Water Treatment · Calculate & Specify
Coagulant and Polymer Dose Calculator
You have a dose from a jar test, an engineering calculation or an established site setpoint. This converts it into litres or kilograms of the product you actually buy, on the basis you actually buy it. It performs unit arithmetic on your numbers and nothing else.
THIS CALCULATOR DOES NOT DETERMINE THE CORRECT TREATMENT DOSE.
Enter a dose you have already validated. Acceptable sources of a validated dose:
- · Jar testing on the actual water, at representative temperature and mixing energy
- · Engineering validation or a process design calculation for the specific plant
- · Manufacturer guidance for the specific grade in the specific duty
- · Established, recorded site operating parameters
Your inputs
Nothing is assumed. Leave a field blank and the result says so.
Result
Arithmetic on your numbers only.
- Flow
- 250 m³/h
- Product as supplied per day
- 108 kg/day
- Active substance per day
- Not calculated
- Product volume per day
- Not calculated
- Product per month
- 3,240 kg/month
- Active-substance quantity not calculated: no active content (% w/w) was supplied.
- Product volume not calculated: no solution density (kg/L) was supplied. Density is product- and temperature-specific and is not assumed here.
This is a chemical quantity, not a treatment outcome. It does not predict turbidity removal, residual metal, sludge production or compliance of any kind.
Definitions, formulas and unit conversions
Validated dose (mg/L) — the concentration of chemical added per litre of water treated, established outside this tool. Active basis is the mass of the active substance itself; as-supplied basis is the mass of the formulated product including water and any other components.
| Quantity | Formula |
|---|---|
| Mass rate | flow (m³/h) × dose (mg/L) ÷ 1000 = kg/h |
| Per day | kg/h × dosing hours per day |
| Active from as-supplied | kg as supplied × active % ÷ 100 |
| As-supplied from active | kg active ÷ (active % ÷ 100) |
| Volume | kg as supplied ÷ density (kg/L) = litres |
| Polymer per dry tonne | t DS/day × kg active per t DS = kg active/day |
Unit conversions used: 1 L/s = 3.6 m³/h · 1 m³/day = 1/24 m³/h · 1 US gpm = 0.2271247 m³/h · 1 US MGD = 157.7255 m³/h · 1 mg/L applied to 1 m³/h = 1 g/h.
Worked example
A plant treats 250 m³/h. Jar testing on the current raw water settled on 18 mg/L of PAC as supplied. The product TDS states a density of 1.20 kg/L. The dosing point runs 24 hours per day.
- Mass rate as supplied = 250 m³/h × 18 mg/L ÷ 1000 = 4.5 kg/h.
- Per day = 4.5 kg/h × 24 h = 108 kg/day.
- Volume per day = 108 kg ÷ 1.20 kg/L = 90 L/day.
- Per 30-day month = 2 700 L, or 3.24 tonnes as supplied.
The 18 mg/L came from a jar test on that water on that day. It is not a property of PAC, it is not transferable to another water, and this arithmetic does not validate it.
Reading the result
- · The per-month figure is what belongs in an enquiry or a budget. State the basis you used, or the quotation you get back will not be comparable.
- · If two products are being compared, compare the active requirement, not the as-supplied one. A cheaper product at half the active content is not cheaper.
- · Deliveries vary. When the CoA active content of a delivery differs from the last one, the as-supplied dose has to be renormalised to keep the active dose constant.
Use this when
- A jar test gave you a dose in mg/L and you need product volume per day for the feed pump and the purchase order.
- You are comparing two coagulants whose active contents differ and want the as-supplied quantity for each.
- You need a monthly tonnage to put into an enquiry or a budget.
How the output is produced
- Active mass rate = flow x dose, converted to consistent units. 1 mg/L applied to 1 m³/h is 1 g/h of active.
- As-supplied quantity divides the active requirement by the fractional active content you enter, and — for a solution quoted per litre — by the solution density you enter.
- Nothing is assumed. If you do not supply an active content or a density, the calculator reports the active basis only and says so.
What this page does not determine
- THIS CALCULATOR DOES NOT DETERMINE THE CORRECT TREATMENT DOSE. The dose must come from jar testing, engineering validation, manufacturer guidance or established site operating parameters.
- It does not predict turbidity removal, residual metal, sludge production or any treated-water quality.
- It does not establish potable-water suitability, regulatory compliance or discharge compliance.
- It does not assume a density or an active content. Unknown inputs stay unknown.
Relevant Allzone products
These are catalogue identities relevant to this decision. A listing here is not a statement that the material is suitable for your system, and it is not a certification, performance or drinking-water claim.
- Poly Aluminium Chloride (PAC)Pre-hydrolysed aluminium coagulant supplied as a solution of stated basicity.
- Aluminium Sulfate (Alum)Aluminium coagulant supplied dry or as a solution of stated Al2O3 content.
- Ferric ChlorideIron coagulant solution, normally quoted as a percentage FeCl3.
- Ferric SulfateIron(III) coagulant used where chloride addition is unwanted.
- Ferrous SulfateIron(II) salt used in coagulation and phosphorus precipitation duties.
- Anionic Polyacrylamide FlocculantBridging flocculant dosed after a coagulant has destabilised the colloid.
- Cationic Polyacrylamide FlocculantCharge-carrying polymer commonly used in sludge conditioning duties.
- Non-Ionic Polyacrylamide FlocculantNeutral bridging polymer used where charge interference is a problem.
- PolyDADMACCationic organic coagulant supplied at a stated active polymer content.
- Polyamine CoagulantLow-molecular-weight cationic organic coagulant solution.
Where this comes from, and what it cannot tell you
Standard jar-test method literature (ASTM D2035 Standard Practice for Coagulation-Flocculation Jar Test of Water)
Supports: That the validated dose for a coagulant or polymer is determined experimentally on the actual water, at representative temperature and mixing energy, and expressed in mg/L.
Limitation: A jar test predicts direction and approximate optimum. Full-scale mixing, retention time and raw-water variability shift the result; confirmation on plant is required.
Standard practice — North America · Current standard practice; confirm the edition in force.
Water-treatment engineering references on coagulation and flocculation (AWWA Water Treatment Plant Design; MWH's Water Treatment: Principles and Design)
Supports: That coagulation performance is governed by charge neutralisation and sweep-floc mechanisms, that metal-salt coagulants consume alkalinity and depress pH, and that rapid-mix and flocculation energy and time control floc formation and strength.
Limitation: Design references describe mechanisms and typical ranges. They do not give a dose for a specific raw water; that comes from jar testing on the actual water.
Engineering literature — general practice · Established water-treatment engineering.
Product technical literature conventions across water-treatment chemical families (PAC basicity and Al2O3 content, hypochlorite trade percent vs percent available chlorine, alum Al2O3 basis, phosphonate active acid content, polymer active polymer content)
Supports: That the same chemical family is quoted on different bases by different suppliers, and that a price per kilogram is only comparable after normalising to active content and, for solutions, to solution density.
Limitation: Conventions vary by supplier and by region. The basis must be read from the specific TDS or CoA; it must never be assumed.
Manufacturer documentation — international · Always read the document for the specific product offered.
Polyacrylamide manufacturer technical literature on make-down, ageing and dosing of dry and emulsion polymers
Supports: That polymer solutions require controlled dilution and an ageing period to develop chain extension, that over-shearing degrades performance, and that emulsion and dry products are quoted on different active-polymer bases.
Limitation: Make-down times, concentrations and shear limits are grade-specific. Always work from the datasheet of the exact grade purchased.
Manufacturer documentation · Grade-specific; verify against the current TDS.
Related knowledge & tools
- Coagulant selection guideWhich coagulant family fits the water — the selection decision, not the arithmetic.
- Clarification troubleshootingIf the validated dose is being fed and the water is still not clearing.
- Chemical strength and documentationWhere the active content and density in this calculation come from.
- Water Treatment KnowledgeSolve a problem, choose and compare, learn, calculate.
