tell, and how to stop it happening again.

Types of health and safety incidents

Most workplace incidents fall into one of five groups. Knowing which one you are dealing with tells you what to do and what you may have to report.

Accidents and injuries

An accident is an unplanned event that results in injury or damage. Examples include slips, trips and falls, manual handling injuries, contact with moving machinery, falls from height and being struck by a vehicle. Some are reportable by law; all should be recorded.

Near misses

A near miss is an event that did not cause injury or damage but easily could have, such as a pallet that falls beside a worker or a forklift that stops a metre short of a pedestrian. Near misses are the cheapest lessons a business ever gets. For every serious injury there are many near misses, so a strong near miss reporting culture is one of the best early warning systems you can build.

A practical guide to accidents, near misses, spills and waste water escapes, and what your business must do next.

Dangerous occurrences

Some events are serious enough to be reportable even when nobody is hurt. Under RIDDOR in Great Britain these include the collapse of a lift or scaffold, an explosion or fire that stops work for more than 24 hours, and the accidental release of a substance that could cause serious injury. Equivalent rules apply in Northern Ireland, the Isle of Man and the Republic of Ireland.

Work-related ill health

Not every harm happens in a single moment. Occupational asthma, dermatitis, hand-arm vibration syndrome, noise-induced hearing loss and work-related stress develop over time. Spotting these early depends on health surveillance, good records and taking employee concerns seriously.

Fires, explosions and property damage

Fires, electrical failures, structural damage and equipment breakdowns can all threaten life even when no one is hurt. They also lead to business interruption and insurance claims, so they belong in your incident log alongside injuries.

Types of environmental incidents

An environmental incident is any event that causes, or could cause, harm to land, air or water, or that breaches a permit, licence or consent condition. The most common types are below.

Waste water and effluent escapes

A waste water escape happens when process water, wash-down water, sewage or contaminated surface water leaves the place it is meant to be contained. Typical causes are blocked or overflowing drains, failed interceptors, bunds that leak, tanks that overfill and pumps that fail. Even a small escape can reach a surface water drain and flow straight into a watercourse, so speed matters.

Chemical, oil and fuel spills

Spills during delivery, storage, transfer or use of oils, fuels and chemicals are among the most frequent incidents. Damaged containers, poor housekeeping and inadequate secondary containment are the usual causes.

Air emissions and odour

Uncontrolled releases of dust, fumes, smoke or gases, and persistent odour that leads to neighbour complaints, can breach permit conditions and trigger regulator action.

Waste and permit breaches

Incorrect waste storage, missing duty of care paperwork, fly-tipping and exceeding the limits in an environmental permit or trade effluent consent are all environmental incidents, even if nothing has yet been released.

Fire water and firefighting run-off

Water used to fight a fire can carry contaminants into drains and watercourses. Planning for its containment is often missed until it is needed.

How to respond: the first hour and first 24 hours

People come first, containment second, paperwork third. The steps below work for most incidents, and your own procedure should set out who does each one.

In the first hour

  1. Make the scene safe. Stop the work, isolate energy sources, and keep people away from the hazard. Do not put rescuers at risk.
  2. Get help for anyone hurt. Provide first aid and call the emergency services where needed.
  3. Contain the release. For a spill or waste water escape, stop the source if it is safe to do so, then block drains, deploy spill kits, bunds or booms, and prevent the material reaching surface water or sewers.
  4. Raise the alarm internally. Tell your manager, the competent person and anyone named in your emergency plan.
  5. Preserve the evidence. Leave equipment and the scene as they are where safe, take photographs, and note names of witnesses before memories fade.

In the first 24 hours

  1. Decide what must be reported and to whom (see the next section). Some duties apply immediately.
  2. Record the facts. Log time, location, people involved, substances, volumes and weather, and what was done to control the event.
  3. Notify your insurer if the policy requires it, and inform affected neighbours, clients or contractors where relevant.
  4. Start the investigation while evidence is fresh.
  5. Look after people. Support injured staff and witnesses, and keep communication honest and factual.

A written incident response plan, tested through drills, makes all of this faster. Staff who know where the spill kits are and who to call will act in minutes rather than hours.

Who you may have to tell

Reporting duties depend on where you operate and what happened. The table shows the main bodies; your permit, licence or consent will list any extra notification conditions.

JurisdictionHealth and safety reports go toEnvironmental incidents go to
EnglandHSE (RIDDOR)Environment Agency
ScotlandHSE (RIDDOR)SEPA
WalesHSE (RIDDOR)Natural Resources Wales
Northern IrelandHSENINIEA
Isle of ManHealth and Safety at Work InspectorateDepartment of Environment, Food and Agriculture
Republic of IrelandHealth and Safety Authority (IR1 form)EPA and local authorities

Health and safety reporting

In Great Britain, RIDDOR requires the responsible person to report the following:

  • Work-related deaths and specified injuries, without delay
  • Injuries that leave a worker unable to do their normal work for more than seven days, within 15 days
  • Injuries to members of the public that need hospital treatment
  • Dangerous occurrences, certain occupational diseases and some gas incidents

In the Republic of Ireland, employers report fatal accidents immediately and notify the HSA using form IR1 when an employee is absent for more than three days.

Environmental reporting

If a pollution incident has happened or is likely, tell your environmental regulator as soon as you become aware of it. In Great Britain the Environment Agency, SEPA and NIEA operate a 24-hour incident hotline on 0800 80 70 60. If waste water has reached a public sewer, contact your water company or sewerage undertaker as well, and if it threatens a drinking water source, make that clear immediately.

Causing or knowingly permitting a polluting discharge is an offence under environmental legislation across the UK and Ireland, and penalties can include unlimited fines and clean-up costs. Prompt, honest reporting and visible action to limit harm are widely recognised as mitigating factors when regulators decide how to respond.

Investigating the incident and finding the root cause

The aim of an investigation is to understand why the incident happened, not to find someone to blame. Blame-focused investigations make staff hide problems, which makes the next incident more likely.

A good investigation follows a simple sequence:

  1. Gather evidence. Interview witnesses separately, review photographs, CCTV, permits, risk assessments, maintenance records and training records.
  2. Build a timeline. Establish what happened in what order, including what was normal and what changed that day.
  3. Identify the immediate causes. These are the direct triggers, such as a failed valve, a blocked drain or a missing guard.
  4. Find the root causes. Ask why repeatedly until you reach the management system gap behind the failure, for example no inspection routine, inadequate training, unclear responsibilities or production pressure. The “5 Whys” technique and fault tree analysis are both useful here.
  5. Agree corrective actions. Give each action an owner, a deadline and a way to check that it worked. Prefer fixes that remove or reduce the hazard over those that rely on people remembering to act.
  6. Share the lessons. Brief the people affected, update risk assessments, method statements and emergency plans, and record what changed.

For serious incidents, consider asking an independent competent person to lead or review the investigation. It adds credibility and often surfaces issues that insiders miss.

Preventing repeat incidents

The businesses with the fewest serious incidents are rarely the ones with the thickest manuals. They are the ones where people report problems early and see something done about them. Five habits make the biggest difference:

  • Make reporting easy and safe. Use a simple form or app, thank people for reporting, and never punish an honest near miss report.
  • Track the trends. Review incident and near miss data monthly. Repeated minor events in the same area point to a bigger failure waiting to happen.
  • Inspect environmental controls. Check drains, bunds, interceptors, tanks, pumps and spill kits on a schedule, and keep records.
  • Train and drill. Run spill response and emergency drills at least annually, and induct new starters and contractors properly.
  • Review your risk assessments. Update them after every significant incident, change of process or near miss that exposed a weakness.

For many organisations, certified management systems such as ISO 45001 for health and safety and ISO 14001 for environmental management provide a ready-made framework for all of this.

Frequently asked questions

What is the difference between an accident and an incident?

An incident is any unplanned event that caused or could have caused harm. An accident is an incident that actually resulted in injury, ill health or damage. Near misses are incidents but not accidents.

What is a near miss in health and safety?

A near miss is an unplanned event that did not cause injury, damage or pollution but had the potential to. Recording and investigating near misses lets you fix problems before someone is hurt.

Do I have to report every workplace accident?

Not every accident is reportable to the regulator, but every accident should be recorded internally. Deaths, specified injuries, injuries causing more than seven days away from normal work and dangerous occurrences must be reported under RIDDOR in Great Britain, with equivalent rules elsewhere.

What should I do if waste water escapes from my site?

Stop the source if it is safe, contain the flow by blocking drains and using spill kits or bunds, and prevent it reaching watercourses or sewers. Then notify your environmental regulator and, if it entered the sewer, your water company. Record what happened and investigate the cause.

Who investigates a serious incident?

Your own business should investigate every incident proportionately. For serious events the regulator may also investigate and can issue enforcement notices or prosecute where the law has been broken.

If you require help identifying legislation applicable to your workplace, please contact one of our team.

Download our free incident response checklist.

Health and safety and environmental regulation across jurisdictions

Introduction

The regulation of health, safety, and the environment at work has never been a purely technical matter. It sits at the intersection of political economy, legal tradition, scientific knowledge, and institutional capacity. A chemical exposure limit in a European Union directive, an inspection protocol in a United States Occupational Safety and Health Administration (OSHA) field manual, a pollution permit condition in China, and a work health and safety duty in an Australian statute all reflect distinct histories of labour struggle, environmental mobilisation, administrative state-building, and, increasingly, economic strategy. To speak of “health and safety and environmental regulation across jurisdictions” is therefore to speak of a family of regimes that share common aspirations—the prevention of harm to workers, communities, and ecosystems—but which pursue those aspirations through markedly different architectures, enforcement cultures, and legal technologies.

The past several years have been a period of unusual turbulence for these regimes. The COVID-19 pandemic exposed the fragility of occupational health and safety (OSH) systems and accelerated debates about psychosocial risks, remote work, and the boundaries of employer responsibility. The intensification of the climate crisis has pushed environmental regulation from the periphery of corporate governance toward its centre, with mandatory climate disclosure, supply chain due diligence, and carbon border measures emerging as central instruments of public policy. At the same time, a powerful counter-movement has taken shape. In the United States, federal agencies have retreated from enforcement and from climate-related rule making, devolving significant regulatory energy to states.

Health and safety and environmental regulation across jurisdictions

In the European Union, the “Omnibus” simplification package has reduced the scope of flagship sustainability directives by dramatic margins, prompting accusations of backtracking on human rights and environmental protection. The result is a global regulatory landscape characterised less by convergence toward a single model than by a complex interplay of harmonisation and divergence, ambition and retrenchment, innovation and inertia.

This article examines that landscape across the principal industrialised and industrialising jurisdictions. It begins with occupational health and safety, comparing the foundational architectures of the United States, the European Union, the United Kingdom, Australia, China, India, and selected other systems. It then turns to environmental regulation, tracing the shift from command-and-control permitting toward market mechanisms, disclosure, and supply chain governance, while noting the unevenness of that shift. Finally, it identifies the cross-cutting trends that are reshaping health, safety, and environmental regulation globally—mandatory climate disclosure, due diligence, the integration of environmental, social, and governance (ESG) considerations with traditional environmental, health, and safety (EHS) functions, digitisation and artificial intelligence, the rise of psychosocial risk, and the politics of regulatory retreat—before concluding with the implications for multinational enterprises and for the future of regulatory governance itself.

Part I: The Architecture of Occupational Health and Safety Regulation

The United States: The General Duty and the Turn Toward Voluntarism

The foundation of federal occupational safety and health law in the United States remains the Occupational Safety and Health Act of 1970, a statute born of the great wave of social regulation of the late 1960s and early 1970s. The Act created OSHA within the Department of Labour and established a dual structure of regulation: a set of specific standards promulgated under the Act, codified principally in Title 29 of the Code of Federal Regulations, and a broad “General Duty Clause” requiring employers to furnish a workplace “free from recognised hazards that are causing or are likely to cause death or serious physical harm”. The Act covers most private-sector employers and, through federally approved state plans, many public-sector workers as well.

The American model has traditionally been characterised as enforcement-oriented and compliance-based. OSHA sets permissible exposure limits (PELs) for hazardous substances, issues detailed standards for particular industries and hazards, and relies on inspections, citations, and monetary penalties to secure adherence. Penalties are adjusted annually for inflation; by 2026, serious violations carried a maximum of approximately USD 16,131, while wilful or repeat violations could attract penalties exceeding USD 161,000, with criminal referral available for wilful violations causing an employee’s death. In practice, however, the reach of federal enforcement is limited by resources: OSHA has long had fewer inspectors than would be required to inspect every covered workplace with any frequency, a constraint that has shaped the agency’s reliance on voluntary programmes and targeted national emphasis programmes (NEPs).

The most significant development in recent American OSH policy has been the explicit shift away from enforcement-based compliance toward what the agency describes as proactive risk management and prevention. In early 2026, OSHA launched its “Safety Champions Program,” a voluntary, self-guided initiative designed to help employers of any size develop workplace safety and health programmes. The agency described the programme as representing a shift in emphasis, and it followed a December 2025 issuance of seven letters of interpretation addressing confined spaces, hazard communication, and related requirements.

This approach has not gone uncontested. Critics have pointed to the simultaneous weakening of the heat illness National Emphasis Program, which had been renewed in January 2025 but was subsequently amended away from enforcement metrics toward voluntary compliance. The practical consequence is a federal regime that retains a robust statutory framework and a General Duty Clause of broad potential application, but which increasingly relies on persuasion, partnership, and employer self-assessment rather than on the deterrent effect of frequent inspection and substantial penalty.

This federal retreat has been accompanied by a pronounced state-level counter-movement. California has moved forward with its own climate disclosure regime, while Colorado and New Jersey have proposed bills requiring Scope 1, 2, and 3 emissions reporting. Several states have advanced heat-illness prevention standards that outpace federal OSHA efforts. For employers operating across the United States, the result is not a single OSH regime but a fragmented compliance environment in which the applicable standard may depend as much on the state of operation as on the federal statute. This fragmentation is a recurring feature of American regulation, but it has become particularly salient in the current period of federal deregulatory energy.

The European Union: Prevention, Participation, and the Framework Directive

The European Union’s approach to occupational health and safety rests on a different foundation. The cornerstone is Council Directive 89/391/EEC of 1989, the OSH Framework Directive, which established the principle that employers must take appropriate preventive measures to make work safer and healthier, provide information and training to workers, and consult with workers and their representatives on matters of health and safety. The Framework Directive does not seek to harmonise every detail of national law; rather, it sets minimum requirements that Member States must transpose into their own legal orders, leaving room for more protective national provisions. This “minimum harmonisation” model has allowed the EU to accommodate diverse industrial relations traditions—from the corporatism systems of Germany and the Netherlands to the more centralised systems of France and southern Europe—while maintaining a common floor of protection.

The EU regime is often characterised as preventive and engineering-oriented, in contrast to the compliance-oriented American model. The Framework Directive requires employers to carry out a risk assessment as the starting point of OSH management, to eliminate risks at source, to adapt work to the individual, and to give priority to collective protective measures over individual protective equipment. This hierarchy of controls is a distinctive feature of European OSH law, reflecting a philosophical commitment to primary prevention rather than reliance on personal protective equipment or behavioural compliance. The EU also requires the appointment of competent health and safety services, the provision of health surveillance where risks warrant it, and the meaningful participation of workers in the design and implementation of preventive measures.

The EU’s substantive standards are updated through a stream of “daughter directives” addressing particular hazards and sectors. The Carcinogens, Mutagens and Reprotoxic Substances Directive has been revised repeatedly since its first adoption in 2004 and now addresses twenty-eight cancer-causing substances. In December 2025, the Council agreed its position on a sixth revision, which would introduce new or revised occupational exposure limits for a range of substances, including isoprene, with the expectation that the revised rules would prevent around 1,700 cases of lung cancer and 19,000 other illnesses over four decades. The directive was formally adopted in October 2026, with Member States given two years to transpose it into national law. Separate directives address asbestos, lead, noise, vibration, and the use of work equipment, among other hazards. The EU has also adopted legislation on the protection of pregnant workers, young workers, and workers on fixed-term or temporary agency contracts, reflecting a broader commitment to equality and to the protection of vulnerable groups.

Enforcement in the EU is a matter for Member States, and the styles and intensities of enforcement vary considerably. Some countries, such as Denmark and the Netherlands, have experimented with risk-based inspection targeting and with reduced monitoring for employers that participate in partnership or voluntary programmes, shifting scrutiny onto non-participating employers. Others, such as Germany, have developed elaborate systems of statutory accident insurance and prevention services that integrate inspection with rehabilitation and compensation. The common thread is not a single enforcement model but a shared legal framework that makes risk assessment, worker participation, and prevention obligatory across the Union.

The United Kingdom: The Health and Safety at Work Act and the Post-Brexit Trajectory

The United Kingdom’s Health and Safety at Work etc. Act 1974 is a landmark of OSH law, and its influence has extended far beyond the UK’s borders. The Act established a general duty on employers to ensure, so far as is reasonably practicable, the health, safety, and welfare of their employees and of others affected by their undertaking. The concept of “reasonably practicable” has been central to the UK regime: it requires employers to weigh the risk against the sacrifice, whether in money, time, or trouble, involved in averting it, and it has allowed the law to adapt to changing circumstances without constant legislative amendment. The Act also created the Health and Safety Executive (HSE) as the principal regulator and established a tripartite structure, involving government, employers, and workers, in the governance of health and safety.

The UK’s departure from the European Union has set in motion a process of divergence that is still unfolding. The HSE has taken on new responsibilities for chemicals regulation through UK REACH, building safety, and dangerous goods, but it has done so with substantially reduced resources. Between 2010 and 2020, the HSE’s organisation-wide budget fell by £122 million, or 43 percent, and by 2025 it employed nearly 3,000 staff and 900 inspectors, well below the more than 4,000 staff and 1,500 inspectors it had in the 2000s. The HSE has also lost access to the European Chemicals Agency’s database, the world’s most comprehensive chemical registration system, a loss that has been compounded by its diminished capacity to respond to new hazard classifications issued in the EU. The statutory obligation on the HSE to respond to all substances given hazard classifications in the EU within a legal time frame has been removed, raising concerns about the transparency and pace of future divergence.

The divergence is not merely a matter of resources, it is also a matter of regulatory philosophy. The UK government has introduced a “growth duty” on the HSE, requiring it to have regard to economic growth in the exercise of its functions, a development that critics argue compromises the regulator’s independence and its ability to prioritise health and environmental risks over economic considerations. The government has also signalled a preference for aligning with the United Nations’ Globally Harmonised System of Classification and Labelling of Chemicals rather than with the EU’s new hazard classes, a choice that the European Commission has stated is not reciprocated on the EU side. The practical effect is a gradual, perhaps accelerating, divergence between Great Britain and the EU in the classification and regulation of chemicals, with implications for trade, for the free movement of goods, and for the level of protection afforded to workers and the public.

Northern Ireland presents a special case. Under the Windsor Framework, Northern Ireland remains aligned with many EU rules, including those on chemicals and product safety, while Great Britain diverges. This creates a regulatory border within the United Kingdom, adding complexity for businesses that operate across the Irish Sea and raising questions about the long-term coherence of the UK’s internal market in regulated products.

Australia: Model Laws and the Persistent Challenge of Harmonisation

Australia’s approach to work health and safety (WHS) has been shaped by a distinctive federal structure and by a long-running effort to achieve national harmonisation. In 2008, the National Review into Model Occupational Health and Safety Laws recommended a set of model WHS laws to be adopted by the Commonwealth, states, and territories. The model WHS Act and Regulations were developed through Safe Work Australia, a national policy body that brings together representatives of the Commonwealth, states, and territories, as well as worker and employer interests. The model laws are based on a general duties framework, supplemented by specific obligations for particular hazards and industries, and they incorporate a hierarchy of controls and a requirement for consultation with workers.

The harmonisation project has achieved substantial but incomplete success. The model WHS laws have been adopted by the Commonwealth, all states, and both territories except Victoria, which maintains its own Occupational Health and Safety Act. Western Australia adopted the model laws through its Work Health and Safety Act 2020, which became operative in March 2022. Yet the persistence of jurisdictional variations has been a source of ongoing concern in the country.

A 2025–2026 best practice review of the model WHS laws, conducted by Safe Work Australia, found stakeholder dissatisfaction with the increasing disharmony between state and territory laws fifteen years after the model laws were introduced. The review’s discussion paper catalogued variations in the WHS duties framework, consultation and representation requirements, right of entry, compliance and enforcement, inspector powers, legal proceedings, offences and penalties, and codes of practice. It also identified a broader challenge: some jurisdictions regulate particular industries separately or outside their WHS frameworks, leading to a patchwork of safety regulation that can be difficult for multi-state employers to navigate.

The Australian experience illustrates a more general tension in federal systems: the desire for national consistency and the reality of regional political and administrative autonomy. The model laws have raised the floor of protection in some jurisdictions and have created a common vocabulary of duties and obligations, but they have not eliminated the differences that matter to employers and workers. The review process itself is an acknowledgement that harmonisation is not a one-off legislative event but a continuing project of maintenance and adjustment.

China: The Work Safety Responsibility System and the Party-State

China’s work safety regime has undergone a profound transformation over the past two decades, driven by a series of high-profile industrial disasters and by the leadership’s determination to project an image of effective governance. The basic law is the Work Safety Law of the People’s Republic of China, originally promulgated in 2002 and most recently amended in 2021. The law establishes an “all-staff work safety responsibility system,” requiring production and business entities to establish and improve rules and regulations, increase investment in work safety, provide education and training to workers, and provide protective equipment that meets national or industry standards. A distinctive feature of the Chinese approach is the “dual prevention mechanism” of graded safety risk management and control and hidden danger identification and rectification, which requires enterprises to identify and classify risks and to rectify hazards on a systematic basis.

The scope of Chinese work safety regulation has been expanding. In December 2025, the Standing Committee of the National People’s Congress promulgated the Hazardous Chemicals Safety Law, which came into effect on 1 May 2026 and imposes a comprehensive responsibility system on entities engaged in the production, storage, use, operation, or transportation of hazardous chemicals. The law requires such entities to meet prescribed safety conditions and to implement an all-employee responsibility system. This builds on a pre-existing architecture of registration, licensing, and safe-use permits for hazardous chemicals, which had been developed through a series of administrative measures issued by the State Administration of Work Safety.

Enforcement in China is intimately connected to the broader apparatus of Party-state governance. Work safety performance is integrated into the evaluation of local officials, and serious accidents can trigger administrative accountability, including the dismissal or prosecution of responsible officials. The use of social credit systems is also extending into the environmental and safety domains, with environmental credit ratings, differentiated regulatory treatment, and credit repair mechanisms being deployed to incentivise compliance. The Chinese model is thus not simply a system of rules and inspections; it is a system of political and administrative incentives in which work safety and environmental performance are treated as indicators of governmental competence and legitimacy.

India: Consolidation, Codes, and the Challenge of Implementation

India’s OSH landscape is in the midst of a significant transition. For decades, the principal statute was the Factories Act of 1948, supplemented by a maze of state-level rules and sector-specific legislation. The Factories Act prescribed measures relating to working conditions, hazard prevention, safety of machinery, ventilation, waste disposal, and the protection of workers, and it led to the creation of rules for hazardous waste handling, biomedical waste management, and chemical safety. Over time, however, the Act came to be seen as outdated and fragmented, and its coverage was limited to manufacturing establishments above a certain size threshold.

The Occupational Safety, Health and Working Conditions (OSH) Code, 2020, represents an attempt to consolidate and modernise this framework. The Code was brought into force on 21 November 2025, and it extends certain obligations under the Factories Act to establishments employing at least ten workers, including information technology and other service-sector establishments. It introduces new duties on employers, including ensuring that the workplace is free from hazards likely to cause injury or occupational disease, complying with OSH standards, providing free annual health examinations for specified classes of employees, ensuring safe disposal of hazardous and toxic waste including e-waste, and issuing letters of appointment to every employee. Employees gain the right to obtain information from the employer relating to their health and safety at work and to make representations about inadequate protection, with escalation to an Inspector-cum-Facilitator. Penalties for non-compliance have been increased, with a maximum fine of INR 500,000 for certain contraventions.

The implementation of the OSH Code has been uneven across India’s states and union territories. By late 2025, eighteen to twenty-five states had already incorporated many provisions of the labour codes into their own rules, and Gujarat had formalised the OSH Code in June 2025, awaiting the central government’s final nod to initiate implementation. Karnataka had enforced the Factories (Safety Audit) Rules, 2024, and other states such as Kerala and Andhra Pradesh had taken steps toward implementation. Bihar repealed its Shops and Establishments Act in light of the overlapping provisions in the OSH Code, a sign of the consolidating logic of the new framework. Yet significant gaps remain: several states, including West Bengal, Meghalaya, Nagaland, and Sikkim, had not completed harmonisation, and enforcement capacity at the state level remained a persistent concern. The Indian experience illustrates a broader challenge facing many emerging economies: the gap between legislative ambition and administrative reality, between the enactment of modern standards and the creation of the inspectorates, training systems, and technical expertise needed to give them effect.

Other Jurisdictions: Japan, Brazil, and South Africa

A comparative account of OSH regulation would be incomplete without attention to jurisdictions that have developed distinctive approaches outside the Anglo-American and European traditions. Japan’s Industrial Safety and Health Act, originally enacted in 1972, was amended in 2025 to address the needs of a diverse and ageing workforce. The amendments, which take effect in stages from 2025 through 2026, promote safety and health measures for solo self-employed workers, strengthen mental health measures in the workplace, improve the prevention of health disorders caused by chemical substances, and promote measures to prevent occupational accidents among older workers. The Japanese approach is notable for its integration of mental health into the statutory OSH framework and for its recognition that the boundaries of the employer’s responsibility are shifting as the nature of work changes.

Brazil’s regulatory framework for OSH is centred on the Consolidation of Labour Laws (CLT) and on a extensive body of regulatory standards (Normas Regulamentadoras) issued by the Ministry of Labour and Employment. These standards address everything from the use of personal protective equipment to the prevention of accidents in confined spaces, and they are enforced through a system of labour inspectors and prosecutors. Brazil’s environmental licensing system, by contrast, has been the subject of intense controversy. In 2025, the Chamber of Deputies and the Senate approved a General Environmental Licensing Bill that United Nations human rights experts warned would introduce “significant regressions” to Brazil’s environmental licensing system and threaten the rights to life, health, and a clean environment. President Lula da Silva subsequently vetoed sixty-three articles of the bill, a decision welcomed by the UN experts, but the episode illustrates the political disagreement of environmental regulation in a country with immense natural resources and powerful agricultural and industrial interests.

South Africa’s OSH regime is based on the Occupational Health and Safety Act of 1993, which imposes a general duty on employers to provide a safe and healthy working environment. The Act is supplemented by regulations on hazardous substances, noise, vibration, and other specific hazards. Environmental regulation is governed principally by the National Environmental Management Act of 1998 (NEMA), which imposes a general duty of care to prevent pollution and ecological degradation and requires environmental authorisation for listed activities. The two regimes overlap in important respects: both address the management of the environment to prevent hazards or risks to human health, and the mining sector, in particular, is subject to both OSH and environmental legislation.

In 2025, South Africa amended its OSH regulations to consolidate obligations previously contained in the Environmental Regulations for Workplaces, and it introduced new provisions on space, safety, and first-aid duties tied to explicit criminal penalties for non-compliance. The South African experience highlights the importance of regulatory integration: OSH and environmental regulation are not separate domains but overlapping systems of risk governance that must be coordinated if they are to be effective.

Part II: Environmental Regulation — From Permits to Markets to Disclosure

The United States: Deregulation, Federalism, and the Retreat from Climate Disclosure

The United States environmental regulatory system is built on a series of foundational statutes enacted in the 1970s: the Clean Air Act, the Clean Water Act, the Resource Conservation and Recovery Act, the Toxic Substances Control Act, and the Comprehensive Environmental Response, Compensation, and Liability Act (Superfund), among others. These statutes established a system of federal standard-setting, permitting, and enforcement, administered principally by the Environmental Protection Agency (EPA) and by state environmental agencies operating under federal delegation. The American model has traditionally been characterised by a combination of technology-based standards, health-based standards, and market-based mechanisms such as the acid rain trading programme established under the 1990 Clean Air Act Amendments.

The current period, however, has been marked by a pronounced deregulatory turn at the federal level. In March 2025, the EPA announced what it described as the “biggest deregulatory action in US history,” with potential implications for greenhouse gas reporting, particulate standards, and air toxics rules. The agency proposed to repeal Greenhouse Gas Reporting Program obligations for forty-six of forty-seven source categories and to suspend the remaining subpart. Separately, the Securities and Exchange Commission (SEC) proposed to rescind the climate-disclosure rules adopted in 2024 but never brought into effect, with the SEC Chair characterising the rules as a “serious overreach” of the agency’s authority. The EPA under Administrator Lee Zeldin has focused on weakening or eliminating regulations perceived as climate-friendly. The combined effect is a federal environmental policy that is retreating from climate-related regulation and from the expansion of disclosure obligations, even as the scientific case for action strengthens.

As with OSH, the retreat at the federal level has been accompanied by state-level activism. California’s climate disclosure regime, comprising Senate Bill 253 (Scope 1, 2, and 3 emissions reporting for entities with revenue over USD 1 billion) and Senate Bill 261 (climate-related financial risk disclosure for entities with revenue over USD 500 million), is now in force, with Scope 1 and 2 disclosures required in 2026. Colorado and New Jersey have proposed similar Scope 1, 2, and 3 reporting requirements, and several states are advancing heat-illness prevention standards that exceed federal requirements. The result is a fragmented environmental regulatory landscape in which the stringency of regulation depends heavily on the jurisdiction, and in which multinational firms must navigate a patchwork of federal, state, and local requirements.

The American experience thus illustrates a broader theme: in federal systems, the retreat of the central state does not necessarily mean the retreat of regulation altogether; it may instead mean its relocation to sub national jurisdictions with different political priorities.

The European Union: The Green Deal, the Omnibus, and the Politics of Simplification

The European Union has positioned itself as the global leader in environmental regulation through its European Green Deal, a comprehensive strategy adopted in 2019 with the goal of making Europe the first climate-neutral continent by 2050. The Green Deal has generated an extensive legislative programme, including the Corporate Sustainability Reporting Directive (CSRD), the Corporate Sustainability Due Diligence Directive (CSDDD), the EU Taxonomy Regulation, the Carbon Border Adjustment Mechanism (CBAM), the Industrial Emissions Directive (IED), the Batteries Regulation, the Deforestation Regulation (EUDR), and the Forced Labour Regulation. Together, these instruments represent an ambitious attempt to harness corporate governance, financial markets, and international trade in the service of environmental and social objectives.

The CSRD requires companies listed on an EU regulated market, as well as other large companies meeting specified thresholds, to report on sustainability matters in accordance with European Sustainability Reporting Standards (ESRS). The reporting obligations cover environmental matters, social matters and treatment of employees, respect for human rights, anti-corruption and bribery, and diversity on company boards, and they include a requirement to report Scope 1, 2, and 3 greenhouse gas emissions. The CSDDD goes further, requiring in-scope companies to conduct human rights and environmental due diligence across their value chains, identifying, preventing, mitigating, and accounting for adverse impacts. The EU Taxonomy provides a classification system for environmentally sustainable economic activities, intended to guide investment and to prevent green washing. The CBAM, which entered its transitional phase in 2023, imposes a carbon price on imports of certain carbon-intensive goods, aiming to prevent carbon leakage and to encourage decarbonisation in third countries. The Deforestation Regulation requires operators and traders to prove that relevant commodities and products placed on the EU market are deforestation-free and legally produced.

This ambitious programme, however, has encountered significant political resistance. In 2025, the European Commission presented its “Omnibus” simplification package, ostensibly to reduce administrative burdens on companies and to improve the coherence of the regulatory framework. The effect of the package, as approved by the European Parliament and Council, has been dramatic. The scope of the CSRD has been reduced by nearly 90 percent, and the scope of the CSDDD by 70 percent, leaving only a small fraction of the companies originally intended to be covered. The Omnibus agreement also deleted the requirement for companies to adopt climate transition plans under the CSDDD and reduced the depth of value chain assessment required, shifting from a comprehensive assessment of all suppliers to a focus on key risks and a more targeted approach to information requests from smaller partners. The EU Deforestation Regulation was delayed by one year, with large and medium-sized companies required to comply by 30 December 2025. The “Stop-the-Clock” Directive delayed reporting obligations by two years for wave 2 and wave 3 companies under the CSRD.

The Omnibus has been fiercely contested. Green and civil society groups, as well as some businesses, have argued that the backtracking puts environmental and human health at risk and undermines the EU’s credibility as a global leader. The European Economic and Social Committee has stressed that simplification measures should not bring about any direct or indirect impacts on the health and safety of workers, and it has called for greater harmonisation of reporting methodologies and interoperability of digital systems. The Omnibus thus encapsulates a central tension in contemporary environmental regulation: the tension between the ambition to regulate for long-term sustainability and the political pressure to reduce short-term compliance costs, particularly in a context of economic stagnation, geopolitical competition, and rising energy prices.

The United Kingdom: Divergence, Chemicals, and the Capacity Gap

The UK’s post-Brexit environmental regulatory trajectory has been shaped by two competing imperatives. On the one hand, the government has sought to demonstrate a commitment to environmental protection, legislating for net zero by 2050 and establishing the Office for Environmental Protection as a watchdog. On the other hand, it has pursued a deregulatory agenda in the name of growth and competitiveness, and it has struggled to replicate the institutional capacity that the UK previously derived from its membership of the EU.

The chemicals sector is the clearest illustration of the divergence. As noted above, the HSE, which serves as the regulator for UK REACH, has lost access to the European Chemicals Agency’s database and has seen its resources decline substantially. The UK government has reduced the fees that industry pays to the HSE for registering substances and applying for authorisations, a move that may ease costs for business but that also reduces the regulator’s revenue at a time when its capacity is already stretched. The statutory link with the EU has been removed, meaning that the HSE is no longer obliged to respond to all new EU hazard classifications within a legal time frame, and it will not need to explain any exclusions from the UK’s mandatory classification and labelling list. Divergence between the UK and the EU in mandatory hazard classifications has so far been minimal, but the institutional framework is now in place for divergence to accelerate, and the loss of data access and regulatory capacity raises questions about the UK’s ability to maintain standards independently.

The divergence extends beyond chemicals. The UK’s approach to environmental permitting, waste regulation, and air quality has evolved in ways that reflect domestic political priorities rather than EU obligations, and the absence of the EU’s infringement procedures and Court of Justice oversight means that the enforcement of environmental law depends more heavily on domestic judicial review and on the Office for Environmental Protection. The UK’s experience illustrates a broader point about the relationship between regulatory autonomy and regulatory capacity: the ability to diverge is not the same as the capacity to regulate well, and the loss of shared institutions and data infrastructure can impose substantial costs on both regulators and regulated entities.

Australia: EPBC Reform and the Quest for National Environmental Standards

Australia’s principal environmental statute is the Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act), which establishes a federal approval process for actions that are likely to have a significant impact on matters of national environmental significance, such as World Heritage properties, Ramsar wetlands, threatened species and ecological communities, and migratory species. The EPBC Act has long been criticised for its complexity, delays, and lack of a coherent national standards framework, and a series of reviews—including a major independent review in 2020—recommended fundamental reform.

In 2025, the federal parliament passed a suite of EPBC Act reforms that represent the most significant overhaul of Australian environmental law in more than two decades. The key elements include the introduction of legally enforceable National Environmental Standards to guide decision-making and provide a consistent framework for assessing projects; the establishment of an independent National Environmental Protection Agency (NEPA) on 1 July 2026, responsible for compliance, enforcement, and oversight; reforms to Commonwealth-State bilateral agreements to ensure that accredited assessment and approval processes operate consistently with the National Environmental Standards; enhanced compliance and enforcement powers, including increased penalties for serious breaches, expanded investigative and audit powers, and new environment protection orders; the consolidation of three existing assessment pathways into a single streamlined framework, with expedited pathways for eligible projects; the introduction of bio regional plans to identify areas suitable for development and conservation; and the establishment of Environment Information Australia as an independent body responsible for collecting, managing, and reporting environmental data.

These reforms seek to reconcile two objectives that are often in tension: the desire for stronger environmental protection and the desire for faster, more certain approvals for economically significant projects. The introduction of National Environmental Standards is intended to provide a clear and consistent benchmark against which projects can be assessed, reducing the scope for ad hoc decision-making. The establishment of NEPA as an independent regulator is intended to strengthen enforcement and to depoliticise compliance. The retention of bilateral agreements with the states, however, means that the federal government will continue to rely on state-level assessment processes, and the effectiveness of the reforms will depend on the extent to which the National Environmental Standards are actually applied and enforced across jurisdictions. The Queensland Productivity Commission has been directed to conduct a public inquiry into the reforms, with a final report due by April 2027, a sign of the continuing disagreement over the balance between environmental protection and economic development.

China: Pollution Permits, Carbon Markets, and the Marketisation of Environmental Governance

China’s environmental regulatory system has evolved from a command-and-control model centred on emissions standards and administrative penalties toward a more hybrid system that incorporates market-based mechanisms, disclosure, and credit-based incentives. The Environmental Protection Law, revised in 2014 and effective from 1 January 2015, established the principle that governments at all levels must take effective measures to prevent and control pollution and public nuisances, and it introduced a system of pollution discharge permits, environmental impact assessment, and public interest litigation. The law also strengthened penalties for environmental violations, including the possibility of daily fines and the detention of responsible persons.

A distinctive feature of the Chinese approach is the use of five-year plans and central policy documents to set environmental targets and to coordinate action across ministries and levels of government. In May 2025, the Central Committee of the Communist Party and the State Council issued an opinion on improving the market-based allocation of resource and environmental factors, with the goal of establishing a basically complete carbon emissions trading system, a water rights trading system, and a pollution rights trading system by 2027. The opinion calls for more active trading markets, better price formation mechanisms, and more efficient allocation of resource and environmental factors, reflecting a strategic shift toward using market instruments to achieve environmental objectives. China’s national carbon market, which initially covered the power sector, is being expanded to include more industries, and the government is developing a system of environmental credit evaluation that will be used to differentiate regulatory treatment and to incentivise compliance.

The Chinese model is not without its tensions. The reliance on market mechanisms and credit systems coexists with a political system in which local officials are evaluated on both economic growth and environmental performance, and the balance between these objectives can shift over time. The central government’s commitment to environmental protection is articulated forcefully in policy documents, but implementation at the local level can be uneven, particularly in regions that are heavily dependent on carbon-intensive industries. Nevertheless, the direction of travel is clear: China is building a more sophisticated and diversified environmental regulatory system, one that combines traditional administrative controls with market instruments, information disclosure, and credit-based incentives.

India: Environmental Impact Assessment, Judicial Intervention, and the Struggle for Regulatory Coherence

India’s environmental regulatory framework rests on the Environment (Protection) Act of 1986, which provides the legal basis for a wide range of rules and notifications on air and water pollution, hazardous waste, biomedical waste, e-waste, plastic waste, and environmental impact assessment. The EIA Notification of 2006 requires certain categories of projects to obtain prior environmental clearance before construction, and it establishes a process of screening, scoping, public consultation, and appraisal. Projects are classified as Category A (appraised at the central level) or Category B (appraised at the state level), depending on their potential environmental impacts.

The Indian environmental regulatory system has been shaped to an unusual degree by judicial intervention. In February 2025, the Supreme Court stayed a notification that had exempted certain categories of projects from the requirements of the EIA Notification, and in May 2025, in the case of Vanashakti v Union of India, the Court struck down a 2017 notification and a 2021 standard operating procedure, holding that the EIA Notification of 2006 is intended to protect the environment and prevent pollution and that exemptions cannot be granted without adequate justification. The Court’s interventions reflect a broader pattern of judicial activism in Indian environmental law, in which the courts have often acted as a check on executive discretion and as a forum for public interest litigation. At the same time, the executive has continued to propose amendments to the EIA regime, including a 2025 draft notification to exempt Common Effluent Treatment Plants and Common Municipal Solid Waste Management Facilities from prior environmental clearance, and the Environment Audit Rules 2025, which create a cadre of certified third-party environmental auditors to undertake on-site verification and audit of projects.

The Indian experience illustrates the importance of institutional checks and balances in environmental regulation. The EIA process is not merely a technical exercise; it is a site of disagreement among developers, regulators, affected communities, and the judiciary. The Supreme Court’s willingness to strike down exemptions has reinforced the legal standing of environmental protection, but it has also highlighted the fragility of regulatory standards when they depend on executive discretion. The challenge for India is to build a system of environmental governance that is both efficient and accountable, and that can withstand the pressures of rapid industrialisation and urbanisation.

Brazil and South Africa: Licensing, Rights, and the Politics of Environmental Protection

Brazil’s environmental licensing system has been one of the most contested areas of environmental policy in Latin America. The country’s licensing regime, which originated in the 1980s and was consolidated by the National Environmental Policy Act of 1981 and subsequent regulations, requires environmental impact assessment and licensing for projects with significant environmental impacts. The system has been criticised by industry for being slow and unpredictable, and by environmentalists for being insufficiently protective. In 2025, the Brazilian Congress approved a General Environmental Licensing Bill that UN human rights experts warned would introduce significant regressions, including the expansion of exemptions and self-licensing, and would threaten the rights to life, health, an adequate standard of living, and a clean environment. President Lula da Silva vetoed sixty-three articles of the bill, a decision that the UN experts welcomed, but the episode demonstrates the intense political disagreement surrounding environmental regulation in a country with a large agricultural sector, extensive mineral resources, and a globally significant portion of the Amazon rain forest. Brazil’s Supreme Court has also been involved in adjudicating the constitutionality of the licensing law, and the outcome of that litigation will shape the future of environmental governance in the country.

South Africa’s environmental regulatory framework is anchored in NEMA, which establishes a general duty of care and a set of principles for environmental management, including sustainable development, the precautionary principle, and the polluter-pays principle. NEMA requires environmental authorisation for listed activities and provides for a range of compliance and enforcement mechanisms. The OSH Act and NEMA overlap in their concern for human health and environmental protection, and the mining sector is subject to a separate regime under the Mineral and Petroleum Resources Development Act. In 2025, South Africa amended its OSH regulations to consolidate environmental health obligations and to introduce new provisions on space, safety, and first aid, with explicit criminal penalties for non-compliance. The South African experience underscores the importance of regulatory integration across OSH and environmental domains, and it illustrates the challenges that developing economies face in building enforcement capacity and in balancing environmental protection with economic development.

Part III: The Convergence Agenda — Global Trends Reshaping HSE Regulation

Mandatory Climate Disclosure: From Voluntary Frameworks to Binding Law

One of the most significant trends in environmental regulation over the past decade has been the shift from voluntary climate disclosure to mandatory reporting. The Task Force on Climate-related Financial Disclosures (TCFD), established by the Financial Stability Board in 2015, provided a widely adopted framework for disclosing climate-related risks and opportunities, organised around governance, strategy, risk management, and metrics and targets. The International Sustainability Standards Board (ISSB), created in 2021, has built on the TCFD framework to develop global baseline standards—MFRS S1 and MFRS S2—for sustainability and climate-related disclosure. As of June 2025, thirty-six jurisdictions had adopted or otherwise used the ISSB standards or were in the process of finalising steps toward introducing them.

The adoption of mandatory climate disclosure is uneven but expanding. In the EU, the CSRD requires disclosure in accordance with ESRS, which are aligned with the ISSB standards. In Australia, mandatory climate-related financial disclosures commenced on 1 January 2025, with a phased approach for different categories of entities.

In New Zealand, climate-related disclosures are mandatory for certain large entities, and the government announced changes to the regime in October 2025. In Brazil, the Comissão de Valores Mobiliários (CUM) Resolution 193 requires publicly traded companies, securitisation companies, and investment funds to disclose climate-related risks following ISSB standards, with mandatory disclosure beginning on 1 January 2026.

In California, Senate Bills 253 and 261 impose Scope 1, 2, and 3 emissions reporting and climate-related financial risk disclosure on large entities doing business in the state. In China, the Ministry of Finance has issued draft Corporate Sustainability Disclosure Standards that largely follow the ISSB, with plans to finalise the standards by 2027 and to phase them in once adopted.

The United States is the notable exception to this trend at the federal level. The SEC’s climate-disclosure rule, adopted in 2024, was stayed and subsequently proposed for rescission, and the EPA has proposed to repeal its greenhouse gas reporting programme for most source categories. The American retreat from federal climate disclosure stands in contrast to the trajectory in most other major economies, and it reinforces the fragmented nature of the US regulatory landscape, where state-level regimes such as California’s continue to impose substantial disclosure obligations.

The trend toward mandatory climate disclosure has several implications. First, it increases the quantity and quality of information available to investors, regulators, and the public, potentially improving market discipline and accountability. Second, it imposes significant compliance costs on companies, particularly those with complex global supply chains, and it requires the development of new systems for data collection, verification, and assurance. Third, it creates pressure for international harmonisation, as companies seek to avoid duplicate reporting requirements across jurisdictions. The ISSB standards are intended to serve as a global baseline, but the EU’s ESRS are more extensive, and the coexistence of multiple frameworks creates the risk of fragmentation even as the broad direction of travel is toward mandatory disclosure.

Supply Chain Due Diligence: Extraterritorial Reach and the Governance of Global Value Chains

A second major trend is the rise of supply chain due diligence legislation, which requires companies to identify, prevent, and mitigate adverse human rights and environmental impacts in their value chains. The EU’s CSDDD is the most ambitious instrument of this kind, but it is part of a broader movement that includes the German Supply Chain Due Diligence Act (LkSG), the French Duty of Vigilance Law, the Dutch Supply Chain Due Diligence Law, the Norwegian Transparency Act, the Swiss Due Diligence Ordinance, and the UK Modern Slavery Act. The UK government has recently released new statutory guidance on the Modern Slavery Act that significantly raises the bar on what a good modern slavery statement looks like under section 54.

The CSDDD, as originally adopted, would have required in-scope companies to conduct due diligence across their entire value chain, to adopt climate transition plans, and to establish grievance mechanisms for affected stakeholders. The Omnibus amendments have reduced its scope and softened its requirements, but the directive nonetheless represents a significant expansion of corporate accountability. The German LkSG, which applies to companies with at least 3,000 employees (and, from 2024, 1,000 employees), requires companies to establish a risk management system, conduct regular risk analyses, adopt preventive and remedial measures, and report annually to the German federal supervisory authority. The French Duty of Vigilance Law imposes similar obligations on large French companies, and it has been used by NGOs and affected communities to bring lawsuits against companies for alleged failures to prevent human rights and environmental harms.

The extraterritorial reach of these laws is a defining feature. The EU Deforestation Regulation requires exporters to the EU to prove that their products are not linked to deforestation, regardless of where the deforestation occurred. The US Uyghur Forced Labor Prevention Act prohibits the importation of goods produced wholly or in part in the Xinjiang Uyghur Autonomous Region, and it places the burden on importers to demonstrate that their supply chains are free from forced labour. These measures extend the regulatory reach of importing jurisdictions into the production processes of exporting countries, creating a new form of trade-related environmental and social governance. For multinational enterprises, the challenge is to build due diligence systems that can operate across diverse legal, cultural, and institutional contexts, and to ensure that their supply chain governance is robust enough to withstand scrutiny from regulators, investors, civil society, and consumers.

The Integration of ESG and EHS

A third trend is the increasing integration of environmental, social, and governance (ESG) considerations with traditional environmental, health, and safety (EHS) functions. Historically, EHS has been concerned with compliance with OSH and environmental regulations, while ESG has been concerned with the broader sustainability performance of the enterprise and its relationships with investors, communities, and other stakeholders. The two domains have often been managed separately, with EHS reporting to the chief operating officer or the head of manufacturing, and ESG reporting to the chief financial officer or the head of corporate affairs.

This separation is breaking down. The ISSB’s sectoral standards, which are integrated into the MFRS system, include topics such as water management and workforce health and safety, recognising that these issues are material to investors and to long-term value creation. The CSRD’s ESRS include disclosure requirements on working conditions, health and safety, and respect for human rights, alongside environmental matters. The CSDDD requires companies to address both human rights and environmental impacts in their due diligence processes. Regulatory bodies are increasingly working to harmonise standards and improve corporate sustainability transparency, and the scope of ESG and EHS regulations continues to expand across regions and sectors.

The integration of ESG and EHS has practical implications for corporate governance. It requires the development of integrated data systems that can capture health, safety, environmental, and social performance across the value chain. It requires the alignment of risk management frameworks so that OSH and environmental risks are assessed alongside climate, human rights, and governance risks. And it requires a shift in organisational culture, from a compliance-oriented approach to OSH and environment to a more strategic approach that recognises these issues as integral to business resilience and long-term value creation.

Digitisation, Artificial Intelligence, and the Future of Regulatory Oversight

A fourth trend is the digitisation of regulatory oversight and the emergence of artificial intelligence as a regulated domain in its own right. Regulators are increasingly using digital tools for data collection, risk profiling, and enforcement targeting. The Chinese social credit system, for example, uses environmental and safety compliance data to rate enterprises and to differentiate regulatory treatment. The EU’s CSRD and the ISSB standards require digital, machine-readable reporting, which facilitates the automated analysis of corporate sustainability data. Environmental sensors, satellite monitoring, and remote sensing are being used to detect pollution and deforestation in near-real time, expanding the scope and precision of regulatory oversight.

At the same time, AI is itself becoming a subject of regulation, with significant implications for OSH and EHS. The EU Artificial Intelligence Act, which entered into force in August 2024, introduces a risk-based framework for AI systems, with prohibitions on “unacceptable risk” systems, AI literacy requirements from February 2025, full application of most provisions from August 2026, and an extended deadline for high-risk AI systems embedded in products from August 2027. Employers using AI in workplace decision-making must ensure staff AI literacy and compliance with strict governance rules for high-risk systems. In the United States, without a federal AI law, states are introducing targeted measures: Texas’s Responsible AI Governance Act prohibits discriminatory AI, and California’s Senate Bill 7 would ban reliance on AI for key employment decisions without human oversight and restrict predictive AI use. In Asia-Pacific, Japan has adopted its first AI law, establishing a national AI strategy centre and mandating cooperation with investigations and adherence to national principles, while Hong Kong has expanded its Building Energy Efficiency Ordinance to cover data centres.

The regulation of AI intersects with OSH and EHS in several ways. AI systems used in workplace monitoring, productivity management, and hiring can affect workers’ privacy, autonomy, and mental health, raising psychosocial risk concerns. AI systems used in industrial processes can enhance safety through predictive maintenance and early warning systems, but they can also introduce new risks if they are poorly designed or inadequately governed. The challenge for regulators is to develop frameworks that encourage innovation while ensuring that AI systems are safe, transparent, and accountable, and that they do not undermine the protections that OSH and environmental law are designed to provide.

Psychosocial Risks and the Right to Disconnect

A fifth trend is the growing recognition of psychosocial risks as a legitimate concern of OSH regulation. Psychosocial risks—including work-related stress, bullying, harassment, violence, and the blurring of boundaries between work and private life—have been identified as emerging risks in the EU, and the European Parliament has called on the Commission to propose a directive on psychosocial risks and well-being at work. The EU Framework Directive already covers all occupational risks, including psychological risks, but the implementation reports and the European Survey of Enterprises on New and Emerging Risks (ESENER) provide evidence that the existing framework has not been sufficient. The European Economic and Social Committee has urged the Commission to propose a directive that would establish binding obligations to identify psychosocial risks through appropriate risk assessments, with the participation of workers and trade unions.

The right to disconnect is one manifestation of this broader concern. France and Italy have introduced comprehensive legislative frameworks, while other countries, such as Romania and Japan, continue to rely primarily on working-time limits, and Canada is moving towards a mixed federal-provincial model. Australia’s new right to disconnect, effective since August 2024 for larger employers, allows employees to refuse to monitor, read, or respond to work-related communications outside working hours, subject to reasonableness considerations. At the EU level, the Commission launched a consultation in April 2024 on fair remote work and the right to disconnect.

The regulation of psychosocial risks represents a significant expansion of the OSH domain. It moves OSH beyond the traditional concern with physical hazards—chemicals, machinery, noise, and ergonomics—to encompass the organisation of work, the quality of working relationships, and the psychological contract between employer and employee. This expansion poses challenges for regulators, employers, and workers alike. It requires new forms of risk assessment that can capture the subjective experience of work, new forms of worker participation that can give voice to concerns that may be difficult to articulate, and new forms of enforcement that can address organisational failures that may not manifest in immediate physical harm. It also raises questions about the boundaries of employer responsibility, particularly in an era of remote work, digital communication, and fragmented employment relationships.

The Retreat from Regulation and the Politics of Retrenchment

A sixth trend, and one that cuts against the others, is the retreat from regulation in several major jurisdictions. In the United States, the federal government has moved decisively away from enforcement-based OSH regulation and from climate-related environmental regulation, devolving significant regulatory energy to states and to voluntary programmes. In the EU, the Omnibus package has reduced the scope of the CSRD and CSDDD by dramatic margins and has delayed the implementation of key sustainability obligations. In the UK, the HSE’s resources have declined substantially, and the government has introduced a growth duty that critics argue compromises the regulator’s independence. In Brazil, the environmental licensing reform was significantly rolled back by presidential vetoes, but the underlying political pressures for loosening environmental controls remain strong.

The retreat from regulation is driven by several factors. Economic stagnation, rising energy costs, and geopolitical competition have created pressure on governments to reduce regulatory burdens on business. The anti-ESG backlash, particularly in the United States, has politicised sustainability reporting and has made it a target for ideological opposition. The complexity and cost of compliance with overlapping reporting requirements have generated legitimate concerns about administrative burden, particularly for small and medium-sized enterprises. And the political cycle in democratic countries creates incentives for governments to prioritise short-term economic growth over long-term environmental and social objectives.

Yet the retreat is not uniform, and it is not uncontested. In the United States, state-level action on climate disclosure and heat-illness prevention has partially offset federal retreat. In the EU, the Omnibus has been criticised by civil society, trade unions, and some businesses, and the European Economic and Social Committee has insisted that simplification must not come at the expense of worker health and safety. In Australia, the EPBC reforms have strengthened environmental standards and created an independent regulator, even as they seek to streamline approvals. In China, the direction of travel remains toward stronger environmental and safety regulation, albeit through a different institutional logic than in liberal democracies. The global picture is therefore one of divergence and disagreement rather than a uniform retreat, with the balance of regulatory ambition depending on the specific jurisdiction, the political complexion of its government, and the strength of its civil society and social partners.

Conclusion: Implications for Multinational Enterprises and the Future of HSE Regulation

The comparative analysis presented in this article reveals a global regulatory landscape that is neither converging toward a single model nor fragmenting into incoherence. It is, rather, a landscape of overlapping regimes, shared principles, and persistent differences. The foundational principles of OSH regulation—the general duty of care, the hierarchy of controls, risk assessment, worker participation, and prevention—are widely shared across jurisdictions, even as they are implemented through different legal instruments and enforced through different institutional arrangements. The foundational principles of environmental regulation—pollution prevention, the polluter-pays principle, precaution, and sustainable development—are similarly widespread, even as the choice of policy instruments varies from command-and-control permitting to market-based trading to disclosure and due diligence.

For multinational enterprises, this landscape presents both challenges and opportunities. The challenges are obvious: regulatory fragmentation increases compliance costs, creates legal risk, and requires sophisticated systems for tracking and responding to developments across multiple jurisdictions. The extraterritorial reach of supply chain due diligence and deforestation regulations means that companies can no longer assume that compliance with local law is sufficient; they must also meet the standards imposed by their major markets. The retreat from regulation in some jurisdictions does not necessarily reduce compliance burdens, because state-level and sub national regulation, as well as investor and consumer expectations, may fill the gap. The rise of mandatory climate disclosure and the integration of ESG and EHS create new reporting obligations and new demands for data, assurance, and governance.

The opportunities are equally significant. Companies that invest in robust HSE management systems, that integrate OSH and environmental considerations into their core business strategy, and that build resilient supply chain due diligence processes are better positioned to manage regulatory risk, to attract investment, and to maintain their social licence to operate. The harmonisation of reporting standards through the ISSB and the development of digital, machine-readable reporting formats create opportunities for efficiency and comparability. The recognition of psychosocial risks and the right to disconnect create opportunities for employers to differentiate themselves as responsible employers in a competitive labour market. And the shift toward market-based environmental instruments, such as carbon trading and environmental credit systems, creates opportunities for companies that are able to innovate and to capture the value of environmental performance.

The future of HSE regulation will be shaped by several forces. The first is the trajectory of the climate crisis, which will continue to drive the development of disclosure requirements, carbon pricing mechanisms, and adaptation obligations. The second is the evolution of work, including remote work, platform work, and automation, which will require regulators to rethink the boundaries of the employment relationship and the scope of OSH protection. The third is the development of artificial intelligence, which will create new risks and new opportunities for regulatory oversight. The fourth is the politics of regulation itself, which will determine whether the current period of retrenchment in some jurisdictions is a temporary pause or a lasting shift in the balance between public protection and private autonomy.

What is clear is that the era of purely national regulation, in which companies could manage compliance jurisdiction by jurisdiction, is over. The most significant regulatory developments of the past decade—the CSRD, the CSDDD, the CBAM, the EUDR, the ISSB standards, and the various supply chain due diligence laws—are all extraterritorial in their reach and global in their ambition. They reflect a recognition that the most pressing health, safety, and environmental challenges are transnational in nature and cannot be addressed through national regulation alone. They also reflect a recognition that the private sector, and particularly large multinational enterprises, have the capacity and the responsibility to contribute to the solution. The challenge for the coming decade will be to build a global regulatory architecture that is coherent enough to be effective, flexible enough to accommodate legitimate jurisdictional differences, and robust enough to withstand the political and economic pressures that will inevitably arise. That is a challenge not only for regulators but for businesses, workers, civil society, and the international community as a whole.

What Businesses Need to Comply with the Workplace (Health, Safety and Welfare) Regulations?

The short answer

Almost every business that employs people, or controls premises where people work, must comply with the Workplace (Health, Safety and Welfare) Regulations 1992 (SI 1992/3004). The main exceptions are construction sites, ships and underground mineral extraction, with lighter requirements for temporary, farming and forestry sites.

The Regulations set the basics of a safe and healthy working environment: ventilation, temperature, lighting, cleanliness, space, workstations, floors, doors, windows and traffic routes, plus welfare facilities such as toilets, washing facilities, drinking water and rest areas. This guide explains who must comply, what counts as a workplace, and what each part of the Regulations asks of you.

The Regulations apply in Great Britain. Northern Ireland and the Republic of Ireland have their own equivalent rules, covered at the end of this article.

Who has to comply?

Regulation 4 puts the duty on two groups: employers, and anyone else who has control of a workplace.

  • Employers. Every employer must ensure that each workplace under their control, where any of their employees work, meets the Regulations.
  • Anyone with control, to any extent. This covers a person who controls a workplace in connection with a trade, business or other undertaking, whether or not it is run for profit. Landlords, building owners and managing agents are caught, but only for the matters within their control, such as shared toilets, stairs, lobbies and ventilation plant.
  • Tenants. A tenant employer is responsible for the workplace they control. Toilets and other facilities can be provided by a landlord or a neighbouring business, but the employer remains responsible for making sure they meet the standard.
  • Self-employed people. The “control” duty does not apply to a self-employed person in respect of their own work or the work of their partners. A sole trader who employs staff is still an employer and is covered.

If your employees work at premises you do not control, such as a client’s site, these Regulations do not place a duty on you for that site. HSE guidance says you should still take the steps needed under your general health and safety duties to make sure your people have access to toilets and washing facilities.

What counts as a workplace?

The Regulations apply to every workplace unless regulation 3 says otherwise. Under regulation 2, a workplace is any premises, or part of premises, that is not domestic premises and is made available to a person as a place of work. That includes any place within the premises the person can access while at work, and any room, lobby, corridor, staircase or other route used to reach it or where facilities are provided for it.

In practice that means:

  • “Premises” includes outdoor places, not just buildings.
  • Domestic premises are outside the Regulations. A private dwelling is not a workplace, so people working from home are not covered. Hotels, nursing homes and the kitchens of hostels or sheltered accommodation are covered.
  • Shared areas count. Common parts of shared buildings and private roads and paths on industrial estates and business parks are workplaces.
  • New work on an existing building must comply. A modification, extension or conversion must meet the relevant requirements as soon as it is in use, and regulation 4A requires any building used as a workplace to have stability and solidity appropriate to its use.

Exclusions and lighter requirements

SituationWhat applies
ShipsExcluded, except regulations 8(1) and (3) (lighting) and 12(1) and (3) (floors and traffic routes) for repair, refit and similar operations in shipyards and dock premises
Construction sites where the only activity is construction workExcluded, except regulations 18 (doors and gates) and 25A (disabled persons). Indoors, regulations 7(1A), 12, 14, 15, 16, 18, 19 and 26(1) also apply
Below ground at a mineExcluded, except regulation 20 (toilets), applied so far as reasonably practicable for “readily accessible”
QuarriesRegulation 12 applies only to floors and traffic routes inside buildings; regulation 20 as modified above
Aircraft, trains, trailers and licensed vehicles used for transportRegulations 5 to 12 and 14 to 25 do not apply. Regulation 13 applies only when stationary inside a workplace and not on a public road
Outdoor farming and forestry workplaces away from the main buildingsRegulations 5 to 19 and 23 to 25 do not apply. Regulations 20 to 22 (toilets, washing, drinking water) apply so far as reasonably practicable
Temporary work sitesRegulations 20 to 25 (welfare facilities) apply so far as reasonably practicable

If construction work is under way inside an otherwise normal workplace, HSE guidance treats it as a construction site, and so excluded, only if it is fenced off. Otherwise both these Regulations and the Construction (Design and Management) Regulations 2015 apply.

What the Regulations require

Regulations 4A to 25A set the standards. Many use words like “suitable”, “sufficient” or “reasonable”, and regulation 2(3) says these must be judged for everyone using the workplace, including disabled people.

RegTopicCore duty
4AStability and solidityA building used as a workplace must have stability and solidity appropriate to its use
5MaintenanceKeep the workplace, and equipment, devices and systems that prevent or reduce hazards, in efficient working order and good repair, with a suitable maintenance system where appropriate
6VentilationEnclosed workplaces need a sufficient supply of fresh or purified air, with a warning device if ventilation plant fails where this matters for health or safety
7TemperatureKeep indoor temperatures reasonable during working hours, insulate where necessary, avoid excessive sunlight effects, avoid harmful heating fumes and provide enough thermometers
8LightingSuitable and sufficient lighting, natural where reasonably practicable, plus emergency lighting where a lighting failure would expose people to danger
9Cleanliness and wasteKeep the workplace, furniture and fittings sufficiently clean, make surfaces cleanable and keep waste in suitable receptacles
10Room dimensions and spaceEvery workroom needs enough floor area, height and unoccupied space for health, safety and welfare
11Workstations and seatingWorkstations suitable for the person and the work, outdoor workstations protected where practicable, and a suitable seat where work can be done sitting
12Floors and traffic routesSuitable surfaces with no hazardous holes, slopes or uneven or slippery areas, effective drainage where needed, kept free of obstructions, handrails on staircases
13Falls or falling objectsTanks, pits and similar structures holding a dangerous substance must be securely covered or fenced where practicable. Work at height is covered by the Work at Height Regulations 2005
14Windows and glazed doors and wallsSafety material or protection against breakage where necessary, and marked so they are visible
15Windows, skylights and ventilatorsMust be possible to open, close and adjust safely, and not create a hazard when open
16Cleaning windowsWindows and skylights must be designed so they can be cleaned safely
17Traffic routesOrganise the workplace so people and vehicles can move safely, with suitable, sufficient routes, separation of pedestrians and vehicles and signs where necessary
18Doors and gatesSuitably constructed with safety devices, including anti-derailment, anti-fall-back and anti-trap features for sliding, upward-opening and powered doors
19Escalators and moving walkwaysMust function safely, have necessary safety devices and an easily accessible emergency stop
20Sanitary conveniencesSuitable and sufficient toilets at readily accessible places, adequately ventilated and lit, kept clean, with separate rooms for men and women unless each is a lockable single room
21Washing facilitiesSuitable and sufficient facilities near toilets and changing rooms, with hot and cold or warm running water, soap and drying means, and showers where the work or health reasons require
22Drinking waterAn adequate supply of wholesome drinking water, readily accessible, with cups unless it is a drinking jet
23Accommodation for clothingSuitable and sufficient space for clothing not worn at work and for special work clothing
24Changing facilitiesWhere special work clothing is worn and people cannot reasonably change elsewhere, provide suitable and sufficient changing facilities
25Rest and eating facilitiesSuitable and sufficient rest facilities, eating facilities where meals are regularly eaten, protection for non-smokers, seating, and rest facilities for pregnant women and nursing mothers
25ADisabled personsParts of the workplace used directly by disabled people, including doors, passageways, stairs, showers, washbasins, lavatories and workstations, must be organised to take account of them

The numbers: minimum figures in HSE’s Approved Code of Practice

The Regulations themselves rarely give figures. The Approved Code of Practice (ACOP) L24 does, and these are the benchmarks inspectors will expect you to meet or beat.

TopicACOP benchmark
Minimum workroom temperatureNormally at least 16°C. At least 13°C if the work involves rigorous physical effort
Space per personAt least 11 cubic metres, ignoring any ceiling height above 3 m
Floor area for 11 m³About 4.6 m² with a 2.4 m ceiling, or about 3.7 m² with a ceiling of 3 m or higher
Fresh air supplyShould not normally fall below 5 to 8 litres per second per occupant

The temperature and space figures are starting points, not guarantees of compliance. The ACOP says 11 m³ may be too little if furniture and equipment take up much of the room, and that 16°C may not give reasonable comfort in every setting. The 11 m³ figure does not apply to retail kiosks, attendants’ shelters, machine cabs or rooms used for meetings and lectures.

Toilets and washbasins

Where men and women both work, the ACOP’s minimum is:

People at workToiletsWashbasins
1 to 511
6 to 2522
26 to 5033
51 to 7544
76 to 10055

Add one toilet and one washbasin for every 25 people (or part of 25) above 100. Where toilets are used only by men, the ACOP gives an alternative table that includes urinals:

Men at workToiletsUrinals
1 to 1511
16 to 3021
31 to 4522
46 to 6032
61 to 7533
76 to 9043
91 to 10044

For men-only provision above 100, add one toilet per 50 men (or part of 50), with at least as many extra urinals.

If you separate groups, such as office and manual staff, calculate for each group. For dirty work that heavily soils the face, hands and forearms, the ACOP raises the washbasin figure to one per 10 people (or part of 10) up to 50 people, then one more per 20 people (or part of 20). If the public also uses your facilities, add more so workers are not kept waiting.

Special situations businesses often ask about

  • Visiting delivery drivers. HSE has said it is updating its guidance to make clear that drivers must have access to welfare facilities at the premises they visit for work, drawing on regulations 20 and 21. If you receive deliveries, check what your site offers.
  • Facilities that are not on your premises. Toilets and washing facilities do not have to be inside your own workplace, and you can use ones provided by a landlord or neighbour. They must still meet the standard and be available whenever your people are expected to be at work. Public facilities are acceptable only as a last resort.
  • Temporary and remote sites. For temporary work sites the welfare duties apply so far as reasonably practicable. For remote workplaces without running water or a nearby sewer, the ACOP expects enough water for washing and enough chemical toilets, emptied and recharged at suitable intervals.
  • Home workers. Private dwellings are not workplaces under these Regulations, so they do not cover people working from home. Your wider duties under the Health and Safety at Work etc. Act 1974 still apply.
  • Disabled workers. Facilities, workstations and routes must be suitable for disabled people who use them, and regulation 25A requires the relevant parts of the workplace to be organised with them in mind.
  • Pregnant women and nursing mothers. Regulation 25(4) requires suitable rest facilities, which the ACOP says should be conveniently placed for toilets and, where necessary, allow a person to lie down.
  • Smoking. Where smoking is permitted, non-smokers must be protected from discomfort from tobacco smoke in rest areas.

How compliance is judged

The ACOP has special legal status. Failure to follow the ACOP is not an offence in itself. But if you are prosecuted for breaching health and safety law and did not follow the relevant ACOP provisions, you must show you complied in some other way, or a court will find you at fault. Following the ACOP’s advice is enough to comply on the matters it covers.

Some duties are qualified. Several regulations apply only “so far as is reasonably practicable” or “where necessary for reasons of health or safety. Others, such as keeping workplaces sufficiently clean or providing suitable and sufficient toilets, are unqualified.

Risk assessment drives the detail. The Management of Health and Safety at Work Regulations 1999 require employers and the self-employed to assess risks. HSE expects you to review your arrangements as the workplace changes, and to consult employees in good time on health and safety matters.

Building Regulations set a baseline. The ACOP says the standards in the Building Regulations should be met when complying with the Workplace Regulations, unless a higher standard is needed to protect health, safety and welfare so far as is reasonably practicable.

Employer checking welfare facilities and workstations during a workplace inspection

Is your workplace compliant?

A practical compliance checklist

Use this as a starting point for a workplace walk-round. It is a prompt, not a substitute for a risk assessment of your own premises.

  • Confirm who controls each part of the premises (you, a landlord, a managing agent) and who is responsible for what
  • Check that no regulation 3 exclusion applies, and note any partial exclusions such as temporary sites
  • Put a maintenance system in place for ventilation, emergency lighting, powered doors, fencing, escalators and similar equipment, and keep records
  • Measure temperatures near workstations and provide thermometers, and plan for hot and cold spells
  • Check lighting, including emergency lighting, and keep windows, lights and fittings clean
  • Compare headcount against floor area and the 11 m³ per person benchmark
  • Inspect floors, stairs and handrails, and set up routines for spills, obstructions, snow and ice
  • Review pedestrian and vehicle routes, crossing points, signs and loading bays
  • Check glazing, doors and gates, and window opening and cleaning arrangements
  • Count toilets and washbasins against the ACOP tables and confirm they are clean, lit, ventilated and private
  • Provide drinking water, clothing storage, changing facilities and rest and eating areas where needed
  • Review access and facilities for disabled workers, and rest facilities for pregnant and nursing workers
  • Agree who cleans shared facilities, and consult employees on what works in practice
  • Review everything when the workplace, headcount or work activity changes

Frequently asked questions

Do the Workplace Regulations apply to small businesses and offices?

Yes. They apply to every workplace except those excluded by regulation 3, and there is no minimum size or number of employees. Shops, offices, schools, hospitals, hotels and places of entertainment are all covered.

Do they apply to people who work from home?

No. Domestic premises are outside the definition of a workplace, so homeworkers are not covered by these Regulations. Your general duties as an employer still apply.

What is the minimum temperature in a workplace?

The Regulations require a “reasonable” temperature indoors during working hours. The ACOP says it should normally be at least 16°C, or 13°C where the work involves rigorous physical effort. The Regulations do not set a fixed maximum, so the question is whether conditions are reasonable.

How many toilets must a workplace have?

The law requires “suitable and sufficient” toilets. The ACOP gives minimums, for example two toilets and two washbasins for 6 to 25 people, and five of each for 76 to 100, with one more of each for every 25 people above that.

Does the landlord or the tenant comply?

Both, for the parts they control. A tenant employer is responsible for the workplace it controls. A landlord or managing agent must make sure common parts and shared facilities within their control meet the standard.

Do the Regulations apply on construction sites?

Mostly not. Construction sites where the only activity is construction work are excluded, apart from regulations 18 and 25A, and some further regulations indoors. Welfare on construction sites is dealt with under the Construction (Design and Management) Regulations 2015.

Northern Ireland and the Republic of Ireland

The 1992 Regulations apply in England, Scotland and Wales. Northern Ireland has its own equivalent, the Workplace (Health, Safety and Welfare) Regulations (Northern Ireland) 1993, which follow a similar structure. In the Republic of Ireland, workplace requirements, including welfare facilities, sit in Part 2, Chapter 1 of the Safety, Health and Welfare at Work (General Application) Regulations 2007 (S.I. No. 299 of 2007). If you operate across several jurisdictions, check the rules for each site.

If you require help identifying legislation applicable to your workplace, please contact one of our team.

This article is general guidance, not legal advice. Check the current legislation and HSE guidance for your circumstances.

UK and EU Health and Safety Law: A Post-Brexit Comparison

Introduction

UK and EU health and safety law remain far more alike than different, but since Brexit they have started to drift apart in how rules are made, updated and enforced. Both systems share one core idea: employers must identify workplace risks and control them. They reach that idea by different legal routes, and the routes are now diverging.

For decades the two were effectively one system. Britain’s modern framework, set by the Health and Safety at Work etc. Act 1974 (HSWA), was built on the Robens Report of 1972. It was enacted in 1974, a year after the UK joined the European Economic Community, but it was a home-grown design. From 1992 onwards, much of its detailed regulation was written to implement EU directives. The famous “six pack” of 1992 regulations, and later rules on work at height, construction, asbestos and display screen equipment, all trace back to Brussels. The EU’s own foundation is the Framework Directive 89/391/EEC, which set common principles for all member states in 1989.

The UK left the EU on 31 January 2020, and the transition period ended on 31 December 2020. Since then Great Britain has been free to rewrite its rules, and Northern Ireland has followed a different path under the Windsor Framework. Meanwhile the EU has kept legislating, adding new rules on machinery, asbestos, chemicals, artificial intelligence and platform work. For a business, a consultant or a safety professional working across the Channel, the practical question is no longer “are the rules the same?” but “where do they still match, and where must I check twice?”

This article compares the two systems in five steps:

  1. The foundations: the UK’s goal-setting model and the EU’s directive model.
  2. What Brexit changed legally, including retained EU law and Northern Ireland.
  3. How regulators and enforcement differ.
  4. A topic-by-topic comparison of the main workplace regimes.
  5. Where the systems diverge, where they still align, and a closing summary.

A note on terms. UK” is used where the point applies across the whole country, and “Great Britain” (GB) or “Northern Ireland” (NI) where it does not, because health and safety is devolved in Northern Ireland and enforced by a separate regulator. “EU” means the Union-level rules, which member states must transpose into national law. Member states differ from one another, so any statement about “the EU” is necessarily a generalisation. This is general information, not legal advice, and the position was checked against public sources in October 2026.

UK and EU Health and Safety Law

Two foundations: goal-setting statute versus directive framework

The UK model rests on a single enabling statute, while the EU model rests on a treaty power and a set of directives that member states must turn into national law. That structural difference explains most of the other contrasts in this article.

The UK model: the 1974 Act

The Health and Safety at Work etc. Act 1974 is an “enabling” Act. It sets broad duties and then lets ministers make detailed regulations under it. Employers must ensure the health, safety and welfare of their employees (section 2) and of other people affected by their work (section 3). Duties also fall on the self-employed, on those who design, make or supply articles and substances (section 6), and on employees themselves (section 7).

Most of these duties are qualified by the phrase “so far as is reasonably practicable”. That wording lets a duty-holder weigh the size of a risk against the cost, time and trouble of removing it. It is the signature of the British approach: the law states the outcome and leaves the method to the duty-holder, with the burden of proving that more could not reasonably have been done resting on the defendant.

Beneath the Act sit regulations, then Approved Codes of Practice (ACOPs), then HSE guidance. An ACOP has a special legal status. A court can treat a breach of the relevant code as proof of a breach of the law unless the defendant shows it complied in some equally effective way. Guidance has no such status and is advisory.

Since 1 October 2013, section 69 of the Enterprise and Regulatory Reform Act 2013 has also removed civil liability for breach of most health and safety regulations. An injured worker must now generally prove negligence rather than rely on breach of a statutory duty alone. Criminal enforcement is untouched.

The EU model: Framework Directive and daughter directives

The EU has no single workplace safety statute. Instead, Article 153 of the Treaty on the Functioning of the European Union lets the Union adopt directives setting minimum requirements for the working environment. Member states can then go further, and many do.

The cornerstone is the Framework Directive 89/391/EEC. It requires employers to ensure the safety and health of workers in every aspect related to work. It also sets out general principles of prevention, which in outline are to avoid risks, evaluate those that cannot be avoided, combat risks at source, adapt work to the individual, and give collective protective measures priority over individual ones. Other core obligations are:

  • a documented risk assessment;
  • competent protective and preventive services;
  • information, consultation and participation of workers;
  • training; and
  • health surveillance.

More than twenty “individual” or daughter directives then deal with particular subjects such as workplaces, work equipment, manual handling, display screens, carcinogens, asbestos, noise, vibration and construction sites.

The key conceptual difference

The two models look alike in practice but differ in legal wording. The EU duty is expressed as an obligation to “ensure” safety, with only narrow exclusions available to member states for unforeseeable events and exceptional circumstances beyond the employer’s control. The British duty is qualified by reasonable practicability.

The European Commission challenged this gap in the Court of Justice. In Case C-127/05, Commission v United Kingdom (2007), the Court held that the UK had failed to transpose the Framework Directive correctly by qualifying the employer’s duty in this way. Britain never amended the 1974 Act in response, and since Brexit there is no longer any obligation to do so. The point remains the clearest example of a difference in legal design that has little to do with day-to-day outcomes but could matter in litigation.

A second difference is the status of detailed rules. In the EU, a directive binds member states, not individual businesses, until it is transposed. In Britain, regulations, codes and guidance form a layered system in which HSE can often adjust the lower layers without new primary legislation. That flexibility matters for the post-Brexit story that follows.

What Brexit changed, and what it did not

Brexit changed who can amend the rules far more than it changed the rules themselves. On 1 January 2021 almost every health and safety regulation in force on 31 December 2020 continued to apply word for word. The real shifts came later, as Great Britain began to use its new freedom, and in Northern Ireland, where a different arrangement applies.

Day one: retained EU law

The European Union (Withdrawal) Act 2018 preserved EU-derived law at the end of the transition period as “retained EU law”. It came in three forms:

Because the main workplace rules were already domestic regulations made under the 1974 Act, they were largely untouched. Chemicals were the exception. EU REACH became “UK REACH”, and EU CLP became “GB CLP”, with HSE and other agencies taking over tasks previously done in Helsinki by the European Chemicals Agency.

The “bonfire” threat and the 2023 Act

In 2022 the government introduced the Retained EU Law (Revocation and Reform) Bill. In its original form it would have revoked all EU-derived secondary legislation at the end of 2023 unless ministers saved it, with an extension available to 23 June 2026 for specified items. Safety bodies led by RoSPA warned that the Management Regulations, work at height rules and the “six pack” could be lost through an arbitrary deadline, and that better regulation is not deregulation. The 1974 Act itself was never at risk because it is domestic law.

The Act as passed in June 2023 dropped the blanket sunset. Instead it:

  • revoked a schedule of around 600 named instruments, which the government described as largely defunct and unnecessary now that the UK has left the EU;
  • ended the supremacy of EU law and renamed the remainder “assimilated law”, from 1 January 2024;
  • gave senior courts more freedom to depart from EU case law; and
  • gave ministers powers to amend assimilated law by regulations.

Those amending powers are the route to post-Brexit divergence. They have already been used. The Chemicals (Health and Safety) (Amendment, Consequential and Transitional Provision) Regulations 2026 (SI 2026/484) came into force on 21 May 2026. They abolished the duty to notify classification and labelling information to HSE and introduced a “fast-track” route under which HSE can adopt classification proposals from trusted overseas authorities, which can include the EU. They also removed the link requiring HSE to consider every opinion of the European Chemicals Agency’s risk committee. HSE says it is maintaining high standards, and the core classification criteria are unchanged. Some environmental groups and Scottish parliamentary committee members questioned the lack of detail and impact assessment.

Northern Ireland: a different regime

Northern Ireland remains inside part of the EU system. Under the Windsor Framework, more than 300 EU legal acts, mostly covering goods, continue to apply there, with the Court of Justice of the European Union as final arbiter of their meaning. The Stormont Brake lets the Northern Ireland Assembly challenge new or replacement EU rules that would significantly affect everyday life. The practical result is that product-safety law such as machinery, personal protective equipment and explosive-atmosphere equipment follows EU rules in Northern Ireland.

Workplace duties are different. Employers’ obligations in Northern Ireland come from domestic legislation, principally the Health and Safety at Work (Northern Ireland) Order 1978, enforced by the Health and Safety Executive for Northern Ireland (HSENI). So a business there lives under EU product rules but locally made workplace rules.

The trade agreement floor

The EU-UK Trade and Cooperation Agreement also matters. Its level playing field provisions include a commitment not to weaken labour and social protections in ways that affect trade or investment, which covers occupational health and safety standards. This is a non-regression promise, not a duty to follow EU changes. It limits how far the UK could cut standards, and it is backed by the agreement’s own consultation and rebalancing mechanisms rather than its main dispute-settlement route. It does not require Britain to copy new EU rules.

Regulators and enforcement

Britain enforces through one national regulator and a heavy criminal-penalty culture, while the EU leaves enforcement entirely to its 27 member states and coordinates them from the centre. This is one of the most visible practical differences between the two systems.

Great Britain and Northern Ireland

The Health and Safety Executive (HSE), created under the 1974 Act, is the national regulator for Great Britain. It shares enforcement with local authorities, which cover lower-hazard sectors such as offices, shops, hospitality and leisure, and with sector regulators such as the Office for Nuclear Regulation and the Office of Rail and Road. In Scotland, prosecutions are decided by the Crown Office and Procurator Fiscal Service rather than by HSE. Northern Ireland has its own regulator, HSENI.

Inspectors have strong administrative tools. They can serve improvement notices and prohibition notices without going to court, and since 2012 HSE has charged businesses a “fee for intervention” when it finds a material breach. HSE raised the hourly rates it charges under several cost-recovery schemes from 1 April 2026.

Criminal penalties are a defining feature. Fines in the Crown Court are unlimited, and the Sentencing Council’s guideline links the level of fine to the offender’s turnover as well as to culpability and the harm risked. Individuals, including directors and managers, can face up to two years in prison for most health and safety offences. Where a death results, organisations can also be prosecuted under the Corporate Manslaughter and Corporate Homicide Act 2007, and individuals for gross negligence manslaughter.

The European Union

There is no EU-level inspector. Article 4 of the Framework Directive requires member states to make sure there are adequate controls and supervision, but how they do it is left to national law. Models vary widely. In Germany, statutory accident insurance institutions (the Berufsgenossenschaften and similar bodies) write accident-prevention rules and inspect alongside the state labour authorities. In France, labour inspectors enforce the Labour Code. Nordic countries typically combine strong inspectorates with dedicated workers’ safety representatives.

The Union’s role is coordination and monitoring:

The UK was a full participant in these bodies before 2021. HSE is no longer part of the EU institutional network, so Britain no longer receives that structured peer review, though HSE still works with international bodies and individual regulators.

Penalties compared

The directives require that national systems be effective, but they do not set penalty levels. Sanctions in the member states therefore range from administrative fines to criminal prosecution of managers, and the amounts differ greatly. British courts’ turnover-linked fines for large companies are generally among the heaviest of any system, though comparisons are hard because many EU states impose liability through insurance and social security schemes as well as courts. A business operating in several countries should not assume that a low-penalty jurisdiction means a low expectation of compliance. Inspections, stop-work orders and civil liability can all carry substantial consequences.

Key regimes compared

On most core workplace topics, Great Britain’s regulations are still near-copies of the EU directives they came from, because they were written to implement them and have rarely been rewritten. The differences that matter sit in how duties are framed, in a few specific numbers, and in areas where only one side has legislated since 2020.

TopicGreat BritainEuropean UnionCurrent position
Risk assessmentManagement of Health and Safety at Work Regulations 1999; significant findings recorded for employers with five or more staffFramework Directive 89/391/EEC; documented assessment, with national rules allowed for the smallest firmsVery similar
Worker consultationSafety representatives (trade-union appointed) and consultation regulations of 1977 and 1996Framework Directive requires consultation and participation; many states mandate safety committees or elected representativesSimilar aims, different mechanics
Work equipment and liftingPUWER 1998 and LOLER 1998Work Equipment Directive 2009/104/ECVery similar
Manual handling and display screensRegulations of 1992Directives 90/269/EEC and 90/270/EECVery similar; EU review under way
Work at heightWork at height Regulations 2005Directive 2001/45/EC, amending the Work Equipment DirectiveVery similar
Noise and vibrationControl of Noise at Work Regulations 2005 and Control of Vibration at Work Regulations 2005Directives 2003/10/EC and 2002/44/ECVery similar
Hazardous substancesCOSHH 2002; workplace exposure limits in EH40Chemical Agents Directive 98/24/EC and Carcinogens Directive 2004/37/ECSimilar, with divergence in limit-setting
AsbestosControl of Asbestos Regulations 2012; control limit of 0.1 fibres per cm³ over four hoursDirective 2009/148/EC, amended in 2023 to 0.01 fibres per cm³ over eight hoursDiverging
ConstructionCDM 2015 with principal designer and principal contractorDirective 92/57/EEC with safety coordinatorsDifferent models
Working timeWorking Time Regulations 1998 with an individual opt-out from the 48-hour limitWorking Time Directive 2003/88/ECSimilar text, different case law
Accident reportingRIDDOR 2013, under reviewNational systems; common statistical definitions for reportingDifferent

Where the match is closest

Risk assessment, work equipment, manual handling, display screens, noise and work at height are the clearest cases. The British regulations and EU directives require the same steps in the same order: assess, control, inform, train and review. Even the numbers match. Both systems use the same lower and upper exposure action values for noise (80 and 85 dB(A)) and the same daily limit of 87 dB(A) allowing for hearing protection. A safety adviser trained in one system can move to the other with very little relearning on these subjects.

Where structure differs

Consultation shows how similar aims can reach different mechanics. Britain’s regime grew from trade-union appointed safety representatives, supplemented since 1996 by direct consultation or elected representatives where no union is recognised. Many EU states give statutory roles to works councils, elected safety delegates or joint committees, with stronger rights to time off and training, and in some cases rights to stop dangerous work.

Construction is the clearest structural contrast. CDM 2015 places named duties on clients, designers, principal designers, principal contractors and contractors, so responsibility follows the project hierarchy. The EU directive instead centres on safety and health coordinators, appointed for the design and execution stages, and national laws vary in how they apply it.

Working time also shows divergence in case law as much as text. The two systems share a 48-hour average weekly limit, minimum daily and weekly rest, and statutory paid leave. But the British law relies heavily on the individual opt-out the Directive permits, which many member states allow only in narrow circumstances. The EU Court of Justice also held in 2019 (Case C-55/18) that employers must have a reliable system for measuring each worker’s daily working time. That ruling binds EU states. Britain has no equivalent duty to record every worker’s daily hours, and since Brexit it is not bound by the ruling.

Chemicals and exposure limits

Chemicals show the biggest practical split. Both sides begin from the same hazard classification system, the UN’s Globally Harmonised System, and both retain a REACH-style registration regime. But UK REACH and EU REACH are now separate, with separate registration requirements, deadlines and databases. GB CLP also now follows a different amendment process from the EU’s CLP, as described earlier. Workplace exposure limits are set in separate processes too: the EU adopts binding and indicative limits at Union level, while Britain’s limits are published and revised through HSE’s EH40 list, advised by its own committees.

Asbestos illustrates the point. The 2023 EU amendment cut the binding limit tenfold, to 0.01 fibres per cm³, with transposition due by 21 December 2025 and a move to more sensitive electron-microscopy measurement by 2029. Great Britain’s control limit remains 0.1 fibres per cm³, but it is averaged over four hours rather than eight, which HSE regards as the more conservative measure. In 2026 HSE published a review concluding that there was no clear evidence that lowering the limit would improve health outcomes, and argued that competence, training and enforcement matter more than the number. HSE has separately consulted on changes to its asbestos regulations covering clearance, surveys and notifiable non-licensed work, with responses closing in January 2026. Where the EU has tightened a number and Britain has deliberately held its own, the two systems are no longer aligned by default.

Where the systems are diverging

Most divergence so far is “passive”: the EU has legislated and Great Britain has stood still, so gaps open without any British decision to differ. A smaller but growing share is “active”, where Britain has chosen its own route. Four areas matter most.

Product safety and conformity marking

Product rules are where the two systems touch most directly, because machinery, protective equipment and electrical goods carry workplace risks as well as consumer ones. Britain originally planned to replace the CE mark with its own UKCA mark. After industry pressure, the Product Safety and Metrology etc. (Amendment) Regulations 2024 made recognition of CE marking indefinite for 21 product regulations, covering machinery, personal protective equipment, electrical and radio equipment and toys. In Great Britain, a CE-marked product in those categories can generally be sold without UKCA marking. UKCA remains necessary for some categories outside that scheme, such as construction products. Northern Ireland follows EU rules, so there CE marking is required and a UKCA mark alone is not valid. Because indefinite recognition is a policy choice rather than a treaty guarantee, some manufacturers keep UKCA marking as insurance.

Machinery is the next test. Regulation (EU) 2023/1230 replaces the Machinery Directive from 20 January 2027. It adds requirements for artificial intelligence in safety functions, cybersecurity, autonomous machinery and digital instructions, and widens mandatory third-party assessment for certain high-risk categories. Northern Ireland must apply it, and a 2026 statutory instrument provides for its enforcement there. For Great Britain the position is open. The government has run a call for evidence on machinery legislation, and its own explanatory material warns of a possible cliff edge in January 2027 if products meeting the new EU rules are not accepted. A business exporting machinery to both markets should plan for the EU deadline and watch the GB decision.

Chemicals

Chemicals regulation has diverged more than any other area. UK REACH and EU REACH are separate systems. The EU has also revised its CLP Regulation, while Great Britain has used the 2023 Act’s powers to change its own, abolishing the classification and labelling notification and creating the fast-track route described earlier. HSE says its policy is to maintain high levels of protection. Critics argue that a divergent GB system may produce different labels for the same chemical on either side of the Channel, and that monitoring divergence is hard. Northern Ireland, by contrast, remains under EU CLP.

New EU initiatives with no British equivalent

The EU’s current Strategic Framework on Health and Safety at Work covers 2021 to 2027. Its main active threads are:

  • Psychosocial risks. No dedicated EU directive exists, although the European Parliament has repeatedly asked the Commission for one covering stress, burnout and work organisation, and trade unions are campaigning for it. Several member states, including Belgium, Denmark and Sweden, already have specific national rules.
  • Review of older directives. The Commission’s Quality Jobs Roadmap promised a mid-2026 report on how the Framework Directive and related directives work in practice, and a review of the Workplace and Display Screen Equipment directives. The European Parliament held a hearing on the post-2027 strategy on 2 June 2026.
  • Digital work. The Platform Work Directive, adopted in 2024, includes rules on algorithmic management and is due for national transposition around the end of 2026. The EU AI Act and the new Machinery Regulation also affect workplace technology.
  • Hazardous substances. The EU has tightened limits for carcinogens and other substances, including asbestos, and has more updates planned.

Great Britain has no matching legislative programme. Instead HSE works mainly through campaigns, guidance and enforcement priorities.

British reforms of its own

Britain is also making its own changes, partly in response to domestic pressures rather than Brexit. HSE has consulted on the first major overhaul of RIDDOR, the injury reporting regulations, since 2013, with responses closing on 30 June 2026. It has also consulted on revising its asbestos regulations. Work-related stress is a major focus, with the Working Minds campaign and inspections that treat stress as a risk to be assessed under the Management Regulations. Building safety has its own regime under the Building Safety Act 2022, and a new duty for venues and events under Martyn’s Law is due in spring 2027. None of these has an EU counterpart, which shows the UK system is evolving rather than frozen.

What still unites them, and what it means in practice

The shared core is large and durable. Both systems place the primary responsibility on the employer. Both expect a risk-based approach in which hazards are identified, removed where possible, and otherwise controlled by measures that protect groups before individuals. Both require information, instruction, training and some form of worker involvement, and both expect employers to have access to competent safety advice. These ideas come from the same intellectual tradition, including the Robens philosophy of self-regulation within a legal framework and international labour standards that both sides support.

Some technical infrastructure also remains common. British standards bodies stay full members of the European standards organisations CEN and CENELEC, so a large body of European harmonised standards for machinery and protective equipment continues to be used on both sides. Management-system standards such as ISO 45001 are international and used in both markets. Professional bodies and trainers move freely between the two systems, and the vocabulary of safety practice remains almost identical.

That shared base means that most compliance programmes for UK workplaces transfer to EU workplaces with adaptation rather than reinvention. But the differences above point to a short list of practical checks.

  • Treat Northern Ireland as its own case for products. EU product rules apply there, and workplace law follows local rules and HSENI.
  • Plan for 20 January 2027 if you make or import machinery. Compliance with the new EU Machinery Regulation is mandatory for EU and Northern Ireland sales from that date. For Great Britain, wait for the government’s decision before assuming that EU-compliant machinery will be accepted automatically.
  • Keep chemical compliance separate. Registrations, safety data sheets and classifications for UK REACH and GB CLP may differ from the EU’s. Do not assume that an EU registration covers Great Britain or the reverse.
  • Check national law in each EU state. A directive sets a minimum. A country may require more, such as formal safety committees, particular training hours or psychosocial risk rules. Using the British approach as a template is a reasonable start, but it does not replace a check of local requirements.
  • Use the strictest exposure limit when working across both. For asbestos in particular, the EU’s binding limit is 0.01 fibres per cm³ over eight hours. The GB figure is not directly comparable because it uses a four-hour average, so plan to the EU rule when working in member states.
  • Watch for case-law differences. EU court rulings on matters such as working-time recording bind member states but no longer bind Britain.

For consultancies and in-house teams, the safest posture is to build one management system around the common principles and then add a short, maintained register of jurisdiction-specific rules.

Summary

UK and EU health and safety law share the same core and are slowly separating at the edges. The ideas are the same, the day-to-day rules are largely the same, and the gaps are growing mainly where the EU has legislated and Great Britain has not, or where Britain has chosen its own path.

Where they are similar

  • Both place primary responsibility on employers and require risk assessment, prevention, information, training and worker involvement.
  • Most British workplace regulations still mirror the EU directives they implemented, including work equipment, manual handling, display screens, noise and work at height.
  • Both use the same hazard-classification science and rely on shared technical standards.
  • Brexit did not repeal the main workplace regulations. The Retained EU Law Act of 2023 dropped the blanket sunset clause that had threatened them.

Where they differ

  • Legal design: Britain’s law is a goal-setting statute qualified by “reasonably practicable”, while the EU’s is a directive framework of minimum rules implemented by 27 states.
  • Enforcement: HSE and local authorities enforce in Great Britain with unlimited, turnover-linked fines. The EU has no central inspector, only coordination through the Commission, EU-OSHA and SLIC.
  • Chemicals: UK REACH and GB CLP now run separately from the EU’s regimes, and amendments in 2026 have made GB CLP diverge further.
  • Products: CE marking is accepted indefinitely in Great Britain for 21 regulations, but Northern Ireland follows EU rules, and the EU Machinery Regulation applies from 20 January 2027 with no GB decision yet.
  • Exposure limits and new topics: the EU has cut its asbestos limit tenfold and is considering psychosocial risk rules, platform work and a post-2027 strategy. Britain has kept its own asbestos control limit after an HSE review and relies mainly on guidance and its own consultations, such as those on RIDDOR and the asbestos regulations.
  • Northern Ireland: it sits between the two, applying EU product rules but local workplace law.

What to watch next

  1. The UK government’s decision on machinery rules before 20 January 2027.
  2. Any Commission proposal on psychosocial risks and the shape of the EU’s post-2027 strategy.
  3. The outcome of the RIDDOR and asbestos consultations in Great Britain.
  4. Further use of the 2023 Act’s powers to amend chemicals and other assimilated law.

The practical message for businesses is to build around the shared principles, and to keep a maintained register of the specific rules that now differ by jurisdiction. We can develop your legal register and maintain it. Contact one of our team now to see how we can help your business.

Does the Control of Asbestos Regulations apply to my business?

If your business owns, manages or is responsible for repairing a non-domestic building, or if your people could disturb the fabric of a building during their work, the Control of Asbestos Regulations 2012 (CAR 2012) almost certainly apply to you. Asbestos was not fully banned in the UK until 1999, so any building built or refurbished before 2000 may contain it. This guide explains who is covered, what you must do, and how to check your own position.

Who do the Control of Asbestos Regulations apply to?

CAR 2012 apply to almost every workplace in Great Britain, but the duties you hold depend on your role. Three groups are caught:

  • Owners and managers of non-domestic premises. Offices, shops, factories, warehouses, schools, farms, care homes and pubs all count, as do the shared areas of blocks of flats and other multi-occupancy homes.
  • Tenants with repair or maintenance responsibility. If your lease makes you responsible for the fabric of the building, you share the duty to manage asbestos, or hold it outright.
  • Employers whose staff may disturb asbestos. Electricians, plumbers, joiners, gas fitters, decorators, telecommunications engineers and facilities teams can all drill into, cut or damage asbestos-containing materials without knowing it.

Self-employed people are covered in the same way as employers. Homeowners living in their own private home are not dutyholders, but a tradesperson working in that home still is.

Does the Control of Asbestos Regulations Apply to You?

Do your business premises have asbestos? Do your employees come into contact with it?

The duty to manage asbestos (Regulation 4)

Regulation 4 is the part that catches most small and medium-sized businesses. If you have it, you must:

  1. Find out whether asbestos is present. Take reasonable steps to locate materials likely to contain it, and assume a material contains asbestos unless you have strong evidence it does not.
  2. Keep a written record of where it is, what condition it is in and how much there is. This is your asbestos register.
  3. Assess the risk that anyone could be exposed to fibres from those materials.
  4. Prepare a management plan that says how you will keep the risk under control, and put it into action.
  5. Review and monitor the plan and the register, especially after any change to the building or the condition of the materials.
  6. Pass the information on to anyone likely to disturb the materials, including contractors, before they start work.

The usual starting point is an asbestos management survey carried out by a competent surveyor, following HSE guidance in HSG264. Sampling and analysis should use a UKAS-accredited laboratory. Asbestos left in good condition and unlikely to be disturbed can often stay where it is, as long as it is managed.

Work that disturbs asbestos

Separately from the duty to manage, CAR 2012 sets rules for any work that could disturb asbestos. These depend on the type of material and the risk of releasing fibres.

  • Licensed work. Work on higher-risk materials such as sprayed coatings, lagging and most asbestos insulating board must be done by a contractor licensed by the HSE. The work must be notified to the enforcing authority, normally at least 14 days in advance.
  • Notifiable non-licensed work (NNLW). Some lower-risk work does not need a licence but must still be notified, and workers need health surveillance and records of the work must be kept.
  • Non-licensed work. Short, low-risk tasks, such as removing a few asbestos cement sheets or drilling into textured coating, still need proper controls, trained workers and a risk assessment.

If your employees do any of this work, you must also give them information, instruction and training at the right level for what they do. Even workers who never handle asbestos on purpose need asbestos awareness training if their work could disturb it.

Quick check: does it apply to my business?

Your situationDoes CAR 2012 apply?What it means for you
You own or manage a non-domestic building built before 2000YesYou hold the duty to manage: survey, register, risk assessment and management plan
You rent premises and your lease makes you responsible for repairsYesYou share or hold the duty to manage, so check your lease and agree responsibilities in writing
You rent premises, the landlord handles all repairs and maintenancePartlyThe landlord holds the duty, but you should ask to see the asbestos register and plan
You manage shared areas of flats or a multi-occupancy buildingYesCommon areas are covered by the duty to manage
You send staff into other people’s buildings (trades, maintenance, installers)YesStaff need asbestos awareness training and must check the register before starting work
Your premises were built after 2000 and have not been refurbished with older materialsUnlikelyKeep a record of how you decided, and check if the building has been altered
You work from your own private homeNoThe duty to manage does not cover private homes, but trades working in them are still covered

If you cannot say for certain which row you fall into, treat the regulations as applying until you have checked.

Northern Ireland, the Isle of Man and the Republic of Ireland

CAR 2012 itself applies in Great Britain. If you operate elsewhere, different legislation applies, although the principles are very similar.

If your business has premises in more than one jurisdiction, you need to manage each site against the law that applies there.

What happens if you ignore the regulations?

Breaches of CAR 2012 are prosecuted regularly. Penalties include unlimited fines and, in serious cases, prison sentences for individuals. Beyond the legal risk, unmanaged asbestos can lead to contractors, cleaners or staff being exposed, claims for illness that can take decades to appear, and delays or cost increases when a refurbishment or sale uncovers material you did not know about.

Frequently asked questions

Do I need an asbestos survey? If you hold the duty to manage and cannot show the building is asbestos-free, a survey is the normal way to meet it. A refurbishment and demolition survey is needed before any major building work.

Does it apply to a small office or shop? Yes. Size makes no difference. If the building is non-domestic and you own it, manage it or are responsible for repairs, the duty applies.

Does it apply if I only rent my premises? It depends on your lease. The duty falls on whoever has repair or maintenance responsibility, or on the person who controls the premises. Where there is no clear owner of the duty, the person in control of the building holds it.

How often should I review my asbestos register? There is no fixed interval. Review it when anything changes, such as damage, building work or a change in use, and carry out regular condition checks. Many businesses reinspect known materials once a year.

Do my staff need training? Anyone whose work could disturb asbestos needs asbestos awareness training. Those who carry out non-licensed or notifiable work need higher levels of training.

Next steps

  1. Establish when your premises were built and whether they have been altered.
  2. Check your lease, or ask your landlord, to confirm who holds the duty to manage.
  3. Ask for the asbestos register and management plan, or arrange a survey if there is none.
  4. Make sure anyone working on the building sees the register before they start.
  5. Arrange asbestos awareness training for staff who could disturb the fabric of the building.

We review your business premises and activities to determine which legislation applies to you as well as detailing the steps you need to take to comply. To discuss your needs further, please contact one of our team.

This article is general guidance and does not constitute legal advice or replace advice on your own premises.

EU vs UK Environmental Regulation After Brexit: A Business Guide

Position as at October 2026. Regulation in this area is moving quickly, so check the current status of individual measures before acting.

When the UK left the EU, the government’s stated aim was to keep environmental standards at least as high as before while gaining the freedom to regulate differently. Six years on, the picture is more complicated than either “race to the bottom” or “business as usual” suggests. The UK and EU have diverged in some areas, drifted passively apart in others, and are now deliberately re-aligning in a few of the most commercially important ones.

This article compares the two systems, explains where they differ and why, and sets out what the direction of travel means for businesses that operate in, or trade with, both markets.

EU UK environmental regulation post Brexit

EU vs UK Environmental Regulation, what has changed since Brexit?

Summary: the key points

  • Structure. The UK retained most EU-derived environmental law as “assimilated law” in 2021, but now amends it independently. The EU has kept legislating, so divergence is partly active (UK changes) and partly passive (the EU changes and the UK does not follow).
  • Governance. The UK replaced Commission and Court of Justice oversight with the Office for Environmental Protection (OEP), which has real powers but fewer than its EU counterparts.
  • Chemicals. UK REACH and EU REACH are now separate regimes, with separate registrations, deadlines and costs. Neither side is currently pursuing a full rewrite.
  • Climate and carbon. The UK runs its own Emissions Trading Scheme. Both sides are now moving towards linking them, alongside border carbon taxes (CBAMs).
  • Planning and nature. England has taken a distinctive route through the Planning and Infrastructure Act 2025, which the OEP and NGOs have criticised as weakening protections.
  • Simplification. Both sides are in a deregulatory mood. The EU’s “omnibus” programme and the UK’s planning reforms pursue similar goals by different means.
  • Northern Ireland. NI still applies a defined body of EU law under the Windsor Framework, creating a three-way compliance map across the EU, Great Britain and Northern Ireland.

1. The legal starting point

On 31 December 2020 the UK converted EU environmental law into domestic law through the European Union (Withdrawal) Act 2018. Directly applicable EU regulations became UK statutory instruments, and directives that had been implemented through UK legislation stayed in place. In 2023 the Retained EU Law (Revocation and Reform) Act renamed this body “assimilated law” and ended the special status it had held.

On day one the two systems were almost identical. The divergence since then comes from three sources:

  1. Active divergence: the UK changes or replaces a rule.
  2. Passive divergence: the EU adopts new legislation and the UK does not follow.
  3. Internal divergence: England, Scotland, Wales and Northern Ireland make different choices on devolved matters such as waste, water and nature.

The third source matters more than it is often given credit for. Because environmental policy is largely devolved, there is no single “UK” regime in many areas.

2. Governance and enforcement

Before Brexit, the European Commission could investigate member states and bring them before the Court of Justice, which could impose financial penalties. After Brexit, the UK’s Environment Act 2021 created the Office for Environmental Protection, which scrutinises government performance, investigates alleged failures and can bring enforcement proceedings.

Differences worth noting:

FeatureEUUK (England-focused)
Oversight bodyEuropean Commission, with Court of Justice backstopOffice for Environmental Protection
Sanctions on governmentCourt-imposed fines on member statesDeclarations and enforcement through the courts; no equivalent fines
Environmental principlesEmbedded in the TreatiesStatutory duty to have due regard to a policy statement on environmental principles
Target settingBinding EU-level targets (climate, nature restoration, waste)Statutory targets set domestically under the Environment Act 2021 and Climate Change Act 2008

The OEP has been willing to criticise the government, including on the planning reforms discussed below, but its powers are narrower than those of the Commission and Court, and the UK government’s response to its recommendations is advisory in practice.

3. Chemicals: two REACH regimes

Chemicals regulation is where divergence is most visible to businesses, because it creates direct, duplicated costs.

UK REACH took effect on 1 January 2021 and applies in Great Britain. It is administered by the Health and Safety Executive with policy led by Defra. It has its own registrations, its own substance evaluation and its own restrictions and authorisation lists. The government is developing an Alternative Transitional Registration model (ATRm) to reduce data requirements and cost, and, because the legislation could not be completed in time, it has extended the transitional registration deadlines to 27 October 2029, 2030 and 2031.

EU REACH continues to apply in the EU and, for most purposes, in Northern Ireland. The Commission spent years preparing a major revision, but it confirmed in April 2026 that it would not open the regulation. It is instead pursuing simplification through secondary legislation, plus stronger enforcement against non-compliant products at EU borders and in the market. A large PFAS restriction proposal is expected to progress by the end of 2026.

What this means in practice:

  • A business supplying both markets needs two sets of registrations, or access to two sets, and must manage two substance lists.
  • Neither side is currently converging, and neither is conducting a wholesale rewrite.
  • Enforcement is likely to be the main change in the EU, while cost and data requirements are the main uncertainty in GB.

4. Climate policy and carbon markets

Separate trading schemes, heading towards a link

The UK left the EU Emissions Trading System and launched the UK ETS in 2021. The UK scheme is smaller and has historically traded at a lower price. It is expanding, including a commitment to bring waste incineration in from 2028.

At the May 2025 UK-EU summit, both sides agreed in principle to link the two schemes. The EU Council approved a negotiating mandate in November 2025, and negotiations have been under way since early 2026. Linking would require the UK to track relevant EU rules “dynamically”, and would allow allowances to be traded across both markets. The intended scope includes power, industry, aviation and maritime.

Carbon border taxes

The more immediate pressure comes from carbon border adjustment mechanisms:

  • The EU CBAM entered its definitive phase on 1 January 2026. UK exporters of covered goods such as steel, aluminium, cement and fertiliser currently receive no exemption. Importers will declare 2026 emissions by September 2027.
  • The UK CBAM starts on 1 January 2027, covering aluminium, cement, fertiliser, hydrogen and iron and steel. Importers above a £50,000 registration threshold will be liable. Indirect emissions are excluded until 2029 at the earliest. Primary legislation is in the Finance Act 2026, with secondary legislation still being finalised.

A completed ETS link would create conditions for mutual CBAM exemptions, but only once the agreement is in force, so there is a real risk of paying both ways in the interim. Businesses in covered sectors should treat this as a live cost issue, not a distant policy debate.

5. Nature, planning and development

This is where UK and EU approaches have diverged most politically.

England has pursued a more flexible planning route. The Planning and Infrastructure Act 2025, which became law in December 2025, creates Environmental Delivery Plans prepared by Natural England and a Nature Restoration Fund. Developers can pay a Nature Restoration Levy instead of carrying out some site-specific assessment and mitigation. The government’s position is that this provides a different route to meet existing obligations, not a removal of protections. The OEP and several nature charities have argued it reduces the level of legal protection for specific habitats and species, and the Act’s amendments responded to part of that criticism. Secondary legislation on how the levy operates was consulted on over summer 2026.

Biodiversity net gain is also evolving. It is due to become mandatory for nationally significant infrastructure projects from 2 November 2026, while a separate consultation has examined exempting brownfield development.

The EU has taken a more target-led approach through measures such as the Nature Restoration Law, which sets binding restoration objectives for member states. At the same time, the Commission has said it will stress-test the Habitats and Birds Directives, so a softening of site-based protection is under discussion in Brussels too.

The honest comparison is that both sides are under pressure to speed up infrastructure and housing, and both are testing how far that can go before it undermines nature protection. The UK has moved first and in a more structural way in England.

6. Industrial regulation and simplification

The EU has set out a programme of “omnibus” simplification packages. The Environmental Omnibus, proposed in December 2025, targets industrial emissions, circular economy reporting, extended producer responsibility, environmental assessments and geospatial data. The Commission says it will save around €1 billion a year for business. The Council agreed its position in June 2026, and EU leaders have set a goal of concluding all simplification packages by the end of 2027.

Changes proposed include allowing environmental management systems under the Industrial Emissions Directive to be prepared at company level instead of per installation, and simplifying reporting for livestock and aquaculture operators. The Council has retained a chemicals inventory requirement as a monitoring tool.

In Great Britain, industrial permitting remains based on the Environmental Permitting Regime derived from the previous EU framework. The UK has focused its reform energy on planning and infrastructure delivery rather than rewriting industrial emissions rules, so the more important divergence for permitted sites is likely to come from what the EU changes and the UK leaves alone.

7. Dynamic alignment: the reset

The most significant strategic shift is political. As part of the “reset” of UK-EU relations, the UK has agreed to pursue dynamic alignment with EU law in three areas: a sanitary and phytosanitary (SPS) agreement, ETS linking, and participation in the EU electricity market. UK participation in decision-shaping and a financial contribution to the EU’s work were also agreed. Electricity negotiations were formally launched in March 2026.

For environmental regulation, this has several consequences:

  • SPS alignment would reverse a number of post-Brexit divergences in areas such as pesticides, food and feed. Campaign groups argue that GB pesticide standards have fallen behind the EU’s, so alignment would raise the bar in some cases.
  • Reduced regulatory freedom. Critics, including some parliamentarians, argue that tracking EU rules limits the UK’s ability to set its own course. The House of Lords European Affairs Committee opened an inquiry into dynamic alignment in March 2026, including its implications for devolution.
  • Timing. The government has indicated it wants legislation by the end of 2026 so an SPS agreement can take effect around mid-2027, but the detail remains subject to negotiation.

8. Northern Ireland: a third regime

Under the Windsor Framework, Northern Ireland continues to apply EU law on goods, including much environmental product legislation. Examples include EU REACH and CLP, and much of the EU Packaging and Packaging Waste Regulation, while Great Britain follows domestic packaging and producer responsibility rules. The EU Deforestation Regulation is set to apply in NI in phases from 30 December 2026, and the UK government has indicated it will consult on a GB regime covering similar commodities.

This produces a three-way compliance map. A single product placed on the EU, NI and GB markets can face different packaging, chemicals and supply chain due diligence rules, and GB producers selling into NI may need to change practices to meet EU requirements.

9. Side-by-side comparison

AreaEUGreat Britain / UK
OversightCommission and Court of JusticeOffice for Environmental Protection
ChemicalsEU REACH; full revision shelved; simplification by secondary legislationUK REACH; ATRm in development; deadlines 2029 to 2031
Carbon pricingEU ETS; CBAM definitive phase from January 2026UK ETS; UK CBAM from January 2027; ETS linking under negotiation
Nature and planningBinding restoration targets; Habitats Directives under reviewEnvironmental Delivery Plans and Nature Restoration Fund in England
Industrial emissionsIED recast; omnibus simplification under negotiationEnvironmental Permitting Regime; less active reform
PackagingPPWRDomestic packaging and EPR rules (EU PPWR largely applies in NI)
DeforestationEUDR applying from December 2026 (phased in NI)GB regime proposed; consultation planned
Direction of travelSimplify and enforce, but keep objectivesDeregulate delivery, re-align selectively through the reset

What this means for businesses

  1. Treat the UK as at least two markets. GB and NI will continue to follow different rules for the foreseeable future, and the EU is a third.
  2. Plan for double chemicals compliance. Map which substances are registered under each REACH regime and monitor ATRm developments.
  3. Model carbon border exposure now. If you import or export steel, aluminium, cement, fertiliser or hydrogen, work out your CBAM liability on both sides and what an ETS link might change.
  4. Watch dynamic alignment. It may improve predictability for agri-food and energy-intensive trade, but it also means EU decisions will increasingly shape GB rules.
  5. Expect planning and permitting to change in England. If your projects affect protected sites, follow the Nature Restoration Levy regulations and Environmental Delivery Plan roll-out.
  6. Build a regulatory horizon scan. With both sides in reform mode, a quarterly review of legislative changes will prevent costly surprises.

Conclusion

The post-Brexit story in environmental law is neither a collapse in standards nor a frozen copy of EU rules. It is a gradual and uneven separation, now partially reversed by political choices to re-align in carbon, agri-food and energy. The most useful way for businesses to think about it is as a moving map: stable in some places, fast-changing in others, and increasingly shaped by trade as much as by environmental policy.

This article is for general information only and is not legal advice. Regulations and deadlines change, so confirm the current position with the relevant regulator or a qualified adviser.

What Businesses Need to Comply with UK REACH?

If your business makes, imports or uses chemicals in Great Britain, UK REACH almost certainly affects you. Since the end of the Brexit transition period, GB has operated its own chemicals regime, separate from EU REACH, and the rules, deadlines and costs have been shifting ever since.

This guide explains who UK REACH applies to, what you must do, and the practical steps to take now.

What is UK REACH?

UK REACH (Registration, Evaluation, Authorisation and Restriction of Chemicals) is the Great Britain chemicals regulation that took over from EU REACH on 1 January 2021. It is administered by the Health and Safety Executive (HSE) as the UK REACH agency, with policy led by Defra.

Its core principle is “no data, no market“: a substance on the GB market must be registered, and the information needed to use it safely must be available and passed down the supply chain.

Important: UK REACH applies in England, Scotland and Wales. Northern Ireland continues to follow EU REACH under the Windsor Framework, so businesses trading across the UK may need to comply with both systems.

UK REACH compliance

Does REACH apply to your business?

Who needs to comply?

Your obligations depend on your role in the supply chain.

RoleWhat it meansTypical obligations
ManufacturerYou make a substance in GBRegister substances at 1 tonne or more per year; classify and label; supply compliant safety data sheets
ImporterYou bring a substance, a mixture or an article into GB from outside GB, including from the EURegister substances at 1 tonne or more per year; meet transitional notification or registration requirements; communicate hazards downstream
Downstream userYou use chemicals in your business activities (formulators, manufacturers, industrial and professional users)Follow the safety data sheet and exposure scenarios; check that suppliers are registered; pass information up and down the chain
Distributor / retailerYou store and sell chemicals without changing themPass on safety information; check the supply chain is compliant
Article producer / importerYou make or import products such as equipment, furniture or textilesNotify and communicate on SVHCs in articles; check restrictions apply

Obligations apply per legal entity, so a group with several GB companies needs to assess each one.

The main UK REACH requirements

1. Registration

Manufacturers and importers of substances at 1 tonne or more per year must register them with HSE. Because most businesses could not complete full registrations on day one, the government introduced transitional arrangements:

  • Grandfathering: companies that held an EU REACH registration could carry it across to UK REACH.
  • Downstream User Import Notification (DUIN): downstream users who had been importing from the EU could notify HSE and keep trading while full registration deadlines run.
  • New Registration of Existing Substances (NRES): a route for substances that were not already registered under EU REACH but were on the GB market.
  • Inquiry and registration of new substances: substances not previously on the GB market need a full registration before supply.

2. Transitional registration deadlines

The deadlines have been pushed back twice. Defra has been developing an Alternative Transitional Registration model (ATRm) that is intended to reduce data requirements and costs. Because the ATRm could not be legislated before the original first deadline of October 2026, the government extended the submission dates. The revised deadlines are 27 October 2029, 27 October 2030 and 27 October 2031, phased by tonnage and hazard:

  • 27 October 2029: the highest tonnage and hazard band (broadly substances at 1,000 tonnes or more per year, and certain highly hazardous substances at lower tonnages)
  • 27 October 2030: substances at 100 tonnes or more per year
  • 27 October 2031: all other substances at 1 tonne or more per year

Even with extra time, you should not wait. The detailed ATRm information requirements are still being finalised, and data gathering, supplier agreements and cost-sharing take time.

3. Safety data sheets and communication in the supply chain

Suppliers must provide safety data sheets (SDS) that meet UK REACH requirements, and downstream users must apply the advice in them. Make sure your SDSs carry the correct GB details and that you have a process to update them when information changes. Where substances of very high concern (SVHCs) are present in articles above the threshold concentration, you must pass on information so the articles can be used safely.

4. Restrictions

Annex 17 of UK REACH lists substances and uses that are restricted or banned. If you manufacture, supply or use a restricted substance, you need to confirm that your use is permitted and that any conditions are met. Restrictions can apply to substances on their own, in mixtures and in articles.

5. Authorisation

Substances of very high concern can be added to the Authorisation List (Annex 14), after which they cannot be used or placed on the GB market without authorisation. Watch the UK REACH Candidate List and the Authorisation List and check whether any of your substances are listed.

6. Classification and labelling

UK REACH works alongside GB CLP, which governs the classification, labelling and packaging of hazardous chemicals. Suppliers must classify and label correctly, and use the GB mandatory classifications where they apply.

Practical steps to get compliant

  1. Map your chemicals. List every substance and mixture you make, import or use, with volumes and suppliers.
  2. Confirm your role. Identify whether you are a manufacturer, importer, downstream user, distributor or article producer for each substance.
  3. Check your supply chain. Ask suppliers whether they hold a UK REACH registration or notification, and get confirmation in writing.
  4. Review your transitional status. Establish whether you have a grandfathered registration, a DUIN, an NRES submission or nothing at all.
  5. Check tonnage bands and deadlines. Work out which deadline applies to each substance and plan backwards from it.
  6. Review safety data sheets. Check they are current and meet UK requirements.
  7. Screen for restrictions and SVHCs. Check your substances and products against Annex 17 and the Candidate and Authorisation Lists.
  8. Assign responsibility and keep records. Name an owner for UK REACH, and keep evidence of your assessments and supplier correspondence.
  9. Monitor developments. Follow HSE and Defra updates on the ATRm, fees and deadlines.

What happens if you do not comply?

Supplying or using chemicals in breach of UK REACH can lead to enforcement action by regulators, including notices and prosecution, as well as commercial risk. Non-compliant supply chains can lose market access, and customers increasingly require evidence of regulatory compliance.

Frequently asked questions

Does UK REACH apply if I only import from the EU? Yes. Since 1 January 2021, substances imported from the EU into GB are treated as imports and can carry registration or notification duties.

Does UK REACH apply in Northern Ireland? No. Northern Ireland follows EU REACH under the Windsor Framework, although businesses moving goods between NI and GB may face obligations under both regimes.

Do small businesses need to comply? Yes. There is no general exemption for small businesses, although the 1 tonne per year threshold means many smaller businesses fall into the downstream user category rather than registrant.

Have the deadlines changed? Yes. The transitional registration deadlines were extended to 27 October 2029, 2030 and 2031. Check the current position with HSE or Defra before making decisions.

How we can help

UK REACH sits alongside COSHH, GB CLP and your wider health, safety and environmental duties. We can help you map relevant legislation for your business and compile a legal register. The register will also include details of how your business must comply with each piece of legislation.

Contact us to discuss your legal register requirements.

This article is for general information only and is not legal advice. Regulations and deadlines change, so confirm the current position with HSE, Defra or a qualified adviser.

What Businesses Need an Environmental Permit?

If your business could pollute the air, water or land, there is a good chance it needs an environmental permit. Operating a regulated facility without one is a criminal offence, and the consequences can include unlimited fines, enforcement notices, prosecution and, in serious cases, imprisonment.

The tricky part is that “regulated facility” covers a far wider range of businesses than most people expect. It is not just chemical plants and landfill sites. Dry cleaners, vehicle dismantlers, farms, food manufacturers, concrete producers and even businesses running a standby generator can all fall within scope.

This guide explains which businesses need an environmental permit, who regulates them, and how to work out where you stand.

A note on jurisdiction: this article focuses on England and Wales, where environmental permitting is governed by the Environmental Permitting (England and Wales) Regulations 2016. Scotland, Northern Ireland and the Republic of Ireland each operate their own regimes, detailed in a summary at the end.

What is an environmental permit?

An environmental permit is a legal authorisation to carry out an activity that could harm the environment or human health. It sets out conditions the operator must meet, such as emission limits, monitoring requirements, waste handling rules and pollution-control measures.

Permits are issued to the operator of the facility, meaning the person or business that controls how it runs day to day, not necessarily the landowner.

An environmental permit is not the same as planning permission, an ISO 14001 certificate or a waste carrier registration. Each has a separate legal purpose, and holding one does not remove the need for the others.

What Businesses Need an Environmental Permit?

Does your business need an environmental permit?

Which businesses need an environmental permit?

Under the 2016 Regulations, you need a permit (or must register an exemption) if you operate a “regulated facility”. The main categories are below.

1. Industrial installations (Part A(1), Part A(2) and Part B)

Larger industrial processes are regulated as installations. They are split into three tiers based on environmental risk:

  • Part A(1) installations are regulated by the Environment Agency (or Natural Resources Wales). They cover the highest-impact activities such as large chemical manufacturing, refining, metals production, major energy and large-scale waste treatment.
  • Part A(2) installations are regulated by the local authority and cover emissions to air, water and land from medium-impact activities such as some glass, ceramics and surface treatment processes.
  • Part B installations are also regulated by the local authority, but focus on emissions to air only. Typical examples include petrol stations, dry cleaners, mobile crushing plant, concrete batching, coating and printing processes, wood processing and some food and animal feed manufacture.

2. Waste operations

If you treat, store, recycle, recover or dispose of waste, you will generally need a permit. This includes:

  • Landfill sites
  • Waste transfer stations
  • Metal recycling and vehicle dismantling sites
  • Anaerobic digestion and composting facilities
  • Waste incineration, gasification and pyrolysis plants
  • Hazardous waste treatment sites

Some lower-risk waste activities may qualify for an exemption, which still requires registration with the regulator and compliance with set limits on quantities and types of waste. Many businesses assume they are exempt without checking, which is a common route to enforcement action.

3. Combustion plants and generators

Businesses running boilers, engines, turbines or generators can fall within permitting requirements depending on their thermal input. Medium combustion plants (roughly 1 to 50 megawatts thermal input) and specified generators, including some standby and backup generators, may need a permit or registration. This surprises many hospitals, data centres, manufacturers and large commercial sites.

4. Discharges to water and groundwater

You may need a permit if you discharge anything to surface water or groundwater, including trade effluent that is not going to a public sewer, treated sewage effluent from a private system, or cooling water. Some activities that could affect groundwater, such as injecting substances into the ground, also require authorisation.

5. Flood risk activities

Work in, over, under or near a main river, flood defence or sea defence may need a flood risk activity permit. This is relevant to construction, civil engineering, landscaping and riverside development, not just industrial operators.

6. Radioactive substances

Businesses that keep, use or dispose of radioactive material or radioactive waste may need a permit or registration. This can include some hospitals, laboratories, industrial gauging operations and sites handling naturally occurring radioactive material.

7. Mining waste operations

Operators that manage waste from mineral extraction, such as tailings, overburden and waste rock, fall within the regime.

8. Solvent emissions and other specific activities

Processes using significant volumes of organic solvents (for example in printing, coating or cleaning), as well as some intensive farming operations (large pig and poultry units above set capacity thresholds), also require permits.

Who regulates environmental permits?

The regulator depends on the activity:

ActivityRegulator (England)
Part A(1) installationsEnvironment Agency
Part A(2) and Part B installationsLocal authority (environmental health or environmental protection team)
Waste operations and mining wasteEnvironment Agency
Water discharges, groundwater activities, flood risk activitiesEnvironment Agency

In Wales, Natural Resources Wales takes the Environment Agency’s role.

What happens if you operate without a permit?

Operating a regulated facility without a permit, or breaching permit conditions, is an offence. Possible consequences include:

  • Enforcement and stop notices requiring you to cease operating
  • Unlimited fines in the Crown Court
  • Prison sentences for individuals in serious cases
  • Prosecution of directors and senior managers where an offence is committed with their consent or neglect
  • Clean-up and remediation costs
  • Reputational damage and difficulties with insurers, lenders and customers

Regulators also publish enforcement outcomes, so a conviction is rarely a private matter.

How to check if your business needs a permit

  1. Identify every activity on site. Consider waste handling, combustion plant, solvent use, discharges and any work near watercourses, not just your core process.
  2. Use the official checker. GOV.UK provides a “check if you need an environmental permit” tool covering permits, exemptions and standard rules.
  3. Check for standard rules permits. Many common activities can be covered by pre-set standard rules, which are quicker and cheaper than a bespoke permit.
  4. Speak to the regulator early. The Environment Agency or your local authority can confirm whether an activity needs a permit and which type. Pre-application advice can save months and reduce wasted application documents and assessments.
  5. Keep records. If you conclude no permit is needed, document your reasoning in case a regulator challenges it.

What about Scotland, Northern Ireland and the Republic of Ireland?

The principles are similar, but the legal framework and regulator differ:

If you operate across more than one jurisdiction, you cannot assume a permit in one place covers another.

Frequently asked questions

Do small businesses need an environmental permit? Size does not determine whether you need one. What matters is the activity. A small dry cleaner or a small vehicle dismantler can need a permit just as a large manufacturer can.

Is an exemption the same as not needing a permit? No. An exemption usually has to be registered, and it only applies if you stay within strict conditions.

Can I apply for a permit myself? Yes, the operator can apply directly. For complex sites, many businesses use a consultant to prepare risk assessments, management systems and technical submissions, because errors cause delays and rejections.

How long does a permit take? It varies widely. Standard rules permits can be relatively quick and determined within 6-8 months, while bespoke permits for complex sites can take even longer. Regulators set statutory determination periods, and incomplete applications restart the clock.

Do permits cost money? Yes. There is typically an application charge and an annual subsistence charge, which vary by activity and risk rating. Check the current charging scheme with the relevant regulator.

Need help working out whether you need a permit?

Getting this wrong is expensive, whether that means operating illegally or paying for a permit you did not need. At Ashbrooke Management Consultants, we help businesses identify which legislation applies to business operations and sites. Once identified, we compile all the legislation into a register and include the steps required to be compliant.

If you need to identify the legislation applicable to your business, please contact one of our team.