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How to Retain Stormwater On-Site Instead of Building Ever-Larger Pipes

Design guide to keeping stormwater on site with green infrastructure: drainage hierarchies, management trains, bioretention, permeable paving, sizing and maintenance.

The least expensive way to avoid ever-larger storm pipes is to produce less runoff in the first place. On-site retention uses a drainage hierarchy, bioretention and rain gardens, permeable pavement, vegetated channels and green roofs so rainfall infiltrates, evapotranspires or is reused close to where it falls. Design these systems early, along the site's natural drainage routes, and settle maintenance ownership before construction begins.

Key takeaways

  • The final destination of runoff is a decision ladder: reuse and infiltration outrank discharge to sewers, so a pipe should be a justified last step, not the default.
  • On-site features work best when planned at the earliest design stage, following natural drainage routes rather than being squeezed into leftover space after the layout is fixed.
  • A management train of several shallow, vegetated features in series outperforms a single oversized structure because each element manages volume, rate and water quality separately.
  • Infiltration is only reliable where field-tested soils are suitable and there is adequate clearance above groundwater; clay and contaminated sites need underdrains and overflows instead.
  • Green infrastructure quietly fails when it is not maintained; assign a named owner, a cleaning schedule and a budget for sediment removal before the design is approved.
  • Retrofitting existing sites is harder than designing new ones, so standards written for new development serve only as a starting point for upgrades.
  • Well-placed retention also cuts combined-sewer overflow frequency and filters pollutants, giving multiple benefits beyond flood control.

Why bigger pipes keep losing the argument

When roofs, roads and parking lots replace soil, rainfall stops soaking in and instead becomes fast, concentrated runoff. Pipe networks are sized from historical rainfall records and are expensive to enlarge, so more intense storms repeatedly push them past capacity, causing local flooding, streambank erosion and overflows from combined sewers that also carry sewage.

Green infrastructure attacks the same problem from the other side. As the U.S. EPA explains, low impact development manages wet-weather flows by infiltration, evapotranspiration or reuse of stormwater as close to its source as possible, using bioretention, rain gardens, vegetated rooftops, rain barrels and permeable pavement. Applied across a watershed it can maintain the natural movement of water and reduce the volume that ever reaches a collection system, slow its delivery so peak flows drop, and filter pollutants through soil and engineered media. On-site retention therefore tends to be the cheaper first step, not a last resort, and it can extend the useful life of the pipe system that remains.

Design to a drainage hierarchy, not a pipe size

The strongest way to keep pipes small is to decide runoff's destination through an explicit priority ladder. The UK national standards for sustainable drainage order final destinations as: first, collect runoff for non-potable use; second, infiltrate it to ground; third, discharge to an above-ground surface water body; fourth, to a surface water sewer; and fifth, to a combined sewer. Moving to a lower-priority destination requires evidence that every higher option has been used to the maximum extent practicable, and higher cost alone is not a valid reason to skip a better destination.

Two conditions make this honest rather than aspirational. Infiltration is only accepted where ground conditions are suitable, with an adequate measured infiltration rate and the base of the feature kept roughly a metre above the maximum likely groundwater level. Rainwater harvesting should be considered wherever there is a genuine demand for non-potable water, a need for landscape irrigation, or a seriously water-stressed location, and it should be sized against a rainfall time series rather than a rough guess. Work through the ladder in writing; the document trail is what protects you later when a regulator asks why water is still being piped away.

  • Priority 1: capture and reuse for non-potable purposes.
  • Priority 2: infiltrate into the ground where soils allow.
  • Priority 3: discharge to an open surface water body.
  • Priority 4: discharge to a surface water sewer.
  • Priority 5 (lowest): discharge to a combined sewer.

Build a management train, not a single monument

Authoritative design guidance consistently argues against concentrating on-site storage into one big structure. The UK standards promote a management train: a sequence of different drainage features operating close to the source of runoff, each contributing to flow control, volume reduction, water quality and opportunities for biodiversity and amenity. Conveyance should follow the natural drainage routes of the site, so that when rainfall exceeds the design event the exceedance flows travel along the same paths, can be captured further downstream, and stay away from buildings and people.

On a typical development the train might start where rain lands. Permeable paving handles parking aisles and light-use lanes, shallow vegetated swales carry water along the edges of roads, bioretention cells and rain gardens sit in medians and beside buildings, and downspout disconnection sends roof water to planted basins or cisterns. Green roofs detain water where it falls and return it to the air through evapotranspiration. Each element only needs to manage its share, which is why the sum is more robust than any single tank.

Choose and place on-site features by site conditions

Feature choice follows soil, slope and space. Rain gardens and bioretention basins are shallow planted depressions with filter media that handle the frequent, moderate rainfall events that create most runoff volume. Vegetated swales are shallow channels that slow flow and settle sediment as water passes. Permeable pavements let water move through the surface into an aggregate storage layer below. Green roofs and a well-designed urban tree canopy round out the toolkit, with trees intercepting rainfall and increasing evapotranspiration.

Site conditions decide what is realistic. Well-drained sands favor full infiltration; heavy clays have slow percolation, so basins tend to be shallower and wider or to rely on an underdrain and overflow. On steep slopes, water moves too quickly to soak in, so features must be placed carefully or stepped. The USGS review of green infrastructure in the Great Lakes notes that performance is strongly shaped by how facilities are maintained: basins with underdrains and permeable pavements can clog with sediment and lose their function if not cleaned, so a maintenance plan is part of the design, not an afterthought. EPA's own practice guidance counters the fears that these systems need large sites or fail on clay and in intense storms, provided they are adapted to those constraints.

Construct and maintain for the system's whole life

On-site retention systems are most fragile at the moment they are built. Construction guidance recommends stabilizing the upgradient drainage area first, using erosion and sediment controls so fines do not wash into the filter media, and keeping heavy equipment off the media to avoid compaction that destroys the infiltration rate you designed for.

Ownership is the second great risk. The UK national standards set detailed design and performance criteria for daily rainfall storage, flood risk, water quality, amenity, biodiversity and long-term maintenance, but policy observers note they do not firmly prescribe who adopts and maintains a shared multi-property scheme, leaving single-property systems the responsibility of the owner. Before any design is approved, name the party that will clean inlets, remove sediment, refresh vegetation, replace failed media and inspect after storms, and confirm the money exists to do it for the life of the development. A drainage feature that nobody maintains quietly becomes a liability that justifies the very pipe expansion you were trying to avoid.

Retention-first site audit checklist

Use this checklist before the site layout is frozen or whenever a drainage concept is proposed. Work through it in order and keep the written evidence, because regulators increasingly ask how higher-priority runoff destinations were considered.

  1. Confirm the design rainfall event and apply a reasonable allowance for future climate change before any layout decision.
  2. Map impervious catchments and the natural drainage routes water would follow on undeveloped ground.
  3. Run the destination ladder in writing: reuse, then infiltration, then surface water, then sewers, recording why each higher option was limited.
  4. Field-test the actual infiltration rate of the soil rather than assuming a value, and check the depth to seasonal groundwater.
  5. Verify the base of any infiltration feature is kept clear of the highest likely groundwater level.
  6. Add sediment pre-treatment, such as a filter strip or sump, ahead of infiltration media to delay clogging.
  7. Chain features into a management train so overflow from one element is captured by the next.
  8. Define a visible exceedance route for storms beyond the design event that directs water away from buildings.
  9. Provide an underdrain or overflow where clay soils or contamination prevent full infiltration.
  10. Assign the maintenance owner, an inspection schedule and a funded budget before sign-off.
  11. Protect filter media from compaction and sediment during construction.

Questions people ask

What is the difference between retention and detention?

Detention temporarily stores runoff and releases it slowly, which cuts peak flow rates but does not reduce the total volume that eventually reaches a sewer or waterway. Retention actually removes water from the runoff stream by letting it infiltrate into the ground, evaporate or be reused, so both the peak and the total volume shrink. Because many pipe and combined-sewer problems are driven by total volume, retention features that infiltrate or reuse water give the larger benefit, whereas a detention basin mainly buys time downstream.

Can on-site retention work on heavy clay soils?

Yes, but it has to be adapted. Slow-percolation clays cannot take the same volume through infiltration, so designers typically make bioretention basins shallower and wider, add an underdrain to release treated water slowly, or use an overflow for large events. EPA guidance specifically addresses clay soils and notes that careful planning helps low impact development work there. The key is to test the actual soil rather than assume, keep any infiltration base clear of groundwater, and size the underdrain so the surface drains within a day or two.

How much space does green infrastructure really need?

Far less than many people assume, because a management train spreads the work across many small features instead of demanding one big basin. EPA materials address the perception that low impact development requires large sites and document well-suited small-space options such as planter boxes, tree trenches and narrow bioretention strips along streets. A rough rule is that the more impervious area you have, the more of it you should convert to, or drain into, shallow planted and permeable surfaces, but exact sizing depends on the design storm, soil infiltration rate and catchment area feeding each feature.

Who should own and pay for the maintenance of an on-site drainage system?

The answer depends on ownership structure and jurisdiction, which is why it should be settled before design approval rather than after problems appear. For a single property, the owner is normally responsible, as the UK national standards state. For a system shared across many properties, an appropriate adopting body should take it on, but guidance has not always prescribed exactly who that is, so buyers and managers should check their local rules. Plan a funded schedule covering inlet cleaning, sediment removal, vegetation care, media replacement and post-storm inspection, because an unmaintained system slowly clogs and can fail to infiltrate at all.

Will retaining water on site flood basements or foundations?

It can, if you locate features carelessly or ignore groundwater. Keep infiltration features a safe distance down-gradient from buildings and foundations, and design so the base of any infiltration element stays well above the maximum likely groundwater level, roughly a metre in the UK standard. Route exceedance flows away from structures and toward capture areas downstream. Where the water table is high or the soil is very slow, an underdrain with an overflow outlet is safer than trying to force full infiltration next to a building.

How do I size a rain garden or bioretention basin?

Sizing starts with the impervious catchment feeding the feature and the design storm volume, then accounts for how much water infiltrates into the native soil below during the emptying period. You subtract infiltration from incoming runoff and divide the remaining storage by the available ponding depth to get surface area. Confirm the infiltration rate by a field test rather than a published guess, keep the base clear of groundwater, and provide an overflow for events larger than the design storm. Because local rainfall and soil differ widely, treat these as engineering inputs and check them against the applicable local standard.

Sources and further reading

Sources were checked when this page was generated. Confirm changing dates, rules and prices with the original publisher.

  1. Nonpoint Source: Urban Areas (Low Impact Development)U.S. Environmental Protection Agency
  2. Addressing Combined Sewer Overflows Using Green InfrastructureU.S. Environmental Protection Agency
  3. Green Infrastructure in the Great Lakes: Assessment of Performance, Barriers, and Unintended Consequences (Circular 1496)U.S. Geological Survey
  4. National standards for sustainable drainage systems (SuDS)UK Government (Defra)
  5. New national standards for sustainable drainage: The right words but missing a mandateChartered Institution of Water and Environmental Management (CIWEM)
  6. Методические рекомендации по организации водоотвода на улично-дорожной сети городов, не имеющих подземной (трубопроводной) ливневой канализацииФАУ «ФЦС» Минстроя России (публикация на meganorm.ru)