Rainwater

Sizing a Rainwater Harvesting Tank: Bounded by the Roof at One End and the WCs at the Other

Eighteen days of the smaller of annual yield and annual demand. On a 74 m² roof that is under 2,000 litres, and the 6,000 in the brochure is a fault.
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A Number Is Wanted by Friday, and the Machine Comes on Monday

The groundworks package is out to price and the tank line is still blank. Everything downstream of it is waiting: the depth and plan size of the excavation, whether the hole needs a concrete surround, whether the dig clashes with the incoming service and the soakaway, how much muck goes off site, and whether the crane hire covers a shell of that diameter. None of that prices from a range. It needs one figure, defensible in a design statement afterwards.

What comes back from a supplier's sizing page, asked the same question, tends to be generous. Enter four bedrooms and a roof and you are offered six thousand litres; enter a school and the suggestion has five digits in it. Generosity is the wrong instinct, and not because a bigger shell costs more. Past a certain volume the extra litres never carry water, because the roof cannot refill them inside a year — and the water that does sit in them sits for months rather than weeks, which is a quality problem, a cleaning problem and, on anything that ends up aerosolised, a risk-assessment problem.

So the specification has two ends. The floor is set by how long the building has to run without rain and by how much of the vessel you can actually draw from. The ceiling is set by what the roof yields in a year and by what happens to water that stays too long. Almost every real answer is pinned against the ceiling, which is why sizing a harvesting tank feels so unlike sizing a hot water cylinder: the arithmetic is not looking for the largest justifiable number, it is looking for the smallest of several.

About Five Per Cent of the Smaller of the Two: Eighteen Days

BS 8515, Rainwater harvesting systems — Code of practice, set out the whole shape of the answer in its intermediate approach: take five per cent of the annual rainwater yield, take five per cent of the annual non-potable demand, and use whichever is the lesser. Five per cent of a year is 18.25 days, so the rule reads the other way round as about eighteen days of the smaller of the two flows; this page works to eighteen whole days, 4.93 per cent of a year, as the site's Rainwater Tank and Cistern Size Calculator does. The rule was written for UK rainfall, which falls fairly evenly through the year, so where the dry season is long the store has longer to carry the building. BS 8515 was withdrawn in 2018 and replaced by BS EN 16941-1, On-site non-potable water systems — Part 1: Systems for the use of rainwater, now in its 2024 edition; BRE's BREEAM guidance gives the new standard's basic approach as the equivalent of BS 8515's intermediate one, and its detailed approach as described in the same way. That detailed route is a daily time-series model that runs the local rainfall record against the building's consumption day by day and reports how often the store empties. Almost nothing domestic is sized that way, and almost nothing needs to be.

The word doing the work is lesser. It is what makes this a bounded problem rather than an open one, and it is the part that gets dropped when a sizing tool asks only about the building and never about the roof. If yield is the smaller number, storage beyond eighteen days of it holds water the sky will not replace. If demand is the smaller number, storage beyond eighteen days of it holds water the building will not use. Either way the surplus is not a reserve, it is residence time.

Residence time is the honest way to talk about oversizing, because it converts a vague unease about stagnation into a number anyone can check. Divide the store by the volume actually turned over each day — which is the smaller of yield and demand, not the tank — and you get the average age of the water in it. A store sized at eighteen days of throughput turns over about twenty times a year and the water in it is a fortnight or so old. Triple that store and the turnover falls to under seven, the mean age climbs to nearly eight weeks, and the biofilm and sediment that BS 8515's screening, calmed inlet and inspection regime exist to manage now have a season to develop rather than a fortnight. Where any of the stored water is later sprayed or misted — a hose reel, a pressure washer, a vehicle wash — the governing document stops being the harvesting standard and becomes the HSE Approved Code of Practice L8, Legionnaires' disease: The control of legionella bacteria in water systems, with the technical detail in HSG274 Part 2; long residence time in a warm buried vessel is what those documents ask you to design out.

The school below shows how far apart the candidate answers can be. Three methods, one building, and a factor of four and a half between the smallest and the largest — with the largest being the one a client asked for by name, because a month of autonomy sounds like prudence.

Only one of those three rows is defensible in a design statement, and it is the smallest. The month-of-autonomy figure is the expensive mistake; the annual-demand row is the subtle one, because the arithmetic around it looks impeccable. Spreading 190 days of school demand across 365 nearly halves the apparent daily draw, so the defensible 27,800-litre store appears to buy almost thirteen days of cover when in term time it buys under seven — and sizing on that diluted draw asks for 38,800 litres instead, more than the roof can keep full. Nothing is wrong with the arithmetic except the denominator and the flow it was applied to.

One 1,150 m² school block, three sizing methods — 563,500 L of annual yield against 786,600 L of term-time demand
BasisTank it producesWhat it actually buysVerdict
18 days of annual yield (about 5%, the lesser of the two)27,800 L6.7 days of term-time demand; turns over about 20 times a yearThe defensible answer — yield is the binding constraint here
18 days of annual demand, spread over 365 days38,800 LAppears to buy 18 days; buys 9.4 in term time, and the roof cannot keep it fullWrong twice: demand is not the lesser, and a school draws its year in 190 days, not 365
'We want a month of autonomy'124,200 LA hole four and a half times the size, water about eleven and a half weeks old, 26 hours to emptyNot a specification, a request — and one the roof cannot honour
One 1,150 m² school block, three sizing methods — 563,500 L of annual yield against 786,600 L of term-time demand

A Year Off the Roof, Not a Storm Off It

Yield here is an annual figure, which makes it a different calculation from the one that answers what a downpour puts in a butt. Three numbers produce it: the plan area of every roof plane routed to the tank, the long-term annual rainfall at the site, and a pair of coefficients that account for what never arrives. The plan area is the flat footprint and not the tiled surface, for the reason rain falls vertically — the roof harvesting guide derives that, along with the millimetre-to-litre identity, and there is no sense in laying it out twice.

Take the rainfall from a record rather than from memory: the Met Office UK Climate Averages for the nearest long-running station, or the NOAA National Centers for Environmental Information 1991–2020 U.S. Climate Normals. Seven hundred millimetres is used below as an example, not a default: the same roof in Cumbria and in Essex differs by a factor approaching two, and the tank with it. Then apply the two reductions the calculation names: a yield coefficient on the catchment, for what the roof surface and the gutters lose, and a hydraulic filter efficiency, for what the filter turns away. Approved Document G works its rainwater figure by BS 8515's intermediate approach, takes the two together and gives 0.7 as its example — seven-tenths of gross — and that is the figure used below, the same one the site's Rainwater Tank and Cistern Size Calculator opens on. Where the filter's maker publishes an efficiency for your filter, use it rather than this sentence.

The house first. Seventy-four square metres of roof plan routed to one buried tank, at 700 mm, is 51,800 litres gross and 36,260 net. The school block: 1,150 square metres of plan area, same rainfall, 805,000 litres gross and 563,500 net. Neither figure is the tank. Both are the ceiling the tank has to sit under, and the second half of the arithmetic is what the building would drink if it could.

This returns a single event rather than a year. For the year in one step, with the share lost before the tank already taken off, use the Rainwater Tank and Cistern Size Calculator; this one still gets there as a slice: put the plan area in with a rainfall depth of 100 mm, or 1 in on the imperial switch, then scale the answer to the site's annual rainfall — 700 mm is seven 100 mm slices, or 27.6 one-inch ones. One working note: the result is gross, since it assumes everything landing is collected, so take your yield coefficient and filter efficiency off it before the figure goes near a tank schedule.

The horizontal (footprint) area of roof draining to the collection point.

The rainfall depth for the event you're estimating.

Estimated water collected

673 gallons

Medium confidence

This assumes 100% collection efficiency — actual yield is somewhat lower due to evaporation, first-flush diversion (recommended to skip the initial dirty runoff), gutter overflow in heavy rain, and roof surface losses.

Roof catchment area
1,080 sq ft

Estimated cost — your price

This site holds no price list for this material — local prices vary too much to publish honestly. Enter your supplier's price and the result is costed with it.

What this calculation does not cover

  • The figure is gross catchment. No runoff or yield coefficient is applied, nothing is subtracted for the depth the roof surface and gutter absorb before runoff even starts, and evaporation and any volume sent to a first-flush diverter are not deducted. The water that actually reaches the barrel is meaningfully less than this.
  • The calculation does not know your storage volume. It reports what falls on the roof, not what you keep — once the barrel is full the rest leaves through the overflow, so for anything beyond a small event this number is larger than the water you end up with.
  • Rainfall is entered as a total depth with no duration, so intensity never enters the arithmetic. Whether the gutter, downspout and diverter can carry the peak rate is a separate sizing problem, and water that overshoots an undersized eaves gutter is lost before the barrel sees it.
  • This is a single event, not a supply. There is no seasonal distribution and no dry-spell interval behind it, so it cannot size a cistern or tell you whether the store will still hold water when you need to draw on it.
  • This is not a water-quality or compliance assessment. It says nothing about what the roof covering leaches into the runoff, nothing about treatment for any use beyond irrigation, and nothing about local rules — some jurisdictions restrict or require registration of rainwater capture, and any tie-in to household plumbing brings backflow prevention and cross-connection requirements with it. Confirm both locally.

The Demand Is Flushes, and a School's Year Is 190 Days Long

Non-potable demand in a building is dominated by WCs and urinals to an extent that surprises people who have only ever thought about the garden. Everything else on the list — washing machine, outside tap, floor washing — is real but secondary, and irrigation is seasonal in a way that makes it a poor basis for a tank that has to earn its excavation in February. Size the store on the flushing and treat the rest as what fills the margin.

The flush volume itself is one of the few figures on this page that is fixed by law rather than by habit, which is what makes the demand side tractable. In England and Wales the Water Supply (Water Fittings) Regulations 1999 cap a WC installed since 2001 at a six-litre flush, with dual-flush cisterns rated at that full flush and a shorter one below it; a mixed-use average of 4.5 to 5.5 litres is a reasonable working figure for a modern installation. In the United States the Energy Policy Act of 1992 fixed 1.6 gallons per flush for tank-type toilets manufactured from 1994, and the EPA WaterSense Specification for Tank-Type Toilets sets 1.28. Where the building is a new dwelling, Approved Document G of the Building Regulations for England and its companion methodology, The Water Efficiency Calculator for New Dwellings, give both the whole-house consumption target of 125 litres per person per day and the fixture-by-fixture method behind it — which is a better starting point for a house than any rule of thumb.

For the house, then: four people, five flushes each per day at an average 5.5 litres, is 110 litres a day and 40,150 a year. A washing machine at four cycles a week adds roughly 10,400 at the 50 litres a cycle used here as a placeholder, and the machine's own energy label carries a litres-per-hundred-cycles figure that should replace it. Total non-potable demand about 50,600 litres against a yield of 36,260, so on this house yield is the lesser and the tank is eighteen days of it — 36,260 × 18 ÷ 365, or 1,788 litres. In a catalogue of moulded shells that means the 2,000 or the 2,700, and emphatically not the 6,000 the brochure's family-home page offers, which the roof would refill six times a year instead of twenty.

For the school, the household average is no use and the standards say so: BS 8515 and BS EN 16941-1 both expect non-domestic demand to be built from the building's own fixture schedule and occupancy pattern, with CIBSE Guide G, Public Health and Plumbing Engineering, the usual source for per-occupant benchmarks in the UK. This page will not publish a per-pupil figure it cannot cite, so the worked example uses a labelled assumption instead: 460 occupants at two flushes each per school day, at a 4.5-litre average across WCs and controlled urinals, is 4,140 litres a day. Multiply by 190 school days — not 365 — and the year is 786,600 litres. That is more than the roof yields, so once again the yield governs, and the tank is eighteen days of 563,500 litres: 27,800 litres. Replace the two-flush assumption with a survey and the demand moves; it will not change which of the two numbers is the lesser, because the roof would have to grow by two-fifths before it did.

The two buildings side by side, from roof plan to tank, at 700 mm a year and Approved Document G's combined 0.7 for the yield coefficient and filter efficiency
House, 4 occupantsSchool block, 460 occupants
Roof plan area routed to the tank74 m²1,150 m²
Gross annual rainfall on it51,800 L805,000 L
Net of yield coefficient and filter efficiency36,260 L563,500 L
Days the building actually draws365190 (term time)
Non-potable demand per drawing day139 L4,140 L
Annual non-potable demand50,600 L786,600 L
The lesser of yield and demandYield, 36,260 LYield, 563,500 L
Tank at 18 days of it1,788 L27,800 L
Autonomy that buys, on a drawing day12.9 days6.7 days
The two buildings side by side, from roof plan to tank, at 700 mm a year and Approved Document G's combined 0.7 for the yield coefficient and filter efficiency

Built to price a fixture swap, so it reports the difference between two flush volumes — which is exactly the arithmetic you need if you drive it deliberately. To read total WC demand rather than a saving, put the real flush volume in the current field and the smallest figure the new field accepts, 0.1 L, in the other; the 'water saved per year' line in the breakdown is then the annual flushing volume. At the house's four people and five flushes it returns 39,420 L against a true 40,150, and the 730 L gap is precisely the 0.1 L floor multiplied out. Read that breakdown line, not the headline: the headline is money, and this site publishes no tariff you could trust. The household box caps at 12, so a school is done by hand or in blocks.

Check the tank lid or manufacturer stamp for the per-flush rating.

WaterSense-certified toilets use 1.28 gal (≈4.85 L) or less per flush.

A commonly cited average is about 5 flushes per person per day.

Number of people regularly using this toilet.

Your local water utility's volumetric rate, in the unit shown.

Water saved per year

12,200 gal

Medium confidence

Figures that depend on a rate wait for yours — this page does not assume one.

What this calculation does not cover

  • Only the volumetric water rate you type in is applied. Sewer charges billed against metered water, fixed monthly service charges, and tiered block rates — where the marginal rate you actually save at is not the average rate on your bill — sit outside the arithmetic entirely.
  • Nothing on the cost side of the swap is included: the toilet, the installation, disposal of the old fixture, or any utility rebate. This is a gross annual water saving, not a payback period or a return on the purchase.
  • Flushing behaviour is assumed identical before and after — one flat volume per flush, the same flush count on both fixtures. Repeat flushes on a lower-volume bowl, a dual-flush full/reduced split, and leakage past a worn flapper or fill valve on either toilet are all outside the model.
  • The per-flush figures are nameplate ratings you enter, not what the fixture delivers. A worn flapper, an adjusted fill line, a re-set flush valve or a displacement device in the tank all move the real volume, and the calculation cannot see any of it.
  • Usage is 365 identical days at a fixed household size and a fixed rate. Vacancies, guests, seasonal occupancy, a household that changes size mid-year, and any rate rise or drought surcharge within the twelve months are not modelled.

What Is on the Moulding and What You Can Draw

The floor of the answer is partly physical rather than statistical, and it catches people out at commissioning. The number stamped on a shell is its brimful capacity, and you can use neither the top of it nor the bottom. Above, the overflow invert has to sit below the inlet so that a full tank passes flow onward instead of backing up the downpipe, and there is freeboard above that again. Below, the draw-off cannot sit on the floor: the whole point of a floating suction hanging a hand's width under the surface is that it takes the cleanest water in the vessel and leaves the settled solids alone, and everything under it is dead volume by design.

So the usable working volume is the depth between the overflow invert and the lowest draw-off level, multiplied by the plan area of the shell — and both of those levels are dimensioned on the manufacturer's installation drawing, which is where to get them rather than from a percentage quoted in an article. Do this before the tank is ordered, not after: if the working volume comes up short of the sizing figure, the fix is the next shell up, and that is a different hole.

Where the litres go in a buried tank

A buried harvesting tank in section, in five parts from the ground down: the access turret and cover, the calmed inlet sharing its level with the overflow that caps the store, the working volume between the overflow invert and the draw-off, the floating suction hanging clear of the floor, and the sediment zone and bedding beneath it that no pump is meant to reach.
  1. Access turret and cover — sets the buried depth, has to be rated for whatever drives over it, and is the only route in for inspection and desludging
  2. Calmed inlet, filter and overflow — the overflow invert caps the store, so everything the roof delivers above this level leaves rather than fills
  3. Working volume — the only litres the sizing calculation is allowed to count, measured between the overflow invert and the lowest draw-off Rain Barrel and Rainwater Collection Calculator
  4. Floating suction and riser — draws a hand's width below the surface, which is the cleanest water in the vessel and never the bottom of it Pump Drain Time Calculator
  5. Sediment zone and bedding — dead volume by design, holding what settles out between cleans, over bedding that has to stay level under a full load

Pick the shell's shape and enter its inside dimensions off the installation drawing, then set the depth to the overflow invert and the draw-off to the lowest suction level: the row for liquid above the draw-off is the working volume, the only figure the sizing is allowed to count, and the capacity row beside it is the number on the moulding.

The shape of the vessel holding the liquid, and which way up it stands.

Across the inside of the barrel, at its widest.

The height of the straight barrel, not counting any dished or domed ends.

Flat ends, shallow dished heads, or full half-spheres.

The dipstick reading, from the lowest point inside the tank up to the surface.

How far above the inside bottom the lowest outlet or suction sits; zero if it drains from the very bottom.

Liquid in the tank

423 gal

High confidence

Standing upright on a flat bottom, the tank has the same cross-section at every level, so depth and contents rise together and a dipstick marked in equal steps reads true from bottom to top.

Capacity when full
1,374.79 gal
Space left above the liquid
951.78 gal
Liquid above the lowest draw-off
423.01 gal
Depth as a share of the inside height
30.77 %
Contents as a share of capacity
30.77 %
Inside height, bottom to top
6.5 ft
Contents in litres (L)
1,601.28 L
Contents in cubic metres (m³)
1.6 m³
Contents in US gallons (gal)
423.01 gal
Contents in imperial gallons (imp gal)
352.23 imp gal
Capacity in litres (L)
5,204.16 L
Capacity in cubic metres (m³)
5.2 m³
Capacity in US gallons (gal)
1,374.79 gal
Capacity in imperial gallons (imp gal)
1,144.76 imp gal

Estimated cost — your price

This site holds no price list for this material — local prices vary too much to publish honestly. Enter your supplier's price and the result is costed with it.

6 ft
Schematic, drawn to the proportions you entered — not to scale on screen.

What this calculation does not cover

  • This is geometry, not gauging. A real tank bulges, dents, sits out of level, carries sludge and has fittings inside it, and none of that is in the arithmetic. For fuel accounting, custody transfer or anything a regulator reads, the governing figure is the tank's own calibrated strapping table or the maker's capacity chart.
  • Every dimension wanted is an INSIDE one. A plastic, bunded or insulated tank's walls are thick enough that outside measurements overstate the capacity, and a double-skinned tank's outer shell can be a good deal larger than the vessel holding the liquid.
  • Depth is measured from the lowest point inside. A tank out of level has a different depth at each end, and a reading taken from the ground, a plinth or the outside of a cradle is not the inside depth; measure at the middle, or at both ends and compare.
  • Dished ends are taken as the 2:1 ellipsoidal head, a quarter of the diameter deep, and both ends of a cylinder as the same kind. A DIN 28013 head is about as deep and holds almost as much. Most torispherical (flanged-and-dished) heads, the ASME and DIN 28011 kinds among them, are shallower and hold less — by Neutrium's coefficients for a thin wall, roughly 62% and 76% of a 2:1 head of the same diameter — and their exact volume needs the wall thickness and the knuckle radius, which this page does not ask for. A tank with a flat bottom and a domed top is outside the model too; a maker's drawing governs.
  • The two ovals are different shapes. An elliptical tank is a true ellipse in section; a flat-sided oval has straight sides between round ends and holds more for the same width and height. Tanks sold as oval can be either, so check which you have before trusting either figure.
  • Nothing here is converted to mass. Oils, fuels and chemicals differ in density, and density moves with temperature, so the same depth can be a different weight on a hot afternoon than on a cold morning.
  • Capacity is the volume the shell encloses, not a fill target. Tanks are filled short of it to leave room for expansion and for the overflow and vent to work, and the working volume of a rainwater or process tank sits between its overflow and its lowest draw-off.

The Store Is Sized on the Year; the Top-Up Is Sized on Twenty Past Twelve

A tank sized at eighteen days of average throughput will still be empty sometimes, and that is not a failure — it is the condition BS 8515 and BS EN 16941-1 both design around by requiring the system to satisfy demand with no rainwater available at all. What that means in practice is that the mains backup, not the tank, is what stops a school's WCs failing in the second week of a dry September. And the backup has to meet the building's peak, not its average, because the average is a fiction spread over twenty-four hours while a primary school does most of its flushing in two twenty-minute windows.

The peaking factor is the standard way of getting from one to the other for a collection vessel: multiply the average daily flow by a factor chosen from the building's occupancy pattern. A school with concentrated break-time use sits high in the usual range; an office or a dwelling with use spread through the day sits low. The result is a design daily throughput rather than an instantaneous flow, and it is the right basis for the top-up leg's duty and for the pump set's turndown. It is not the right basis for pipe sizing at the WC manifold, which is a separate calculation done in loading units under BS EN 806-3 and BS 8558, or in water supply fixture units against Hunter's curve where the International Plumbing Code applies. The two answer different questions and neither substitutes for the other.

One consequence for the tank itself is worth stating plainly, because it is another instance of the ceiling. Mains top-up belongs in a small header volume, not in the whole vessel — a day or two of demand, admitted through a Type AB air gap of the kind specified in BS EN 13077, so there is no continuous path from a non-potable store back to the main under any failure. Sizing the top-up to fill the whole tank turns a harvesting system into an expensively buried mains cistern, and it does it silently: the WCs keep flushing, the meter keeps turning, and nobody notices until the bill is read against the rainfall record.

Labelled for greywater cisterns, but the arithmetic in it — average daily flow multiplied by a peaking factor — is the generic scaling its own source names as the standard method for collection and detention systems, and nothing inside it is specific to greywater. Enter the school's term-time average of 4,140 L/day and the peaking factor your occupancy pattern justifies; at 3.5 it returns 14,490 L/day, which is 604 L/h or about 10 L/min sustained. The input caps at 5,000 L/day, so a larger building goes in per wing. Choose the factor from the building rather than from the default, and record where you got it — it is the one assumption in this calculation that nobody downstream can check.

The building's average daily greywater generation.

The multiplier applied to the daily average to size for short-duration peak demand.

Peak inflow rate

325 gal/day

Medium confidence

Peaking factor depends on the building's occupancy pattern and fixture usage profile — confirm the appropriate factor for your specific application against local greywater reuse code requirements.

Add the equipment this sizes

This result is a specification — 325 gal/day — not a quantity. Put the thing it sizes into your project: how many, what you call it, and your supplier’s price.

What this calculation does not cover

  • The answer is a flow per day, not the flow an inlet actually sees. Multiplying a daily average by a peaking factor carries no duration, so it cannot tell you the flow per minute arriving when two showers and a washing machine discharge at once — size inlet pipework, filters, diverters and transfer pumps from fixture discharge rates, not from this figure.
  • Nothing here sizes the cistern itself. Storage volume, retention time, drawdown against reuse demand, overflow to sewer and any make-up water arrangement are separate calculations, and greywater codes generally cap how long untreated greywater may be held before it must be used or discharged.
  • No treatment or water-quality content: screening, settling, filtration, disinfection and the rules on which fixtures may feed the system (kitchen sink and dishwasher waste is excluded in many jurisdictions) are all outside the model. It is also not a compliance check — permits, cross-connection control, backflow protection and non-potable pipe labelling are set by your local greywater code.
  • The peaking factor is never checked against anything: no fixture count, occupancy schedule, or code table. The result is a straight multiplication, so a factor borrowed from a different building type — or from a different peak definition, peak day versus peak hour — passes straight through to the answer with nothing flagging it.
  • Daily flows outside 50–5,000 L/day (13–1,320 gal/day) and factors outside 1.5–4 are pulled back to those bounds rather than calculated. A building generating more than about 5,000 L/day of greywater cannot be entered whole; it has to be split and run per wing or per riser.

Everything You Store, You Will One Day Have to Pump Out

Cleaning is where an oversized tank sends its bill, and it is almost never in the appraisal. Harvesting standards expect periodic inspection and desludging of the sediment zone, and a buried vessel has exactly one access route: the turret at the top. Emptying means pumping out through a hose, against the lift from tank invert to ground and into whatever receives it, and against the friction of every metre of hose.

The arithmetic is unkind to the big shell in a way volume alone does not convey. Take the school's 27,800-litre store, a submersible rated 100 litres a minute at zero head with 30 metres of maximum head, three and a half metres of lift and twenty-five metres of 32 mm hose. The pump does not deliver its rated flow — it settles at about 81 litres a minute where the head it can still produce matches the lift plus the friction — and the tank takes just under six hours. The 124,200-litre tank from the month-of-autonomy row takes over twenty-five, which is a two-day attendance and a different quotation. That is the same decision costing money for a second time, years after the hole was backfilled.

  1. Isolate the pump set and the mains top-up before anything is drawn down, so the top-up float does not spend the clean refilling behind you.
  2. Divert the downpipes at the filter, or pick a settled dry spell — a shower part way through empties several hours of pumping back into the vessel.
  3. Pump from the tank floor rather than through the floating suction, which is designed to avoid exactly the sediment you are trying to remove.
  4. Step the hose bore up rather than the pump duty if the time looks unacceptable: friction falls with almost the fifth power of the bore, and a bigger pump through the same narrow hose spends the extra output making heat.
  5. Treat the confined space properly. A buried tank below ground with a single top opening is a confined space, and entry is a permit and a rescue plan, not a ladder and an assistant.
  6. Refill through the mains top-up before the pump set is put back into automatic, so the floating suction is submerged and the pump is not asked to prime on air.

Written for pools and flooded floors, and exactly right here, because it solves for the operating point rather than dividing volume by the number on the box. Volume goes in as cubic metres in metric, not litres — 27.8 for the school store, and 124.2 for the month-of-autonomy shell — with the lift measured from the water surface to where the hose discharges, not to the pump. The bore is the most sensitive input on the form by a wide margin. Watch the breakdown line reporting what share of the rated flow survives the lift and the hose: below a fifth, the linear pump curve behind the result is at its weakest and the answer is an order of magnitude rather than a schedule.

The volume of water to move — a pool, a flooded floor, a tank.

The headline flow on the pump's box or plate — measured with no lift and no hose.

The lift at which the pump's flow falls to zero — on the same plate as the rated flow.

Height from the water surface up to the hose outlet.

The inside bore of the discharge hose — the single most sensitive number here.

Total discharge hose length, including the part lying flat.

Estimated drain time

10.4 hours

Medium confidence

Built on a linearised pump curve and Hazen–Williams hose friction (C = 150). A manufacturer's published curve, where you have one, governs.

Delivered flow at the operating point
21.14 gal/min
Share of rated flow surviving lift and hose
39.88 %
Friction head in the hose
9.13 ft
Total dynamic head
15.63 ft
33 ft
Schematic, drawn to the proportions you entered — not to scale on screen.

What this calculation does not cover

  • The vertical lift is held constant for the whole job and no water is assumed to arrive while the pump runs. In a pool the lift grows as the level drops; in a flooded basement groundwater, rain or a live leak keeps feeding the space. Real time to empty runs longer than this figure, and where inflow matches the delivered flow the level never falls at all.
  • Only straight hose length is charged for friction. Fittings, quick-couplers, a strainer or foot valve, a check valve, kinks, a partly closed discharge and any suction-side pipework all add head that is not in this number. Hazen-Williams with C = 150 is an empirical fit for smooth pipe carrying clean water — silt, debris, cold water or a ribbed corrugated hose all move the real loss away from it, and the formula is at its weakest in bores this small.
  • The pump is modelled as a straight line between the two figures on its plate. Where you have the manufacturer's published curve, that curve governs. Nothing here checks that the pump can prime at your suction lift, that it will hold prime as the water shallows, or that it is rated to run continuously for the hours reported — most utility pumps also stop drawing well before the floor is dry.
  • This is a time estimate, not a decision to empty the pool. It says nothing about hydrostatic uplift on an empty shell, liner shrinkage or collapse, or the groundwater conditions that decide whether a pool can safely be drained at all. Those questions belong to the pool builder and to the shell's own relief arrangements.
  • Where the water goes is outside this calculation. Discharging chlorinated, salt or silt-laden water to a storm drain, a watercourse or adjoining land is regulated in most places, and the receiving drain's capacity may be far below the flow reported here. Confirm the disposal route with the local water authority before running the pump.

What the Tank Quietly Does to the Softener

Harvested rainwater arrives at essentially zero hardness, which is a genuine benefit and also a trap for anyone specifying treatment on the same drawing. The trap is not that the rainwater needs softening — it does not, and a softener downstream of the tank would be an expense with no duty. It is that moving the WCs and the washing machine onto the tank removes a quarter to a third of the volume that used to pass through the softener — wherever the WC branch was softened too, which is more installations than it should be — and a softener is sized on volume.

Two things follow, one obvious and one not. The obvious one is that nothing fed from the tank should ever be plumbed through the softener, and that WCs should not have been softened in the first place — softening a cistern's fill is salt spent on water that goes straight to drain, which is why a properly configured installation leaves the WC branch and the outside taps on hard mains regardless of whether harvesting is involved. The other is that the softener's regeneration interval stretches. A unit sized for a seven-day cycle at the pre-harvesting volume now sees roughly a quarter less water and reaches the same capacity in nearer ten days — and that runs past the maximum interval most metered valves impose as a calendar override, because resin sitting unregenerated for long periods is its own hygiene problem. Set the override deliberately and record it in the O and M file rather than leaving the installer's default to be discovered years later.

One more coupling belongs on the same drawing: whatever supplies the tank's mains top-up should be taken off the hard main, upstream of any softener, and it should not be softened. Sodium-rich water introduced into a store that may end up on planting, or into a vessel whose overflow discharges to a soakaway, is a chemistry nobody designed and nobody wanted. It is a five-minute decision at the schematic stage and an expensive one to unpick after the ground floor is screeded.

Use this on the pre-harvesting condition, which is the sizing case: the softener still has to serve the whole house on the day the tank is out of commission. Four people at 15 grains per gallon on a weekly cycle needs 31,500 grains and lands on a 32,000-grain unit. Note what is baked in before trusting it anywhere else — 75 US gallons per person per day, a North American household figure, against the 125 litres per person per day a new English dwelling is designed to under Approved Document G. Take the hardness from the utility's annual water quality report rather than a guess, and divide mg/L by 17.1 to reach grains per gallon.

Number of people in the household.

Your water hardness in grains per gallon (GPG).

How often you want the softener to regenerate.

Recommended softener capacity

24,000 grains capacity

Medium confidence

This is a standard rule-of-thumb sizing method. Iron content, unusually high water use (irrigation, hot tubs), and manufacturer-specific efficiency ratings can shift the ideal size.

Daily softening demand
2,250 grains/day
Capacity needed before rounding
15,750 grains

Add the equipment this sizes

This result is a specification — 24,000 grains capacity — not a quantity. Put the thing it sizes into your project: how many, what you call it, and your supplier’s price.

What this calculation does not cover

  • The size it recommends is a nameplate grain rating, and nameplate ratings are measured at maximum salt dose. Run at the lower, more economical salt settings most units are actually set to, the same bed delivers materially fewer grains per cycle. The figure also holds back no reserve, while a metered valve starts a cycle before the bed is exhausted, so real intervals come out shorter than the days you picked.
  • Water use is a flat 75 gallons (284 litres) per person per day, a planning convention rather than your household's measured consumption. Irrigation, a pool or hot tub top-up, a home business, or a second dwelling on the same supply are not in that figure. Two meter reads a fortnight apart with the irrigation off beat it.
  • Only calcium and magnesium hardness is counted. Iron and manganese consume exchange capacity too and have to be added to the hardness figure by the equipment maker's own method; sediment, chlorine and extreme pH foul the bed or shorten resin life without changing this number at all.
  • This is the grains side of the job only. It says nothing about the control valve's service flow rating, the pressure drop that costs when three fixtures run together, or the resin bed's own service flow limit — a tank with enough grains still passes hardness if water is pushed through it too fast. The sizes it chooses from are common single-tank residential ratings; twin-tank and commercial units are outside it.
  • This is not a compliance check. Brine discharge to a septic system or sewer is restricted or banned in some jurisdictions, the drain line carries its own air gap and sizing requirements, and softening adds sodium to the treated water in proportion to the hardness removed — none of that is in this calculation.

Buoyancy, Backfill, and the One Claim You Cannot Make

An empty buried tank is a boat. A 6,000-litre shell displaces six tonnes, and if the excavation fills with groundwater or surface run-off while the tank sits empty — which is exactly the state it is in between delivery and commissioning — the uplift will lift it, crack the inlet connection, or tilt it enough that the overflow invert no longer runs the way it was drawn. Every manufacturer of moulded underground tanks publishes an installation instruction that makes the bedding, the backfill material and any concrete anti-flotation surround a condition of the warranty, and those instructions also state the maximum cover depth and whether the shell is rated for a trafficked or non-trafficked location. They are shell-specific, not general advice: a surround detailed for one manufacturer's ribbing is not evidence for another's.

The inlet side has its own governing document, most often skipped because the tank feels like the interesting part. Whatever is above the filter still has to carry the peak intensity of a storm — gutters and downpipes sized under BS EN 12056-3, Gravity drainage systems inside buildings — Roof drainage, layout and calculation — because water that overshoots an undersized eaves gutter has left the system before any of this arithmetic applies. Downstream, the overflow must be at least the bore of the inlet, trapped and vermin-screened, and taken to a destination that can accept it in a real storm rather than to the ground beside the building.

The claim to be careful with is the drainage one. A harvesting tank is not, by itself, attenuation. A stormwater condition asks for empty volume available at the start of the design storm, and the working volume of a harvesting store is by design as full as the weather has recently allowed — most full, in fact, precisely in the wet periods when attenuation is wanted. CIRIA C753, The SuDS Manual, deals with the circumstances in which harvesting can be credited towards stormwater control, and it turns on a controlled release or a dedicated retention volume kept empty rather than on the storage existing at all. Claiming the tank twice, once as supply and once as attenuation, is the single most common way one of these schemes fails at technical approval.

  1. Fix the tank position against the drainage survey first — outside the foundation's zone of influence, clear of the incoming service and the soakaway, and reachable by a tanker hose for desludging.
  2. Check the winter groundwater level, not the level on the day of the trial hole, and specify the anti-flotation measure the manufacturer's instruction requires for that condition.
  3. Bed, backfill and fill in the sequence the instruction gives, which usually means filling the tank with water in step with the backfill so the shell is never resisting ground pressure empty.
  4. Mark every metre of non-potable pipework and label every outlet, to BS 1710 identification, and put restricted-access outside taps on the harvested leg rather than ordinary ones.
  5. Record the working volume, the overflow invert level, the top-up header volume and the softener override in the O and M file, because the next person to touch the system will have none of this page's arithmetic.

What the tank line on the schedule needs behind it

Six figures, in this order, and the tank is the smallest of them rather than the largest. Everything here is measurable from a drawing, a rainfall record and a manufacturer's data sheet, and all of it is cheaper to settle before the excavation is priced than after the shell is on site.

  • Plan area of every roof plane actually routed to the tank — Flat footprint, not tiled surface, and only the planes whose downpipes reach the filter. A plane draining to the front gully is not catchment however large it is.
  • Annual rainfall from a named station, and the two reductions — Met Office climate averages or the NOAA 1991–2020 normals. Then a yield coefficient on the catchment and a hydraulic filter efficiency, which Approved Document G takes together at 0.7 in its example; the filter maker's own efficiency replaces it where there is one.
  • Annual non-potable demand, on the days the building actually draws — Flushes dominate. A house draws 365 days; a school draws about 190. Using the wrong denominator is the error that survives review, because the arithmetic around it is faultless.
  • About five per cent of the lesser of the two — the tank — Eighteen days of the smaller flow, 4.93 per cent of a year, from the intermediate approach of BS 8515, which was withdrawn in 2018 and replaced by BS EN 16941-1. 1,788 L for the worked house, 27,800 L for the school block. If the store the client wants is larger, the question to ask is what will refill it.
  • Working volume between overflow invert and draw-off — Off the manufacturer's installation drawing, not off the moulded capacity. The freeboard above and the sediment zone below are both unusable, and finding that out at commissioning means a different shell and a different hole.
  • Peak day, mains top-up duty, and the emptying time — Peak from the average by a peaking factor you can justify. Top-up into a header of a day or two through a Type AB air gap. And the hours to pump the store out for a clean, which is the running cost of every litre of oversizing.
Open this as a workspace →

Opens the calculators above on one screen with the dimensions from this article already filled in. Quantities only — this site publishes no price list, because local prices vary too much to publish honestly.

Drawn from

  • BS 8515, Rainwater harvesting systems — Code of practice (simplified, intermediate and detailed sizing approaches; screening, calmed inlet and maintenance requirements), withdrawn by BSI on 19 July 2018
  • BS EN 16941-1, On-site non-potable water systems — Part 1: Systems for the use of rainwater (2018, and the current 2024 edition)
  • BRE, BREEAM Knowledge Base KBCN1179 (18 September 2018) — BS 8515 withdrawn and replaced by BS EN 16941-1:2018, whose basic approach is equivalent to BS 8515's intermediate approach
  • ARCSA/ASPE 63, Rainwater Catchment Systems
  • BS EN 12056-3, Gravity drainage systems inside buildings — Part 3: Roof drainage, layout and calculation
  • BS EN 13077, Devices to prevent pollution by backflow of potable water — Air gap with non-circular overflow (unrestricted) — Family A, Type B
  • BS EN 806-3, Specifications for installations inside buildings conveying water for human consumption — Part 3: Pipe sizing — Simplified method
  • BS 8558, Guide to the design, installation, testing and maintenance of services supplying water for domestic use within buildings and their curtilages
  • BS 1710, Specification for identification of pipelines and services
  • The Water Supply (Water Fittings) Regulations 1999 (England and Wales) — maximum flush volume for WCs installed since 2001, and backflow protection by fluid category
  • Approved Document G, The Building Regulations (England) — Sanitation, hot water safety and water efficiency, with The Water Efficiency Calculator for New Dwellings; Appendix A, Table A5.1, rainwater collection by the BS 8515 intermediate approach, with 0.7 as the example yield coefficient and hydraulic filter efficiency
  • CIBSE Guide G, Public Health and Plumbing Engineering — per-occupant consumption benchmarks for non-domestic buildings
  • HSE Approved Code of Practice and guidance L8, Legionnaires' disease: The control of legionella bacteria in water systems
  • HSE HSG274 Part 2, Legionnaires' disease: Technical guidance — The control of legionella bacteria in hot and cold water systems
  • CIRIA C753, The SuDS Manual — rainwater harvesting used towards stormwater control
  • US Energy Policy Act of 1992 — 1.6 gallons per flush for tank-type toilets manufactured from 1994
  • US EPA WaterSense Specification for Tank-Type Toilets — 1.28 gallons per flush
  • International Plumbing Code — non-potable water systems provisions and water supply fixture unit sizing
  • Met Office UK Climate Averages (1991–2020 station series) and NOAA National Centers for Environmental Information 1991–2020 U.S. Climate Normals

Guidance, not a specification. Local codes, the engineer of record and the product manufacturer’s instructions govern where they differ from anything written here.