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The service-path visual is unavailable. Sizing results remain available below.
Household flow and filter sizing inputs
Presets keep your selected display units and replace the planning values.
Use current water-test or utility information when available.
Confirm the exact cartridge or media against its manufacturer data sheet.
One column-level unit keeps the repeated worksheet compact and auditable.
Format: fixture, simultaneous count, flow, priority. Priorities: critical, essential, comfort, optional, shed.
Use product labels or measured flow when available.
Use a meter or water-bill average when possible.
Accepted range equals 25-90 PSI.
From 0% to 50% above the worksheet peak.
%
Accepted range equals 2-15 PSI.
Use the number of housings or treatment stages installed in the same service path.
The neutral default is 0, which applies no manufacturer override.
One decimal is the default.
Sizing plan
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Calculation trace:
The hydraulic and maintenance factors are planning assumptions, not a certified product curve.
target = Σ(count × fixture flow) × (1 + headroom)
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FixtureSimultaneousFixture flowPeak flowPriorityCopy
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Whole-house filtration has to satisfy two different clocks. During a busy few minutes, the filter must pass the combined flow from showers, faucets, toilet refills, appliances, and any filtered outdoor tap. Across weeks and months, its media or cartridge must cope with the total water volume and the material being removed.

Daily use cannot stand in for peak flow. A household may average a few hundred gallons per day yet briefly need several fixtures at once. Choosing a filter from the daily total alone can produce weak showers and slow fills; choosing only by a large port size can ignore the cartridge's restriction and contaminant claim.

Service-flow rating
The flow a housing, cartridge, or media system can pass under stated conditions.
Pressure drop
The pressure lost as water crosses the treatment path. Loss normally rises with flow and as a filter becomes loaded.
Capacity
A volume or time estimate for maintenance. It does not prove that peak household demand can pass through the system.

Water quality determines what treatment belongs in the line. Sediment, chlorine taste, chloramine, iron, turbidity, microorganisms, and dissolved chemicals call for different media and certifications. A larger filter does not automatically remove more kinds of contaminants, and a certified reduction claim applies only to the contaminants and conditions named for that product.

Private wells need particular care because appearance and taste do not establish safety. Current laboratory results and local health guidance should lead the treatment decision. Media tanks also need a separate backwash-flow check, while cartridge systems need manufacturer pressure-drop curves at the intended flow.

A sizing estimate is useful for comparing housing classes and spotting hydraulic risk before shopping. Final selection still depends on measured flowing pressure, actual fixture demand, water analysis, pipe size, bypass and drain requirements, and the exact manufacturer's rated performance.

How to Use This Tool:

Build the service-flow estimate from simultaneous fixtures, then check pressure and maintenance separately.

  1. Choose a household profile as a starting point, then select the source-water load and treatment train that match current evidence.
  2. Edit the Peak fixture worksheet with one fixture, simultaneous count, flow, and priority per row. Use measured or rated fixture flow where possible.
  3. Enter daily water use and the inlet pressure measured while water is flowing. Set headroom from 0% to 50% and a clean pressure-drop limit from 2 to 15 PSI.
  4. Select the number of filter stages in the same series path. Apply a manufacturer capacity override only when a product data sheet supplies a relevant gallon rating.
  5. Review service-flow fit, estimated outlet pressure, and replacement timing. Treat any undersized or pressure-risk result as a reason to measure again or obtain a product-specific design.

Interpreting Results:

The selected class is the first planning class that clears both the service-flow target and the entered clean pressure-drop limit. If none clears both, the estimate falls back to the first class that clears flow; if even that is unavailable, it shows the largest class and marks the flow as undersized.

  • Sized means rated service flow is at least the headroom-adjusted fixture peak. It is not a guarantee that a particular cartridge will meet that rating.
  • Healthy pressure requires estimated outlet pressure of at least 40 PSI and pressure drop no greater than the selected limit.
  • Watch allows at least 35 PSI outlet pressure and drop no greater than 135% of the limit. Anything lower is Risk.
  • Normal replacement timing reaches the floor assigned to the source-water load. Below that floor, at least 0.75 month is Short; less is Very short.

Technical Details:

The estimate combines a hydraulic screen with a capacity screen. Fixture rows create the simultaneous peak. Headroom raises that peak to a shopping target, while a nonlinear pressure model estimates clean-filter loss. Daily gallons then convert adjusted capacity into a maintenance interval.

Formula Core:

All flows are converted to US gallons per minute (GPM), pressure to pounds per square inch (PSI), and daily volume to gallons per day before calculation.

Qpeak=(ni×qi) Qtarget=Qpeak×(1+h100) r=max(0.05,QtargetQrated) Δp=Δpbase×r1.85×fsource×ftreatment×(1+0.38(s-1)) Cadjusted=max(100,Cbase×fsource capacity×ftreatment capacity×futilization) M=max(0.25,min(CadjustedD×30.44,Msource cap,Mtreatment cap))

n is simultaneous fixture count, q is fixture flow, h is headroom percent, s is the number of stages in series, C is adjusted gallon capacity, D is daily use, and M is the interval in months. The stage multiplier is 1.00, 1.38, or 1.76 for one, two, or three stages.

Lookup Core:

The following are fixed planning classes, not a catalog of certified products. Each class supplies the service rating, base capacity, and base clean drop used by the formulas.

Whole-house filter planning classes
Planning classService GPMBase capacityBase drop
10 in standard housing512,000 gal4.8 PSI
10 in large-diameter housing1030,000 gal3.7 PSI
20 in large-diameter housing1565,000 gal3.1 PSI
Dual 20 in parallel housings25125,000 gal2.6 PSI
10 x 54 media tank class9220,000 gal2.8 PSI
12 x 52 media tank class12320,000 gal2.6 PSI
14 x 65 media tank class18520,000 gal2.4 PSI
Parallel media tank class28900,000 gal2.2 PSI

Source-water and treatment factors deliberately make the planning result more conservative as loading or restriction increases. The capacity calculation also applies 0.92 when target flow exceeds 75% of the selected service rating and 0.84 when it exceeds 90%.

Water source and treatment factors
ConditionCapacity factorPressure factorInterval capNormal floor
Municipal, low sediment1.001.0012 mo3 mo
Municipal chloramine or taste/odor load0.721.089 mo2 mo
Well water, visible sediment0.501.284 mo1 mo
Well water, iron or heavy turbidity0.361.482.5 mo0.75 mo
Seasonal or intermittent home0.701.126 mo1 mo
Sediment prefilter1.120.9012 mo
Sediment plus carbon0.861.1812 mo
Carbon block or fine filtration0.621.429 mo
Backwashing media tank3.400.8260 mo

Rule Core:

Fixture rows accept zero to 20 simultaneous uses and zero to 50 GPM per fixture, with no more than 30 rows and a positive combined peak. Daily use must equal 25 to 1,500 gallons per day, inlet pressure 25 to 90 PSI, and capacity override 0 to 1,000,000 gallons. One US gallon equals 3.785411784 litres, and one PSI equals 6.894757293168 kPa for the displayed conversions.

Limitations:

The pressure equation, capacity factors, class values, and interval caps are planning assumptions rather than certified product curves. Dirty-filter loss, media chemistry, water temperature, pipe fittings, valves, and actual contaminant loading can move the result substantially.

  • Verify the exact cartridge or media's service flow and pressure-drop curve at the intended flow.
  • Match third-party certification to the contaminant of concern; a certification number is not a universal removal claim.
  • Test private well water and confirm treatment with qualified local guidance. Do not infer drinking-water safety from this size estimate.
  • Check backwash flow, drain capacity, pump cycling, and pressure-tank behavior separately for regenerating or backwashing systems.

References: