Anthony-JohnsonConsulting Engineer Ltd

The Designer’s problems

Short articles on the questions that decide whether a design works in the ground, not just on paper. Written for homeowners, self-builders and architects who want to know why we ask for what we ask for. Choose a problem below.

Technical words like infiltration rate have a dotted underline: hover over or tap them for a plain-English meaning.

Drainage

Percolation tests and soakaways: the right test, the right season, the right depth

A soakaway is only as good as the number it was sized from. Get the test wrong, test in the wrong month, or ignore the groundwater, and a soakaway that passed on paper can sit full of water for most of the winter.

1

Three tests, and how much ground each one sees

“Percolation test” is used loosely for several procedures that look alike on site: dig a hole, fill it with water, time how long it takes to drain. They differ in how big the hole is, how deep it goes and how the result is used, and those differences decide how far the answer can be trusted.

The Building Regulations test. Approved Document H prescribes one simple percolation test, and it is precise about where the hole goes: 300 mm square, with its base 300 mm below the invert of the incoming pipe. The hole is soaked overnight, refilled and timed as the water falls from 75% to 25% full, giving a percolation value, Vp, in seconds per millimetre. Under H2 that decides whether the ground can take treated effluent through a drainage field, acceptable where Vp falls between 15 and 100 s/mm. Under H3 the same test is used for rainwater soakaways: Vp is converted to an infiltration rate to size soakaways serving small areas, with larger areas referred to BRE 365 or BS EN 752.

Followed to the letter, the test samples the ground just below the pipe, which is right for a shallow drainage field but not for a soakaway whose base may be a metre or more deeper. Some builders, sensibly, dig a trial pit to the depth of the proposed soakaway and form the 300 mm test hole in its base. That gives a reading much closer to the ground the soakaway will actually sit in, and it is good practice. Even so, the test still wets only a 300 mm cube of ground.

BRE 365. The standard method for surface water soakaways. A trial pit is dug to the depth of the proposed soakaway, filled quickly, timed from 75% to 25% full, and filled twice more, ideally on the same or consecutive days. The slowest of the three runs is used, not the average, and it is expressed as an infiltration rate in metres per second, which feeds straight into the storage calculation.

The SuDS approach. The CIRIA SuDS Manual (C753), enforced by Lead Local Flood Authorities, builds on BRE 365. It asks for the test at the location, depth and head of water of the real device, applies a factor of safety to the measured rate (higher where failure would flood buildings), and sets limits such as a minimum workable infiltration rate and a minimum depth above groundwater.

Three ways of testing the same Fen site. A: the Building Regulations hole dug as prescribed, 300 mm below the pipe, sits in free-draining sandy silt. B: the same 300 mm hole formed in the base of a trial pit at soakaway depth lands in a sandy pocket and still drains quickly. Two metres away the proposed soakaway cuts through a finer silt and clay lens and sits in silty clay. C: a BRE 365 trial pit dug to the full soakaway depth wets all of these layers and gives the slower, true result. Ground level Pipe invert Sandy silt Silty clay Finer silt / clay lens Proposed soakaway 75% 25% A B C As prescribed Hole at pit base BRE 365 pit about 2 m apart
Same site, three tests. A, the hole as prescribed, samples only the sandy silt below the pipe. B, the same hole in the base of a trial pit, is closer to the real depth but lands in a sandy pocket. Two metres away the soakaway cuts through a finer silt and clay lens and sits in silty clay. C, a BRE 365 pit to full depth, wets all of it, and its slowest run reflects the slower ground.
TestUsed forWhat it samples
Building Regulations (Approved Document H2 and H3)Foul drainage fields; small rainwater soakawaysA 300 mm cube: just below the pipe as prescribed, or at the base of a deeper trial pit
BRE 365Surface water soakawaysThe full soakaway depth; slowest of three fills, in m/s
SuDS Manual (C753)Infiltration SuDS for planningAs BRE 365, reduced by a factor of safety
2

How the wrong test produces a soakaway that cannot cope

Ground is rarely the same all the way down, or all the way across. A sandy or silty layer just under the topsoil can drain freely while a clay or silt band a metre lower, or a lens of finer silt a couple of metres away, barely drains at all. A soakaway only works as well as the ground around its sides and base, so the test has to sample that ground.

The Building Regulations test is not wrong, and it is not meant to be the last word. It is a prescribed minimum, and its result is only as representative as the small cube of ground it is dug in. Taken as written, with the hole just below the pipe, it tests only the upper layer. If that layer is the free-draining one, the test passes comfortably while the base of a deep crate soakaway sits in a slower band the hole never reached.

Moving the hole to the base of a trial pit at soakaway depth helps, but in variable ground such as the Fens it can still miss what matters. Silts and clays change over a few metres sideways as well as downwards: a sandy pocket at the bottom of one pit, a finer-grained silt or clay lens beside the soakaway two metres away. A 300 mm hole does not see reduced permeability in the ground next to it, however carefully it is placed. A BRE 365 pit, dug to the full depth and filled over its whole face, does, because the water has to leave through every layer the soakaway will.

How the test is run matters too. Averaging results, or timing a first fill into dry ground, gives a rate the ground cannot keep up once it is wet. BRE 365 deliberately repeats the fill and takes the slowest run for exactly this reason: the third fill into saturated ground is usually the honest one.

Because the storage volume of a soakaway depends directly on the rate it can empty, an optimistic rate gives an undersized soakaway. If the rate used is several times faster than the real one, the soakaway fills during the storm, surcharges back up the pipes and spills across the garden or against the building. Worse, it may not drain down before the next rain, so it starts each storm part full.

Signs a soakaway was sized from the wrong test

Gullies or downpipes that back up during heavy rain, while the soakaway is still full a day later.

Standing water over the soakaway in winter, even after light rain.

A deep crate soakaway sized from a single 300 mm hole, wherever it was dug, or from an averaged result.

3

Why the test should be done in late winter

Ground behaves very differently through the year. Over autumn and winter, rain soaks down and refills the groundwater, a process called recharge. By late winter, typically February and March, the soil is at its wettest and the groundwater table is at or near its highest.

That is the condition a soakaway has to work in, because long, wet winter spells are when it is most likely to be called on repeatedly with no time to dry out. A test dug in August into dry, cracked ground can drain spectacularly fast and look like an excellent result. The same pit in March may drain at a fraction of the rate, or fill from below with groundwater before any water is added.

A late-winter test gives the worst realistic case, and that is the one to design for. It also lets whoever digs the pit see and record the groundwater level directly, which a summer test cannot do. That record is one of the first things we ask for when designing from the results.

If a test has to be done in summer

Treat the result with suspicion. Expect the authority to ask for a repeat in winter, or for groundwater monitoring through the wet season, before the design is accepted.

4

The metre that matters: depth to groundwater

Water can only soak away into ground that has room for it. Below the groundwater table every pore is already full, so a soakaway sitting in groundwater has nowhere to send its water. It simply fills and stays full.

For that reason SuDS guidance, and many Lead Local Flood Authorities, require at least 1 metre of unsaturated ground between the base of the soakaway and the highest seasonal groundwater level. That metre does three jobs. It gives the water somewhere to go. It stops groundwater rising into the soakaway and taking up its storage. And it filters the runoff through soil before it reaches the groundwater, which protects water quality.

This is why the depth measured in late winter is so important. A summer reading can suggest two metres of clearance when the winter peak leaves almost none. In low-lying parts of the region, including the Fens, the winter water table can sit within a metre or so of the surface, and a conventional deep soakaway is often simply not possible. A shallow, wide design or a different drainage route is then needed.

Section through a soakaway. The late-winter groundwater level sits far higher than the summer level. The base of the soakaway must stay at least 1 metre above the late-winter level. A dashed line shows a possible higher future winter level that eats into that clearance. Ground level Soakaway From roof Summer groundwater Late-winter groundwater (highest) Future winter peak? At least 1 m unsaturated ground
Clearance is measured to the late-winter peak, not to the summer level. Any future rise in winter groundwater comes straight off that clearance.
5

From 20% to 30% to 40%: why rainfall is uplifted

A warmer atmosphere holds more moisture, so the heaviest bursts of rain are becoming more intense. Drainage is designed from historical storm records, so an allowance is added on top to cover the change over the life of the development. That allowance has been revised upwards twice as the climate science has improved.

2006 to 2016: 20% or 30%. National planning guidance (PPS25, carried into the 2012 technical guidance to the NPPF) set the uplift by how long the development would stand. Peak rainfall was increased by 20% for the period to 2085 and by 30% for 2085 to 2115. Housing, expected to last a century, was normally designed to the 1 in 100 year storm plus 30%. A building with a shorter life could justify 20%.

2016: a choice between 20% and 40%. In February 2016 the Environment Agency replaced those figures with a range instead of a single number: a central allowance of 20% and an upper end allowance of 40% for the 2070 to 2115 period. Flood risk assessments had to test both, but the guidance left the design figure to be agreed with the local authority. Many Lead Local Flood Authorities required 40% for drainage. Others accepted 20% with justification, for example a shorter design life, a less vulnerable use, low consequences if the system was exceeded, or the cost of the extra storage on a marginal scheme.

2022 onwards: 40% by catchment. In May 2022 the allowances were recalculated for each river management catchment using the Met Office’s high-resolution projections. Development with a lifetime beyond 2100, which includes all housing, must now be checked against the upper end allowance for the 2070s for the 1% annual exceedance probability storm. For the Cam and Ely Ouse catchment, which covers much of our area, that is 40%. Lower central figures still apply to development with a shorter design life, which is why commercial and temporary buildings can legitimately use a smaller uplift.

There is one more reason the lower figures survived for so long. Lead Local Flood Authorities are statutory consultees only on major development. A single house or an extension is approved by Building Control against Approved Document H, which has no climate change allowance of its own, so for years many small soakaways were sized to past rainfall with no uplift at all.

The effect on storage is direct. A soakaway stores the difference between what flows in and what soaks away. On slow-draining ground almost all of the storm has to be stored, so 40% more rain needs roughly 40% more storage. A soakaway built to past rainfall holds only around 70% of today’s design storm, and one built to the 20% figure around 85%. In practice the storm that used to be the one-in-a-hundred-year event now overtops them more often. The water backs up through gullies, ponds on drives and patios, or runs onto a neighbour’s land, and owners are left wondering why a soakaway that worked for years has started to fail.

Storage on slow-draining ground, in proportion, for the same 1 in 100 year storm. Every soakaway sized to an older figure is now short of today’s design storm.
GuidanceUplift for housingWhy a lower figure was possible
PPS25 / NPPF technical guidance, 2006 to 201630% (to 2115)20% for a design life ending before 2085
Environment Agency, Feb 201620% central or 40% upper endChoice agreed with the authority; central accepted with justification
Environment Agency, May 202240% upper end (Cam and Ely Ouse)Central figures only for shorter-life development
6

Is climate change raising groundwater under our soakaways?

The evidence points that way, with honest caveats. UK climate projections show milder, wetter winters and hotter, drier summers. More of the year’s rain is expected to fall in winter, when it recharges groundwater, and recharge may be squeezed into a shorter, more intense season. Both favour faster rises and higher winter peaks.

A review of UK groundwater research by Jackson, Bloomfield and Mackay (2015) found that, under a high emissions scenario, the median of the modelled projections showed higher average winter groundwater levels by the 2050s at most sites, alongside lower summer levels. The same review found no clear trend in the historical records yet, and stressed that local geology controls how each site responds. Near the coast and estuaries, projected sea level rise of 0.4 to 1 metre by 2100 adds a further push upwards on groundwater.

For a soakaway, the consequence is direct. The 1 metre of clearance measured when it was designed is not guaranteed for its lifetime. If the winter peak climbs, the unsaturated zone thins, the ground around the soakaway is wetter when the heavy rain arrives, and the infiltration rate falls just when it is needed most. A soakaway that discharged at a perfectly good rate twenty years ago can start to hold water through the winter without anything about the soakaway itself having changed.

That is why we advise testing in late winter, keep a generous margin above the groundwater, and design storage with the climate uplift in it. Where the ground or the water table will not support a soakaway, it is better to say so at the start and design an alternative, such as attenuation with a controlled discharge, than to build something that is full before the rain stops.

What this means for your project

Book the infiltration test for late winter where the programme allows. We can advise on how and where to dig it.

Use a BRE 365 test at the real soakaway depth, three fills, slowest result.

Record the groundwater level in the pit and keep at least 1 m below the base.

Size storage with the 40% climate uplift, and check what happens when it is exceeded.

7

The caveats

Everything above concerns rainwater. Homes with no mains sewer also have foul water to deal with, and here what is accepted on site does not always match the rules.

A treatment plant to a soakaway. A package treatment plant serving a typical four-bedroom house discharges around 0.75 m³ of treated effluent a day, every day of the year. The Building Regulations and the Environment Agency expect that effluent to go to ground through a drainage field designed to BS 6297 and sized from the H2 percolation test. For a four-bedroom house that field typically takes up an area of around 6 m × 6 m. On a tight plot there may simply be no room for it, and some local authority building control departments will then accept the plant discharging into a soakaway instead.

It looks like a sensible compromise, but the two are not the same. Effluent from a treatment plant is cleaner, not clean: it still carries bacteria, nutrients and some organic matter. A drainage field is laid shallow, within the topsoil and upper subsoil where oxygen and soil bacteria are plentiful, and as the effluent trickles through that living layer it receives its final, tertiary stage of treatment. A soakaway is set deeper, below the organic topsoil, and releases the effluent in one place into ground with far less biological activity and much closer to the groundwater. The tertiary treatment never happens.

There is a regulatory catch too. The Environment Agency’s general binding rules for small sewage discharges to ground require a drainage field, and they exclude soakaways designed for rainwater that were installed after December 2007, as well as boreholes and similar deep structures. A building control approval does not override those rules. A system that breaks them needs an environmental permit, and the Agency will not grant one where effluent can reach groundwater directly. That is worth knowing before buying a house, as well as before building one.

When the land will not take it. Where the ground fails the percolation test, or the winter water table is too high, the water has to go somewhere other than into the ground. For treated effluent the next option is usually a watercourse that flows all year, often after further polishing through a reed bed, and it needs the Environment Agency’s rules or a permit to be met. For surface water, attenuation ponds and basins hold the storm and release it slowly to a ditch or stream at an agreed rate. Both need land, consent from the Environment Agency or the internal drainage board, and a watercourse to discharge to.

The hierarchy. A connection to the public sewer is the last resort for surface water. Defra’s National Standards for Sustainable Drainage (2025) and Anglian Water’s own surface water policy set the same order, shown alongside. Anglian Water asks for sufficient evidence that every disposal route above a sewer has been explored, which in practice means BRE 365 infiltration results and an investigation of nearby watercourses. It accepts surface water into a combined sewer only in exceptional circumstances, says it will seek to separate surface water from any new development, and limits new connections to the equivalent greenfield runoff rate, with storage on site for the 1 in 100 year storm plus climate change.

Foul water runs the other way. Anglian Water and the Environment Agency’s joint advice (2020) starts from a presumption that new development connects to the public foul sewer. A package treatment plant is considered only where a connection is shown not to be feasible on cost or practicality, and a septic tank only after that, and only on suitably permeable ground. The planning application has to justify the choice, normally on a foul drainage assessment form (FDA1). The general binding rules add that a connection is expected where a public foul sewer is within 30 m of the property boundary.

Why the order matters. In many older towns and villages foul water and rainwater share a single combined sewer. In heavy rain the rainwater fills those pipes, and storm overflows release the mix of rainwater and sewage into rivers to stop it backing up into homes and streets. Every roof and drive connected to a combined sewer adds to that storm flow. That is how untreated sewage reaches our rivers in wet weather, and it is the real reason the hierarchy exists. A soakaway that works, tested properly and sized for the climate it will face, is worth far more than a pipe to the nearest manhole.

Comparison of a shallow drainage field spreading effluent through the topsoil and a deeper soakaway releasing it in one place below the topsoil, closer to groundwater. Ground level Base of organic topsoil Groundwater Drainage field shallow trenches spread effluent through the topsoil, where bacteria complete treatment Soakaway released in one place, below the topsoil, near groundwater
Where the effluent goes. A drainage field spreads it through the living topsoil, where bacteria finish the treatment. A soakaway releases it in one place, below that layer and nearer the groundwater.

Surface water hierarchy (Defra 2025; Anglian Water)

  1. Collect and reuse (rainwater harvesting)
  2. Infiltrate to ground (soakaways, permeable paving)
  3. Discharge to a watercourse or surface water body
  4. Discharge to a surface water sewer
  5. Discharge to a combined sewer, as a last resort

Each step down has to be justified with evidence. Anglian Water allows a combined sewer connection only in exceptional circumstances.

Foul water hierarchy (Anglian Water and Environment Agency, 2020)

  1. Connect to the public foul sewer
  2. Package treatment plant, where a connection is not feasible
  3. Septic tank, only on suitably permeable ground

Sources

  1. BRE Digest 365, Soakaway design (2016), test procedure as summarised by West Devon Borough Council.
  2. Building Regulations percolation test for rainwater soakaways under H3, small areas and conversion of Vp to an infiltration rate: Copeland Borough Council, Percolation tests for soakaways.
  3. Approved Document H2 / BS 6297 drainage field percolation test and the 15 to 100 s/mm range: Unda, BS 6297 infiltration testing; Stratford-on-Avon District Council.
  4. CIRIA C753 The SuDS Manual; infiltration requirements including 1 m above highest groundwater: Essex Design Guide, Infiltration.
  5. Environment Agency, Flood risk assessments: climate change allowances (peak rainfall updated May 2022).
  6. 2016 allowances (20% central, 40% upper end) and the previous 30% requirement: Hertfordshire County Council, climate change allowances note; susdrain briefing note.
  7. Upper end peak rainfall allowances by catchment, including 40% for the Cam and Ely Ouse: Essex Design Guide, Climate change.
  8. Jackson, C. R., Bloomfield, J. P. and Mackay, J. D. (2015), Evidence for changes in historic and future groundwater levels in the UK, Progress in Physical Geography 39(1).
  9. GeoSmart, Groundwater flooding and climate change, summarising UKCP18, BGS recharge modelling and Environment Agency sea level projections.
  10. Environment Agency, General binding rules: small sewage discharge to the ground.
  11. Defra National Standards for Sustainable Drainage Systems (2025), discharge hierarchy as summarised by Unda, The SuDS hierarchy explained; Approved Document H order of priority as summarised by Eden District Council.
  12. Environment Agency, Combined sewer overflows explained (2020).
  13. Anglian Water, Surface water drainage policy.
  14. Anglian Water and Environment Agency, Non-mains sewerage advice note to local planning authorities (November 2020).

Need a soakaway designed?

We advise on how and where to carry out BRE 365 infiltration testing, then use the results to design soakaways and SuDS to current climate allowances across Norfolk, Cambridgeshire, Lincolnshire, Suffolk and Peterborough.

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