US Salinity Lab thresholds · ESP ≥ 6% sodic, ≥ 15% strongly sodic

Exchangeable Sodium Percentage (ESP) Calculator: Exchangeable Na from CEC

Turn exchangeable sodium and cation exchange capacity from a lab report into ESP, sodium base saturation, and a dispersion verdict. Enter sodium as meq/100g, as ppm (mg/kg), or as a percentage of CEC, and read the classification with the amendments that follow from it.

Live ESPpercent of CEC –

Lab report entry

meq/100g (cmolc/kg)

meq/100g (cmolc/kg), pH 7 or as reported

ESP = exchangeable sodium ÷ CEC × 100. Both values must be on the same unit basis.

Result

Result · ESP
10.00%
Sodic
0%6%: sodic line15%: strongly sodic line100%
Exchangeable Na, meq/100g1.80
Exchangeable Na, mg/kg (ppm)413.8
CEC used, meq/100g18.00
Na as a fraction of CEC10.00%
Exchangeable Na, lb/acre (6-inch slice)927

Both inputs read as meq/100g, so ESP is a straight ratio: 1.80 ÷ 18.00 × 100.

Sodic (6 to 15%): sodium is high enough to deflocculate clay and block pores. Gypsum plus a leaching fraction usually restores structure: size the rate with the gypsum requirement calculator.

Exchangeable sodium percentage: the formula, the thresholds and the fix

ESP is the simplest sodicity number on a soil test: the share of the exchange complex occupied by sodium. It matters because sodium does not flocculate clay. Where calcium holds particles in crumbs, sodium pushes them apart, the crumbs disperse, and the same soil that drained last season now crusts, ponds and sets hard. Everything below is one ratio plus the consequences of that ratio.

1. The calculation, worked through

ESP (%) = (exchangeable Na+ ÷ CEC) × 100
exchangeable Na (meq/100g) = exchangeable Na (mg/kg) ÷ 229.9
exchangeable Na (mg/kg) = exchangeable Na (meq/100g) × 229.9

Worked example. A report lists exchangeable sodium at 1.8 meq/100g and CEC at 18 meq/100g. ESP = 1.8 ÷ 18 × 100 = 10.00%. Sodium occupies a tenth of the exchange sites, which lands in the sodic band: dispersion risk is real, but the structure is still recoverable with gypsum and drainage. The same report written as ppm would show 414 mg/kg, and 414 ÷ 229.9 returns the same 1.80 meq/100g.

2. Why 6% and 15% are the numbers people quote

ESPClassificationWhat is happening in the soil
0 – 6%Non-sodicSodium is dispersed harmlessly; structure and infiltration are governed by something else.
6 – 15%SodicClay begins to disperse on wetting; surface crusting, slower infiltration, seal-prone seedbeds.
> 15%Strongly sodicThe classic US Salinity Laboratory definition of an alkali soil: hard setting, poor aeration, most crops fail.

The 15% line comes from the US Salinity Laboratory's Diagnosis and Improvement of Saline and Alkali Soils (Handbook 60), where "alkali soil" was defined by ESP at or above 15. Field experience moved the practical threshold down: dispersion of many clay soils begins near 6%, which is why modern guidance treats 6% as the action line and 15% as the severity line. The calculator flags both.

3. ESP, SAR and sodium saturation are three views of the same problem

IndexSampleHow it is measuredWhen to use it
ESPSolid soilExchangeable Na ÷ CEC × 100The sodicity status of the field itself
Na saturationSolid soilSame ratio, expressed as base saturation of NaBase saturation work alongside Ca, Mg and K
SAR Irrigation waterNa ÷ √((Ca + Mg) / 2) in meq/LPredicting whether the water will cause sodicity

SAR describes the water you are applying; ESP describes the soil you already have. They track each other closely in the field, but they are not interchangeable, and a sodic soil under good water still needs gypsum. Calculate the incoming hazard with the SAR and CROSS calculator, and read the exchange complex as a whole in the base saturation calculator.

4. Unit conversions you will meet on a lab report

  • meq/100g (cmolc/kg) to ppm (mg/kg): multiply by 229.9, the equivalent weight of sodium (22.99 mg/meq) scaled by the 100 g basis.
  • ppm to meq/100g: divide by 229.9. Sodium at 230 mg/kg is 1.00 meq/100g.
  • Percent of CEC is already ESP. If your report lists "Na base saturation %", you do not need CEC at all.
  • lb/acre in the results assumes a 6-inch (15 cm) acre-slice at a bulk density near 1.3 g/cm³, about 2.24 million lb of soil per acre.

Units are the most common source of a tenfold sodicity error, so the calculator keeps the conversion visible rather than hiding it: switch the entry mode above and watch which rows recompute.

5. What to do once the number is above 6%

  1. Confirm the diagnosis. Re-run the test, check the CEC method (pH 7 versus measured), and rule out a saline soil where the problem is total salt rather than exchangeable sodium: ESP can sit low while ECe is high.
  2. Replace sodium with calcium. Gypsum (calcium sulphate) is the standard amendment where free lime is absent; in calcareous soils the lime already present is often enough once pH and drainage are right. Rate it from CEC and exchangeable sodium with the gypsum requirement calculator.
  3. Leach. Displaced sodium has to leave the profile. Apply the amendment, then enough water to move the displaced Na below the root zone, with a drainage plan if the water table is high.
  4. Rebuild structure. Organic matter, crop residues and traffic control at wet consistencies keep the recovered aggregates from re-dispersing. Then re-test at the same depth and season.

The full walkthrough, including how ESP appears alongside CEC and base saturation on a real report, is in exchangeable sodium percentage (ESP): what it is, how to calculate it and how to fix it.

References

  • Richards, L.A. (1954). Diagnosis and Improvement of Saline and Alkali Soils, USDA Agriculture Handbook No. 60 — source of the ESP ≥ 15% alkali-soil definition and the exchangeable sodium methods.
  • US Salinity Laboratory Staff and Brady, N.C. and Weil, R.R., The Nature and Properties of Soils — sodicity thresholds, dispersion and reclamation practice.
  • Rengasamy, P. (2006). "World salinity and sodicity problems", in Salinization of Land and Water Resources — the case for the 6% dispersion threshold.
  • Sumner, M.E. and Naidu, R. (1998). Sodic Soils: Distribution, Properties, Management, and Environmental Consequences, Oxford University Press.
Agronomic notice and disclaimer: The ESP calculator reports the ratio you enter. It does not diagnose the cause of poor structure, does not account for salinity (ECe), carbonate, or water table effects, and does not replace a full soil test with a local agronomist's interpretation. Amendment rates must be confirmed against material purity, application method and leaching capacity.

Sources and method: the publications this tool cites are listed in the calculator sources register, one table per calculator, with a link to each source that still answers and the formula this page prints kept as the primary record.