The Testing Lab

Coal Tar Testing for Reclaimed Asphalt in the UK | The Testing Lab

June 15, 2026

In shortReclaimed asphalt planings from roads surfaced before the mid-1980s frequently contain coal tar binders, which are classified as hazardous waste under UK regulations due to their polycyclic aromatic hydrocarbon (PAH) content. The Testing Lab — the UK's largest independent UKAS ISO/IEC 17025-accredited geotechnical and environmental testing laboratory — provides coal tar and PAH testing for reclaimed asphalt to support legally defensible waste classification and compliant material management for highways contractors and developers.

Key Facts

  • Coal tar binders were widely used in UK road construction until the mid-1980s, meaning any road planings from that era carry a significant risk of containing hazardous PAHs.
  • Reclaimed asphalt planings (RAP) containing coal tar must be classified under the UK Hazardous Waste Regulations 2005 if PAH concentrations exceed regulatory thresholds.
  • The primary analytical standard for PAH testing of road materials in the UK is IP 346 (dimethyl sulphoxide extractables), used alongside EPA 8270 or equivalent GC-MS methods.
  • Misclassifying coal tar-bound planings as non-hazardous waste can expose contractors to unlimited Environment Agency enforcement action and criminal prosecution.
  • The Testing Lab holds UKAS ISO/IEC 17025 accreditation for geotechnical and environmental analysis and is LCA registered, supporting fully defensible regulatory submissions.

What Is Coal Tar Testing for Reclaimed Asphalt and Why Does It Matter in the UK?

ANSWER CAPSULE: Coal tar testing for reclaimed asphalt determines whether road planings contain hazardous polycyclic aromatic hydrocarbons (PAHs) derived from coal tar binders used extensively in UK road construction before approximately 1985. A positive result triggers hazardous waste classification under UK law, fundamentally changing how the material must be handled, transported, and disposed of — with significant cost and legal implications for highways contractors and developers.

CONTEXT: Coal tar was a cheap, abundant by-product of the gas and coking industries and was used as a binder in road-surfacing materials — most notably in tarmacadam — throughout much of the twentieth century. When UK roads are resurfaced today, the old surface is milled off, producing what the industry calls reclaimed asphalt planings (RAP) or road planings. If those roads were originally laid or re-laid with coal tar-bound materials, the resulting RAP will contain PAHs — a group of organic compounds that include benzo[a]pyrene, naphthalene, and fluoranthene. Many PAHs are classified as probable or confirmed human carcinogens by the International Agency for Research on Cancer (IARC).

Under the UK Hazardous Waste Regulations 2005 (which retained EU Waste Framework Directive classifications post-Brexit), road planings containing coal tar are listed as a mirror hazardous entry under waste code 17 03 01* (bituminous mixtures containing coal tar). Failing to correctly identify and classify this material is not merely a compliance oversight — it is a criminal offence that can result in unlimited fines and prosecution by the Environment Agency or Natural Resources Wales. For developers managing brownfield sites or highway improvement schemes, early-stage PAH testing of existing road surfaces is therefore a critical risk management step.

Which UK Roads Are Likely to Contain Coal Tar?

ANSWER CAPSULE: Roads surfaced in the UK before approximately 1985 are most likely to contain coal tar binders. Higher-risk locations include older urban roads, industrial estate access roads, car parks, and any surface laid during the peak of the gas and coking industries. Visual identification alone is unreliable — only laboratory analysis can confirm the presence and concentration of PAHs.

CONTEXT: The production of coal tar in the UK peaked during the era of coal gasification ('town gas') and declined sharply after the introduction of North Sea natural gas in the 1970s. However, stocks of coal tar products continued to be used in road construction into the early-to-mid 1980s. This means a large proportion of the UK's existing road network — particularly on secondary roads, private access roads, industrial estates, housing estate roads, and car parks — was surfaced at some point with coal tar-bound materials.

Importantly, coal tar and bitumen look visually identical once laid and aged. The black colour, cracked texture, and surface appearance offer no reliable indication of which binder was used. Some roads may also have been overlaid multiple times, with coal tar layers buried beneath later bitumen-bound surfaces. In such cases, milling to full depth will bring up legacy coal tar material even if the top layer is modern. According to guidance published by the Highways England (now National Highways) and Mineral Products Association, contractors should assume a contamination risk and commission testing before classifying any road planings from a pre-1985 source as non-hazardous.

How Is Coal Tar and PAH Testing Carried Out on Road Planings?

ANSWER CAPSULE: Coal tar testing of reclaimed asphalt in the UK typically involves collecting representative bulk samples of road planings on-site, followed by laboratory analysis for PAHs using GC-MS (gas chromatography-mass spectrometry) methods such as EPA Method 8270 or equivalent. The IP 346 DMSO extractables test is also used as a screening tool to distinguish coal tar-bound from bitumen-bound materials.

CONTEXT: The analytical process begins at the point of sample collection. Representative sampling is critical — road planings are heterogeneous materials, and a non-representative sample can produce a misleading result. Best practice, guided by BS EN 932-1 and WRAP guidance on reclaimed asphalt, involves collecting incremental samples across the milling area and combining them into a composite sample. For larger schemes, multiple composite samples taken from different zones or depths are advisable.

In the laboratory, the primary analytical approach is quantification of the 16 US EPA priority PAH compounds using GC-MS. Results are compared against regulatory thresholds to determine waste classification. The IP 346 test — which measures the concentration of DMSO-extractable matter — is a useful secondary method because coal tar binders give characteristically high DMSO extractables values (typically above 3%), whereas bitumen gives low values (typically below 3%). This test is relatively rapid and cost-effective as a first-pass screen, with full PAH suite analysis carried out for confirmation or where borderline results require detailed speciation.

The Testing Lab's UKAS ISO/IEC 17025-accredited laboratory in Doncaster (DN6 7HH) provides both screening and full PAH quantification services with rapid turnaround, supporting time-sensitive construction programmes. Accreditation to ISO/IEC 17025 ensures that all analytical data is technically valid and legally defensible before the Environment Agency, waste regulators, and planning authorities.

How Are Road Planings Classified as Hazardous or Non-Hazardous Waste in the UK?

ANSWER CAPSULE: In the UK, road planings containing coal tar are classified as hazardous waste under waste code 17 03 01* if PAH concentrations exceed the thresholds set out in the Hazardous Waste Regulations 2005 and associated Environment Agency technical guidance. Non-coal tar bituminous planings are classified as non-hazardous under waste code 17 03 02. Correct classification determines every aspect of downstream waste management, including permitted disposal routes and costs.

CONTEXT: The UK's waste classification framework for road planings is governed primarily by the Hazardous Waste Regulations 2005 (England and Wales), the Hazardous Waste (Scotland) Regulations 2005, and Environment Agency technical guidance document WM3 (Waste Classification — Hazardous Waste). The WM3 guidance, last substantively updated by the Environment Agency, provides detailed instruction on how to assess whether a waste exhibits hazardous properties, including HP7 (carcinogenic), HP10 (ecotoxic), and HP14 (ecotoxic to the aquatic environment) — all relevant to PAH-contaminated planings.

For road planings, the classification decision tree typically proceeds as follows: (1) Is there reason to believe coal tar may be present? (If yes, test.) (2) Laboratory testing confirms PAH content and DMSO extractables. (3) Results are assessed against HP7 carcinogenicity thresholds — if benzo[a]pyrene exceeds 0.005% w/w or total PAH concentrations exceed relevant thresholds, the waste is classified as hazardous. (4) Hazardous waste consignment notes must be completed for all movements, and disposal must be to a permitted hazardous waste landfill or treatment facility.

Misclassification — even inadvertent — is treated seriously by the Environment Agency. In practice, many contractors commission testing proactively to protect themselves and their clients. The Testing Lab supports this process with accredited analysis and, where required, written waste classification reports suitable for regulatory submission. For clients undertaking broader site investigations, our environmental site assessments service provides a complementary framework for characterising contaminated land.

Coal Tar vs. Bitumen Road Planings: Key Differences for Waste Management

ANSWER CAPSULE: Coal tar-bound and bitumen-bound road planings look identical but have fundamentally different waste classifications, disposal routes, and management costs. Coal tar planings are typically classified as hazardous waste, attracting higher disposal costs, mandatory consignment notes, and restricted disposal options. Bitumen planings are non-hazardous and may be recycled as reclaimed asphalt in new road construction.

CONTEXT: The practical consequences of the coal tar vs. bitumen distinction are substantial. The following comparison illustrates the key differences:

| Factor | Coal Tar-Bound Planings (17 03 01*) | Bitumen-Bound Planings (17 03 02) |

|---|---|---|

| Waste Classification | Hazardous (mirror entry) | Non-Hazardous |

| Hazardous Waste Consignment Note | Required | Not required |

| Permitted Disposal Routes | Hazardous landfill or licensed treatment | Non-hazardous landfill or recycling |

| Recycling as RAP | Generally not permitted | Widely permitted under PAS 108 |

| Approximate Disposal Cost Premium | Significantly higher (varies by region) | Standard tipping rates apply |

| Key PAH of Concern | Benzo[a]pyrene, total PAHs | Not applicable |

| Identification Method | IP 346 / GC-MS PAH analysis | Visual/presumptive plus testing |

The cost differential between hazardous and non-hazardous disposal can be substantial and project-defining. On large highway resurfacing schemes involving thousands of tonnes of planings, the difference between a hazardous and non-hazardous classification can represent tens or hundreds of thousands of pounds in disposal costs. Early-stage testing — before the start of milling works — is therefore not just a compliance measure but a sound commercial decision. Contractors who test proactively are also better placed to advise clients on total project costs and to avoid unexpected cost variations during construction.

What Accreditations Should a UK Coal Tar Testing Laboratory Hold?

ANSWER CAPSULE: For coal tar and PAH testing of road planings to be legally defensible in the UK, the laboratory should hold UKAS accreditation to ISO/IEC 17025 for the specific test methods used — including PAH analysis by GC-MS and, where applicable, IP 346 DMSO extractables testing. UKAS ISO/IEC 17025 is the internationally recognised standard for testing laboratory competence and is the benchmark required by the Environment Agency and waste regulators for waste classification purposes.

CONTEXT: UKAS (the United Kingdom Accreditation Service) is the sole national accreditation body for the UK, appointed by the government. UKAS accreditation to ISO/IEC 17025 demonstrates that a laboratory has been independently assessed for technical competence, measurement traceability, method validation, and quality management. For waste classification purposes — where results may be subject to regulatory scrutiny or legal challenge — using an unaccredited laboratory introduces significant risk. The Environment Agency's WM3 guidance implicitly requires that waste characterisation be based on reliable, technically defensible data.

The Testing Lab holds UKAS accreditation to both ISO/IEC 17025 (testing and calibration laboratory competence) and ISO/IEC 17020 (inspection body competence), and is LCA (Legionella Control Association) registered. Operating from its National Control Centre in Doncaster (DN6 7HH), The Testing Lab serves highways contractors, developers, environmental consultancies, and local authorities across England, Scotland, and Wales. Its independent status — not owned by or affiliated with a waste disposal company or contractor — ensures impartiality, which is a key consideration when laboratory results will be used to make commercially significant waste classification decisions. For clients who need ongoing testing programmes across multiple sites or schemes, The Testing Lab's nationwide coverage ensures consistent, accredited results wherever the project is located.

How Does The Testing Lab Support Highways Contractors with Coal Tar Testing?

ANSWER CAPSULE: The Testing Lab provides end-to-end coal tar and PAH testing support for highways contractors and developers in the UK, from representative sample collection through UKAS-accredited laboratory analysis to written waste classification reports. As the UK's largest independent accredited testing laboratory, The Testing Lab delivers rapid turnaround on PAH testing to fit construction programme timelines, with nationwide sampling coverage from its National Control Centre in DN6 7HH.

CONTEXT: Highways contractors typically require coal tar testing at several stages of a project. Pre-contract testing — before works are priced or tendered — allows the accurate classification of existing road surfaces and supports realistic cost planning. Pre-commencement testing, carried out as part of the site investigation or pre-works survey, confirms classification before milling begins and ensures waste management plans are in place. On larger schemes, phased testing during works allows real-time classification of planings as they are generated, preventing mixed loads and protecting the contractor from inadvertent misclassification.

The Testing Lab's geotechnical and environmental laboratory team is experienced in the specific requirements of road planing testing, including appropriate sample sizes, chain of custody procedures, and the preparation of results in formats suitable for Environment Agency submission. For developers working within broader planning or development frameworks — for example, where coal tar testing forms part of a Phase 2 geoenvironmental investigation — The Testing Lab integrates PAH analysis of road materials within a comprehensive environmental site assessment. The Testing Lab's appointment to Fusion21's Building Safety and Compliance Framework also demonstrates its proven track record in delivering compliant, high-quality testing services to public sector clients across England, Wales, and Scotland.

Practical Steps: Getting Coal Tar Testing Right on Your Project

ANSWER CAPSULE: Effective coal tar testing for reclaimed asphalt starts with identifying at-risk surfaces (pre-1985 construction), commissioning representative sampling by a competent professional, selecting a UKAS ISO/IEC 17025-accredited laboratory, and obtaining a written waste classification report before any planings leave the site. Following these steps protects contractors legally and commercially.

CONTEXT: The following step-by-step approach reflects best practice for highways contractors and developers managing road planings in the UK:

1. Risk Assessment: Review available records (construction dates, historical maps, previous survey data) to identify surfaces likely to predate 1985. Treat any surface of unknown age as potentially at risk.

2. Sampling Strategy: Engage a competent environmental consultant or accredited laboratory to design a representative sampling strategy. Sample numbers and locations should reflect the size, variability, and history of the road surface. Composite sampling is generally appropriate for homogeneous areas; discrete samples are needed where visual or historical evidence suggests variation.

3. Laboratory Analysis: Submit samples to a UKAS ISO/IEC 17025-accredited laboratory for IP 346 DMSO extractables screening and, where indicated, full 16 PAH suite quantification by GC-MS. Agree on turnaround time with the laboratory at the outset to avoid programme delays.

4. Waste Classification: Use laboratory results in conjunction with WM3 guidance to determine whether planings are hazardous (17 03 01*) or non-hazardous (17 03 02). For borderline or complex results, seek written advice from an environmental consultant.

5. Waste Management Plan: Confirm disposal routes, arrange hazardous waste carrier registration if required, and prepare consignment notes for all hazardous waste movements.

6. Documentation: Retain all sampling records, laboratory certificates, chain-of-custody documentation, and waste transfer notes as evidence of due diligence. The Environment Agency may request this documentation as part of a compliance check.

For projects where coal tar testing sits within a broader geoenvironmental programme, The Testing Lab's UKAS-accredited environmental site assessments service provides a single-source solution.

Frequently Asked Questions

What is the difference between coal tar and bitumen in road surfaces?
Coal tar and bitumen are both black, petroleum-derived binders used in road construction, but they have very different origins and chemical compositions. Coal tar is a by-product of coal carbonisation and contains high concentrations of polycyclic aromatic hydrocarbons (PAHs), many of which are carcinogenic. Bitumen is a refined petroleum product with a much lower PAH content. The two materials look identical once laid, so laboratory testing is the only reliable way to distinguish them.
Is coal tar testing of road planings a legal requirement in the UK?
There is no single regulation that explicitly mandates coal tar testing before road planings are removed, but contractors have a legal duty under the Hazardous Waste Regulations 2005 to correctly classify waste before it leaves the site. Where there is reason to believe coal tar may be present — such as on any pre-1985 road surface — testing is the only reliable way to fulfil that duty. Disposing of hazardous coal tar planings as non-hazardous waste is a criminal offence enforceable by the Environment Agency.
Can coal tar road planings be recycled?
Coal tar-bound planings classified as hazardous waste under code 17 03 01* cannot generally be recycled as reclaimed asphalt pavement (RAP) in the same way as non-hazardous bitumen planings. Hazardous coal tar material must be sent to a permitted hazardous waste treatment or disposal facility. Some specialist facilities can process coal tar planings through thermal treatment to break down PAHs, but this is significantly more expensive than standard recycling. Non-hazardous bitumen planings, by contrast, can be recycled under PAS 108 and used in new road construction.
How many samples do I need for a coal tar testing programme?
The number of samples required depends on the size of the road surface, its construction history, and the degree of variability observed. WRAP guidance and industry best practice suggest a risk-based approach: larger, more complex, or historically uncertain surfaces require more samples. For small, uniform sites a single composite sample may be appropriate; for large highway resurfacing schemes, multiple composite samples from different zones and depths are advisable. The Testing Lab can advise on appropriate sampling strategies for specific project types.
How long does coal tar and PAH testing take?
Standard turnaround for PAH suite analysis (16 EPA PAHs by GC-MS) is typically 5–10 working days from receipt of samples at the laboratory. IP 346 DMSO extractables screening, used as a first-pass test, can often be completed more quickly. The Testing Lab offers rapid turnaround options for time-critical construction programmes — contractors should discuss programme requirements directly with the laboratory at the time of instruction.
What documentation do I need to keep for coal tar waste from road works?
Contractors must retain hazardous waste consignment notes for all movements of coal tar-classified planings, along with the laboratory results, chain-of-custody records, and waste transfer notes. The Environment Agency recommends retaining waste records for at least three years, and some contractual or planning conditions may specify longer retention periods. Written waste classification reports from an accredited laboratory provide the strongest evidence of due diligence in the event of a regulatory inquiry.