
Pool water chemistry and water balance: pH, alkalinity and LSI
In pool water chemistry, water balance is the state in which the water neither dissolves nor deposits calcium carbonate; pH, alkalinity, hardness, temperature and TDS set it together.
In pool water chemistry, water balance is the state in which the water neither dissolves nor deposits calcium carbonate; pH, alkalinity, hardness, temperature and TDS set it together.
Pool water balance is the state in which the water is saturated with respect to calcium carbonate (CaCO3), meaning it neither dissolves lime from the pool finish and grout nor deposits scale on the surfaces and on the heater exchanger. This state is set by the combination of five quantities rather than by a single parameter: pH, total alkalinity, calcium hardness, water temperature and total dissolved solids (TDS). The numerical expression of the balance is the Langelier Saturation Index (LSI); if the index is close to zero the water is balanced, if negative it is corrosive (scale-dissolving), if positive it is scale-forming (scale-depositing).
Water balance does not mean the water is disinfected. A pool water can be in exact balance by LSI with zero free chlorine; conversely, water with 3 mg/L free chlorine keeps eroding a concrete pool surface if its alkalinity is low. Disinfection and balance are two separate ledgers; pool maintenance requires keeping both at once. This article deals with the link between the two, in particular how pH affects both; dosing tables, hardness reduction and turbidity removal are the subject of separate articles.
The table below gives the parameters that enter the operating specification of a pool project and the ranges that can be verified in the sources. For parameters where the source texts give no numerical range, the table does not invent one; it states in which direction the specification should limit them.
| Parameter | Unit | Target range | Effect on balance |
|---|---|---|---|
| pH | dimensionless | 7.2-7.6 (operating target 7.4; 7.2-7.8 accepted in the LSI approach) | Enters LSI directly; sets the HOCl/OCl- ratio of chlorine |
| Total alkalinity | mg/L CaCO3 | 80-120 | Buffers pH; factor D in LSI |
| Calcium hardness | mg/L CaCO3 | 200-400 | Factor C in LSI; if low, the water dissolves scale |
| Cyanuric acid | mg/L | No numerical range in the source text; an upper limit is written in the specification and accumulation is monitored | Extends chlorine half-life 4-6 times; does not enter LSI |
| Free chlorine | mg/L | Specification value; shock target 10 mg/L | Disinfection; indirect effect on pH through the chlorine product |
| Combined chlorine (chloramine) | mg/L | Lowest value achievable | Source of odour and irritation; burned off by shocking |
| TDS | mg/L | Specification value; monitored against the source water value | Factor A in LSI; as it rises, pHs falls |
| Temperature | °C | By pool type (set in the project) | Factor B in LSI; scaling tendency rises as the water warms |
Values should be read as mg/L CaCO3 equivalent; in the pool sector ppm CaCO3 and mg/L CaCO3 are the same quantity, and dividing by 50 converts to meq/L. Calcium hardness enters the LSI calculation as the CaCO3 equivalent, which is 2.5 times the ion concentration, rather than as the ion concentration itself.
The two concepts most often confused on site are pH and total alkalinity. pH is a logarithmic scale showing the hydrogen ion concentration of the water at that moment. Total alkalinity measures how much the pH of the water will resist when acid is added, that is, its buffer capacity; by the source definition it is 'the capacity of water to resist acidification' and should not be confused with basicity. In pool water this capacity is provided by bicarbonate and carbonate ions.
The practical consequence is this: in a pool with 40 mg/L alkalinity the pH can jump from 7.2 to 7.9 within the day; in a pool taking the same load at 100 mg/L alkalinity the pH moves by a few hundredths. If the operator corrects the pH with acid every day and finds it high again the next day, the problem is alkalinity, not pH. The alkalinity article stresses that adding or removing carbon dioxide does not change alkalinity but does change pH; fixtures that drive off CO2, such as waterfalls, raise pH while leaving alkalinity constant. This is why, among pool chemicals, sodium bicarbonate is sold separately as an 'alkalinity increaser' and sodium carbonate as a 'pH increaser'.
Balance and disinfection terms
- Langelier Saturation Index (LSI)
- The difference between the measured pH and the pH at which the water would be saturated with CaCO3 (pHs). Developed by Wilfred Langelier in 1936; LSI = pH - pHs.
- pHs (saturation pH)
- The pH at which the water would be in equilibrium with calcium carbonate at given temperature, TDS, calcium hardness and alkalinity values. Source formula: pHs = (9.3 + A + B) - (C + D).
- Hypochlorous acid (HOCl)
- The main disinfecting species that chlorine forms in water; pKa value 7.53. Under standard conditions it is a stronger oxidant than chlorine gas.
- Hypochlorite ion (OCl-)
- The deprotonated form of HOCl. As pH rises, the share of chlorine in this form increases; in basic solution effectively only OCl- is present.
- Combined chlorine (chloramine)
- Compounds formed by the reaction of chlorine with nitrogenous waste such as urea; measured as the difference between total chlorine and free chlorine.
- Cyanuric acid (CYA)
- A stabiliser in equilibrium with free chlorine that releases chlorine slowly; it prevents sunlight from consuming chlorine rapidly and accumulates as trichlor is used.
To calculate LSI, pHs is found first. The source formula has four factors: A = (log10[TDS] - 1) / 10; B = -13.12 x log10(°C + 273) + 34.55; C = log10[Ca, mg/L CaCO3] - 0.4; D = log10[alkalinity, mg/L CaCO3]. Then pHs = (9.3 + A + B) - (C + D) and LSI = measured pH - pHs. The source gives factor B as 2.09 at 25 °C and 1.09 at 82 °C; the table shows the intermediate values at pool temperatures and the other factors for typical pool water.
| Factor | Input value | Calculation | Result |
|---|---|---|---|
| A (TDS) | 1,000 mg/L | (3.000 - 1) / 10 | 0.20 |
| B (temperature) | 25 °C | -13.12 x log10(298) + 34.55 | 2.09 |
| B (temperature) | 28 °C | -13.12 x log10(301) + 34.55 | 2.03 |
| B (temperature) | 30 °C | -13.12 x log10(303) + 34.55 | 1.99 |
| C (Ca hardness) | 250 mg/L | log10(250) - 0.4 | 2.00 |
| C (Ca hardness) | 400 mg/L | log10(400) - 0.4 | 2.20 |
| D (alkalinity) | 100 mg/L | log10(100) | 2.00 |
Worked example: for pool water at 28 °C, TDS 1,000 mg/L, calcium hardness 250 mg/L, alkalinity 100 mg/L and measured pH 7.4, pHs = (9.3 + 0.20 + 2.03) - (2.00 + 2.00) = 7.53; LSI = 7.4 - 7.53 = -0.13. The source states that values between -0.5 and +0.5 show no marked dissolving or depositing behaviour; this water is considered balanced. If in the same pool the pH rises to 7.8, alkalinity to 150 mg/L, hardness to 400 mg/L, temperature to 30 °C and TDS to 1,500 mg/L, then pHs = (9.3 + 0.22 + 1.99) - (2.20 + 2.18) = 7.13 and LSI = +0.67: the water scales, and lime builds up in the exchanger and the grout. Conversely, the combination pH 7.0, alkalinity 60 mg/L, hardness 150 mg/L, 26 °C and TDS 800 mg/L gives pHs = 8.01 and LSI = -1.01: the water is corrosive and dissolves calcium out of the concrete pool plaster.
The three examples show that balance is built from the combination; in a heated pool project, the water going from 28 °C to 34 °C raises the LSI by about 0.1 without any chemical being added.
Whatever form chlorine is added to the water in, the result is hypochlorous acid (HOCl), and HOCl partly dissociates in water into the hypochlorite ion (OCl-): HOCl <=> H+ + OCl-. The pKa of the dissociation is 7.53; at pH 7.53 half of the chlorine is HOCl and half is OCl-. The source states that at neutral pH the composition is about 75 percent HOCl and 25 percent hypochlorite, while in basic solution effectively only OCl- remains. For pool water this means: free chlorine measured at pH 7.2 contains markedly more HOCl than the same reading at pH 7.8. The test kit shows the same figure in both cases; what reveals the difference is the pH.
The choice of pool chemicals affects this balance from two directions. Sodium and calcium hypochlorite push the pH up as they dissolve, while trichlor and dichlor tablets are acidic and pull pH and alkalinity down. A pool using trichlor needs regular alkalinity increaser, a pool using hypochlorite needs regular acid dosing; the choice of disinfectant also sets the balance side.
Cyanuric acid and combined chlorine: two separate accumulation problems
- Cyanuric acid is in equilibrium with free chlorine and releases chlorine slowly; the source states that the half-life of the active chlorine residual is thereby extended 4 to 6 times. In outdoor pools this is the practical way to reduce loss to sunlight.
- The same equilibrium works in reverse: chlorine bound to cyanuric acid appears in the free chlorine reading, but its reaction rate drops; as cyanuric acid rises, the same free chlorine value carries less immediate disinfecting power. Since the sources give no numerical threshold, the upper limit is written per project.
- As trichlor tablets dissolve, cyanuric acid accumulates in the pool; evaporation removes water but not cyanuric acid, so the concentration rises instead. The way to lower the accumulation is partial water replacement; it does not break down chemically.
- Combined chlorine (chloramine) forms from the reaction of chlorine with urea and other nitrogenous waste and accumulates under insufficient chlorination; the 'chlorine smell' is the smell of chloramine, not of free chlorine.
- Chloramines are broken down by superchlorination (shock); the source gives shocking every two weeks in summer with a 10 mg/L chlorine target as an example.
Because the parameters depend on each other, the correction order changes the result: total alkalinity first, then pH, then calcium hardness. A pH set before alkalinity is corrected drifts in the absence of a buffer; an LSI calculated before hardness is corrected gives the wrong target pH. Cyanuric acid and TDS are parameters that are monitored rather than adjusted: they only rise, and the only correction is water replacement. This order is the skeleton of the pool maintenance programme and is also applied as the column order on the pool water measurement record sheet.
Items for the specification and operating plan
- Target LSI range: between -0.3 and +0.3, acceptance limit -0.5 to +0.5. The obligation to correct when the water leaves the band stated by the source is written as a specification clause.
- Measurement frequency: pH and free/combined chlorine every day, alkalinity and hardness once a week, cyanuric acid and TDS once a month; the record sheet has an LSI column.
- The correction order (alkalinity, pH, hardness) and a waiting time of one full circulation turnover between doses are written into the plan.
- The pH counter-dose is specified together with the chlorine product: alkalinity increaser stock for trichlor, acid stock for hypochlorite.
- For cyanuric acid, the partial water replacement ratio when the upper limit is reached, and for TDS the source water reference value, are defined.
- In heated pools the target pH and alkalinity are recalculated with the temperature correction (factor B).
The saturation index was developed by Wilfred Langelier in 1936 to predict whether a protective calcium carbonate film would form on the pipes of drinking water networks. Water with a slightly positive index leaves a thin lime layer on the inner pipe surface and isolates the metal from the water; water with a negative index dissolves that layer. The same logic was carried into the pool construction sector, because a pool also has surfaces to protect: cement-based plaster and grout, the mortar under the tiles, stainless steel ladders and nozzles, the heater exchanger.
The adaptation for pool construction brings two differences. The first is temperature: mains water is around 10-15 °C while pool water is between 26-34 °C, and factor B carries that difference. The second is TDS: pool water accumulates dissolved solids through evaporation and chemical addition, and factor A must be re-taken every season. The Swimming pool sanitation article notes that pool pH is kept at 7.2-7.8 in the LSI approach and at 7.8-8.2 in the alternative approach called the Hamilton index; the difference comes from which side is given more weight, the HOCl share of chlorine or the scaling tendency. A pool project should state in its specification which index it takes as the basis.
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References
- 1.Langelier saturation index — Wikipedia, 2026
- 2.Hypochlorous acid — Wikipedia, 2026
- 3.Cyanuric acid — Wikipedia, 2026
- 4.Swimming pool sanitation — Wikipedia, 2026
- 5.Alkalinity — Wikipedia, 2026
- 6.Trichloroisocyanuric acid — Wikipedia, 2026
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Book a free site surveyNo. Balance describes whether the water is saturated with respect to calcium carbonate (LSI); disinfection concerns free chlorine and the HOCl share. The common parameter linking the two is pH: it enters the LSI and also sets the proportion of HOCl, the effective form of chlorine.
Çilek Havuz Content & Technical Team
The source states that LSI values between -0.5 and +0.5 show no marked dissolving or depositing behaviour. The operating target is written as -0.3 to +0.3. Water drifting to the negative side dissolves lime from the finish, water drifting to the positive side deposits scale in the exchanger and the grout.
Çilek Havuz Content & Technical Team
The pH of human tears is 7.4, and the source gives this value as the ideal set point for a pool. 7.4 is also just below 7.53, the pKa of HOCl; more than half of the chlorine stays in the effective HOCl form.
Çilek Havuz Content & Technical Team
Cyanuric acid does not evaporate and does not break down under pool conditions; trichlor and dichlor products add a little more with every dose. The only way to lower it is partial water replacement. The specification should state the upper limit and the share of water to be replaced when it is reached.
Çilek Havuz Content & Technical Team
Alkalinity is the buffer for pH. A pH correction made without a buffer is lost after one circulation turnover, and the acid or base is wasted. After alkalinity has been brought into the 80-120 mg/L band, pH is adjusted, calcium hardness is corrected last, and the LSI is recalculated.
Çilek Havuz Content & Technical Team

