Water quality basics
TDS, Hardness and Iron: A Water Quality Guide
Quick answer
TDS, hardness and iron are three different measurements that are often read as one. TDS describes salinity, hardness describes scale risk from calcium and magnesium, and iron describes staining and fouling risk. This guide gives the thresholds that decide when softening, iron removal or reverse osmosis is justified, and the order to test them.
What do TDS, hardness and iron actually measure?
TDS is the total mass of dissolved solids, reported in mg/L and estimated in the field from conductivity at a conversion factor of 0.5–0.7. Hardness counts only calcium and magnesium, expressed as an equivalent mass of calcium carbonate. Iron is a single element, reported as total iron in mg/L, dissolved plus particulate. Each number answers a different question: salinity, scale potential and staining potential.
A water can carry 900 mg/L TDS and almost no hardness when the solids are sodium chloride. Another can sit at 180 mg/L TDS and still scale a heater, because 150 mg/L of that total is calcium carbonate. Treating TDS as a hardness proxy is the most common error in package selection, and it usually shows up as a softener that was never installed or an RO that scales in its first season.
- TDS: mg/L, with conductivity in µS/cm multiplied by 0.5–0.7
- Hardness: mg/L as CaCO₃, calculated as Ca × 2.5 + Mg × 4.1
- Iron: mg/L total Fe, dissolved ferrous iron clear, oxidised ferric iron visible
- Alkalinity: mg/L as CaCO₃, the partner value that decides whether hardness scales or stays soluble
Why can two waters with the same TDS behave differently?
Behaviour is set by which ions carry the TDS, not by the total. Sodium and chloride are monovalent, stay soluble and raise conductivity without scaling. Calcium and magnesium are divalent, precipitate as carbonate above roughly 60 °C, and consume soap. Sulphate adds a scaling path as calcium sulphate above about 1,800 mg/L at 25 °C. Silica polymerises above 100–150 mg/L and is difficult to remove once baked onto a membrane.
Temperature and pH decide the outcome. Water at 500 mg/L TDS as calcium bicarbonate may be stable at 20 °C and deposit scale at 70 °C, because calcium carbonate solubility falls as temperature rises. The same concentration as sodium chloride stays clear at any domestic temperature. That is why a softener decision needs hardness, alkalinity and pH, not a TDS pen alone.
What hardness level needs a softener?
Softening is justified by the combination of hardness, temperature and downstream equipment. Below 60 mg/L as CaCO₃, most commercial systems run without scale. Between 60 and 120 mg/L, scale forms slowly above 60 °C, and the decision depends on the heater, the steam generator and the RO recovery target. Above 120 mg/L, softening is the default for any system that heats water or runs an RO above 65% recovery.
| Hardness (mg/L as CaCO₃) | Classification | Typical effect | Action |
|---|---|---|---|
| 0–60 | Soft | No scale in most cases; corrosive below 50 | No softener; check pH and alkalinity |
| 60–120 | Moderately hard | Light film on heaters above 60 °C | Softener optional; decide by temperature and recovery |
| 120–180 | Hard | Visible scale at 60–80 °C, higher soap use | Softener recommended |
| 180–300 | Very hard | Rapid scale, reduced heat transfer | Softener required |
| Above 300 | Extremely hard | Scale within weeks; RO scaling likely | Softening plus blending or RO |
Bands are practical guidance, not a regulatory scale. Heated equipment and high-recovery RO shift the decision downward.
How much iron and manganese can a well tolerate?
Iron above 0.3 mg/L stains fixtures and laundry, and manganese above 0.05 mg/L leaves black deposits. Both are aesthetic thresholds used by the World Health Organization, and both are the point where an RO membrane begins to foul, because iron oxide plugs the feed spacer and is not removed by normal cleaning. Dissolved ferrous iron passes a 0.45 µm filter and looks clear; oxidised ferric iron is caught on the filter and looks orange.
| Parameter | Trigger | Symptom if ignored | First response |
|---|---|---|---|
| Iron (Fe) | Above 0.3 mg/L | Orange staining, metallic taste | Oxidation plus multimedia filtration |
| Manganese (Mn) | Above 0.05 mg/L | Black deposits, bitter taste | Oxidation at higher pH plus filtration |
| Turbidity | Above 1 NTU | Cartridge clogging, membrane fouling | Multimedia filter, 5 µm cartridge |
| Hardness | Above 120 mg/L as CaCO₃ | Scale on heaters and membranes | Softener or antiscalant |
| TDS | Above 600–1,000 mg/L for drinking | Mineral or salty taste | Reverse osmosis or blending |
| Free chlorine at RO inlet | Above 0.1 mg/L | Irreversible membrane oxidation | Activated carbon or bisulphite |
Which numbers should you collect before choosing a system?
A laboratory analysis costs far less than a wrong skid. Take the sample after the pressure tank and before any treatment, and record whether the iron and manganese samples were field-filtered, because filtered and unfiltered results describe different fractions of the same metal. A single snapshot is not enough for a well: test again after heavy rain and at the end of the dry season.
| Parameter | Method | Design use |
|---|---|---|
| TDS and conductivity | Gravimetric or meter at 25 °C | RO stage, pump pressure, blending ratio |
| Hardness | EDTA titration or ICP | Softener size, resin volume, salt dose |
| Iron and manganese | Colorimetric, filtered and unfiltered | Oxidation method, filter media, backwash rate |
| pH and alkalinity | Electrode and titration | Scaling index, corrosion control, oxidant dose |
| Turbidity and SDI15 | Nephelometer and 0.45 µm test | Prefilter rating, RO feed acceptability |
| Nitrate, sulphate, chloride | Ion chromatography | RO rejection check, corrosion risk |
| Bacteria and coliforms | Membrane filtration or plate count | UV dose, chlorination and dechlorination |
Sampling point, date and filtration status must be recorded with the results.
How do the three parameters decide the treatment train?
The order is fixed by what each step can tolerate. Oxidation and filtration come first because iron and manganese foul every downstream surface, including softener resin and RO membranes. Softening comes next because it protects heaters and allows higher RO recovery. Reverse osmosis follows, and carbon plus UV polish the permeate.
- 01
1. Oxidise and filter
Aeration, chlorination or ozone converts dissolved iron and manganese into filterable oxide, removed in a multimedia or catalytic bed at 10–30 m/h.
- 02
2. Soften
A strong-acid cation resin exchanges calcium and magnesium for sodium, with 30–650 kg of resin in the CK-SF range and 25–800 L salt boxes.
- 03
3. Desalinate
A single-stage RO at 10–15 bar removes 95–99% of dissolved salts, delivering 50–75% recovery across the CK-RO range.
- 04
4. Polish and disinfect
Activated carbon removes residual oxidant and taste, then UV at 30–40 mJ/cm² or ozone protects the stored water.
When is RO justified by TDS alone?
RO is justified when TDS drives taste, a process limit or a regulated limit, not when it merely reads high. For drinking water, many people notice a mineral or salty edge above 600 mg/L and reject the water above 1,000 mg/L. For process water the limit comes from the equipment: boiler make-up, humidifiers, ice machines and beverage recipes each set their own number.
A single-stage RO removes 95–99% of dissolved salts and, from a feed of 300 µS/cm at 25 °C, delivers permeate at or below 10 µS/cm. Below 600 mg/L, carbon filtration and UV usually solve taste and safety problems at lower cost and without a concentrate stream. Between 600 and 1,000 mg/L, blending permeate with raw water is often the cheapest way to hit a taste target.
Concentrate disposal belongs in the same decision. A small RO at 50% recovery doubles the salt load sent to drain, and where discharge is metered or sewer rules limit TDS, that cost changes the comparison. Where the building also needs soft water, a softener may solve the scale problem at lower capital cost and leave the TDS untouched. The two devices are not interchangeable, and buying one to fix the other problem is how projects end up with a plant that meets the spec sheet and not the requirement.
Can one filter fix TDS, hardness and iron at the same time?
No single cartridge does all three. A sediment filter removes particles down to its rating, typically 5–100 µm, and passes dissolved salts, hardness and dissolved iron. A softener removes hardness by ion exchange and leaves TDS almost unchanged; sodium rises by about 46 mg/L for every 100 mg/L of hardness removed. Activated carbon removes chlorine, taste and some organics but not salts or hardness.
RO rejects all three dissolved groups at 95–99%, but it needs iron removed first, because iron oxide fouls the membrane and is not recovered by cleaning. The practical order is oxidation and filtration for iron, softening for hardness, then RO for salinity, with carbon and UV as polishing steps. A vendor who proposes one vessel for all three is describing a cartridge, not a treatment train.
FAQ
Frequently asked questions
Questions buyers actually ask during sizing and quotation. Answers match the specifications above.
01 Is TDS the same as hardness?
02 What TDS level is safe for drinking?
03 Does a softener reduce TDS?
04 Can a carbon filter remove iron?
05 Does boiling water reduce TDS or hardness?
06 How often should well water be tested?
07 What is the first step if all three values are high?
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- Water quality basics TDS vs Hardness: What the Numbers Really Mean TDS and hardness both read in mg/L but measure different things. Convert one to the other, interpret soft and hard water, and choose the right treatment.
- Water quality basics Iron and Manganese in Well Water: Removal Guide Iron above 0.3 mg/L stains; manganese above 0.05 mg/L turns water black. Compare aeration, chlorine and ozone, then size the filter and backwash.
- Water quality basics SDI and Turbidity: Setting RO Feed Water Limits SDI predicts colloidal fouling; turbidity does not. Learn the 15-minute test, the limits membranes need, and which pretreatment actually lowers SDI.
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