Comparisons

Land contamination phase 1 against phase 2

6 min readBy PlanScope Editorial Team

A phase 1 preliminary risk assessment is research and a walkover. Phase 2 is boreholes and laboratory analysis. The conceptual site model decides whether you need the second one.

The difference between phase 1 and phase 2 contamination work is simple to state and expensive to get wrong. Phase 1 is a desk based preliminary risk assessment that asks whether a credible pollutant linkage might exist on your site. Phase 2 is intrusive work, boreholes and trial pits and laboratory testing, that goes and finds out. You commission phase 2 only if phase 1 says you need to, and the document that carries the decision between them is the conceptual site model.

For a self-builder putting two houses on an old yard, that sequence is usually the difference between a £900 report and a ground investigation that reshapes the budget.

What the desk study actually does

A phase 1 preliminary risk assessment is research, a walkover and a judgement. The researcher assembles historic Ordnance Survey maps back to the 1870s, British Geological Survey mapping and any borehole records for the area, Environment Agency data on landfills, permitted processes and recorded pollution incidents, local authority records, coal mining and other mineral information where relevant, and radon and groundwater vulnerability data.

Then somebody walks the site. Photographs of a filled hollow, a dieback patch in the grass, a rusted tank behind a shed or a made ground exposure in a ditch bank do more for a report than another archive search.

The output is not a verdict on whether the land is contaminated. It is a statement of whether contamination is plausible given the history, the geology and the proposed end use, written up as a contaminated land assessment with a clear recommendation. Residential end use with private gardens is the most sensitive category in common use, which is why the same site can pass for a warehouse and fail for housing.

Everything turns on the pollutant linkage: a source, a pathway and a receptor, all three present and connected. No linkage, no risk in regulatory terms, however grim the site history sounds.

The conceptual site model is where those linkages are set out, and the way pollutant linkages work is worth understanding before you read either report. A phase 1 builds a preliminary model from documents. A phase 2 tests that model against physical evidence and then revises it, which is the part people forget: the model after the dig should look different from the model before it, or the dig told you nothing.

Getting the receptors right is where small schemes go wrong. Future residents and their vegetable plots are receptors. So are construction workers, buried services, building fabric, controlled waters and, on some sites, ecological receptors. A model that lists only "site users" will come back from the council's contaminated land officer with questions.

When phase 2 can be avoided

Plenty of sites stop at phase 1, and a well-argued phase 1 that says no further work is required is a legitimate outcome rather than a failure to sell more work.

That conclusion holds up where the history shows continuous agricultural or residential use with no infilling, the geology gives no gas generating strata or mine workings, there is no evidence of made ground, and the end use is no more sensitive than what is already there. It falls apart quickly on former petrol filling stations, garages, tanneries, gasworks, scrapyards, orchards with historic pesticide use, infilled ponds and quarries, and anywhere the maps show a works with no name.

Councils vary in how readily they accept a no-further-action phase 1, which is why what triggers the dig is worth checking against your authority's own approach before you assume the desk study closes the matter.

What the intrusive stage involves

Phase 2 is a site investigation designed to test specific hypotheses, carried out in accordance with BS 10175 and, for the geotechnical elements, BS 5930. A typical residential scheme involves some combination of machine-dug trial pits, window sample holes or cable percussive boreholes, soil samples taken at stated depths and sent for laboratory analysis, groundwater monitoring wells, and gas monitoring standpipes.

Ground gas is the element that controls programme. Carbon dioxide, methane and oxygen readings, with flow rates, have to be taken across a series of visits spread over weeks or months, deliberately including periods of falling atmospheric pressure when gas is most likely to be drawn out of the ground. You cannot compress that into a fortnight because a contractor wants to start.

The analytical results are then compared against generic assessment criteria for the proposed end use. Where the generic screening shows an exceedance that matters, the assessor moves to a detailed quantitative risk assessment with site specific parameters instead of defaulting straight to excavation.

This stage sits squarely in professional territory. Local planning authorities expect reports prepared by suitably qualified and experienced persons, and the Environment Agency's Land Contamination Risk Management guidance sets out the competence expectation. An AI-assisted draft can structure the narrative, marshal the policy references and flag what is missing, and a qualified contaminated land specialist then has to do the assessment and put their name to it. Where ground conditions rather than chemistry are the issue, a geotechnical assessment covers foundation design and is often commissioned from the same rig visit.

Remediation, verification and discharging the condition

Most contaminated land conditions come in four linked parts, and reading them in order tells you where you are:

  1. Submit a preliminary risk assessment (the phase 1).
  2. Where that identifies potential linkages, submit a site investigation and risk assessment (the phase 2).
  3. Where that confirms unacceptable risk, submit a remediation scheme for approval.
  4. On completion, submit a verification report demonstrating the scheme was carried out.

A fifth clause usually deals with unexpected contamination found during works, requiring you to stop and report it. That clause is not decoration. Discovering something unrecorded and carrying on is how a development ends up in a Part IIA conversation under the Environmental Protection Act 1990, which is a slower and less friendly regime than planning.

Remediation on small residential sites is often simple: dig out a hotspot and dispose of it, or place a clean cover system of specified depth over garden areas with a marker layer beneath. Gas protection measures to BS 8485 are designed against the characteristic situation derived from the monitoring. Verification is the step people underestimate, because it needs photographs, validation sampling, waste transfer documentation and imported material testing collected as the work happens rather than reconstructed afterwards.

Cost and programme

Phase 1 is a research and reporting exercise, so it is measured in days and the fee reflects that. Phase 2 involves mobilising plant, utility clearance, traffic management on some sites, laboratory schedules and repeat monitoring visits, so it costs a multiple of the desk study and takes weeks rather than days. Gas monitoring can add months on its own.

The planning consequence is about ordering. Commission the phase 1 at feasibility stage, before you buy the land if you can, because it is the least costly piece of due diligence available on a former commercial plot. Where a council has imposed a condition that must be discharged before work starts, budget the phase 2 into the pre-start programme rather than the construction programme, and allow for the possibility that the remediation scheme needs approving before anything moves.

This is general guidance, not legal advice; check the position with your local planning authority or a qualified professional before relying on it. For specialist technical reports, qualified professional input may be required.

PlanScope provides AI-assisted draft reports for planning applications. Reports should be reviewed before submission. We do not guarantee planning approval. If you want to check which reports a former industrial plot is likely to need, enter your postcode on PlanScope.

Frequently asked questions

Do I always need a phase 2 after a phase 1?

No. Where the desk study finds no plausible pollutant linkage, because the site has a continuous agricultural or residential history, no made ground, no gas generating strata and no more sensitive end use, a phase 1 recommending no further work is a legitimate outcome. Councils differ in how readily they accept that, so check your authority's approach early.

What standard governs a phase 2 site investigation?

BS 10175 is the code of practice for the investigation of potentially contaminated sites, with BS 5930 covering site investigation practice more generally. Ground gas work draws on BS 8576 and CIRIA guidance, and gas protection design for new buildings follows BS 8485. The Environment Agency's Land Contamination Risk Management guidance sets the overall framework.

How long does ground gas monitoring take?

Longer than most programmes allow for. Readings have to be taken over a series of visits spread across weeks or months, deliberately including periods of falling atmospheric pressure when gas is more likely to migrate. The number of visits depends on the risk category and the ground conditions, and it cannot be compressed to suit a build start date.

Who can write a contaminated land report?

A suitably qualified and experienced person. Local planning authorities and the Environment Agency both expect assessments to come from specialists with relevant competence, and a report signed by someone without it is likely to be rejected at discharge of conditions stage. An AI-assisted draft can organise the structure and flag missing data for that specialist to complete.

What is a verification report?

It is the document that proves the approved remediation was actually carried out. It collects photographs, validation sampling results, waste transfer notes, testing certificates for imported material and records of gas membrane installation. Because the evidence has to be gathered while the work happens, the verification requirements should be read before remediation starts, not afterwards.

Sources and further reading

contaminated landphase 1 desk studyphase 2 investigationbs 10175ground gasconditions

This article is general guidance about the planning system in England and, where stated, the rest of the UK. It is not legal or professional advice. Check your local planning authority’s validation requirements and take professional advice for your specific site.

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