RO • NF • Water Treatment

Advanced Salt Rejection Calculator

Analyze membrane rejection, passage, recovery, ion removal, pressure behavior, mass balance, stage performance, normalization, trends, and reportable operating results.

Calculator setup

hours
months

Units and reporting preferences

g/mol
Used for molar concentration conversion. Default represents NaCl.

Core water-quality inputs

1

Concentration measurements

2

Conductivity measurements

Flow, recovery, and mass balance

Leave one flow blank to solve it using Qf = Qp + Qc. Concentrate concentration can also be estimated from the salt mass balance.

Pressure and operating conditions

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%
%

The automatic temperature correction is a simplified comparison aid. Use manufacturer normalization software for contractual or warranty decisions.

Rated performance and thresholds

%
%
%
%

Individual ion rejection

IonChargeFeedPermeateUnitLive rejection
Sodium Na⁺ +1
Chloride Cl⁻ -1
Calcium Ca²⁺ +2
Magnesium Mg²⁺ +2
Potassium K⁺ +1
Sulfate SO₄²⁻ -2
Nitrate NO₃⁻ -1
Fluoride F⁻ -1
Bicarbonate HCO₃⁻ -1
Silica SiO₂ 0
Boron B 0
Ammonium NH₄⁺ +1
Phosphate PO₄³⁻ -3
Iron Fe varies
Manganese Mn varies

Stage-by-stage analysis

Use the same concentration and flow units selected above. Empty stage rows are ignored.

StageFeed concentrationPermeate concentrationFeed flowPermeate flow
1
2
3
4
5
6
7
8

Baseline and historical monitoring

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%

Notes and record options

Results appear above this form.
Session storage

Saved calculation history

No saved calculations are available in this session.

Formula reference

Salt rejection
R = (1 − Cp / Cf) × 100
Conductivity rejection
R = (1 − Kp / Kf) × 100
Salt passage
SP = Cp / Cf × 100 = 100 − R
Water recovery
Recovery = Qp / Qf × 100
Flow balance
Qf = Qp + Qc
Salt mass balance
CfQf = CpQp + CcQc
Concentration factor
CF = 1 / (1 − recovery as a decimal)
Required rejection
Rrequired = (1 − Ctarget / Cfeed) × 100

How to use this calculator

  1. Choose concentration or conductivity mode based on your available measurements.
  2. Select units before entering feed, permeate, concentrate, flow, pressure, and temperature data.
  3. Enter feed and permeate values from samples taken under stable operating conditions.
  4. Add feed and permeate flow to calculate recovery and complete the flow balance.
  5. Enter concentrate data when available for salt mass-balance checking.
  6. Add rated membrane data and custom thresholds for practical performance classification.
  7. Use the ion table when laboratory results are available for individual species.
  8. Add baseline values to identify meaningful performance changes.
  9. Review warnings, charts, and mass-balance closure before exporting or printing the report.

Understanding salt rejection performance

What salt rejection means

Salt rejection describes the percentage reduction between feed-water concentration and permeate concentration. A membrane with high rejection allows only a small fraction of dissolved salt into the product stream. The complementary result is salt passage, which shows the percentage crossing the membrane.

Rejection is not a universal membrane constant under every operating condition. It can change with feed composition, pressure, temperature, recovery, pH, membrane age, pretreatment, fouling, scaling, oxidation, mechanical damage, and sampling quality. Comparisons are strongest when measurements are normalized to consistent reference conditions.

Concentration and conductivity methods

Laboratory concentration data provides a direct basis for salt rejection. Conductivity is often faster and easier for routine plant checks. Conductivity-based rejection assumes the relationship between ionic concentration and conductivity remains reasonably comparable between the sampled streams.

Conductivity should not be treated as an exact replacement for complete ionic analysis. Different ions contribute differently to conductivity. Temperature compensation, instrument calibration, dissolved gases, pH, and sample handling can also affect measured values.

Recovery and concentrate behavior

Recovery measures how much feed water becomes permeate. Higher recovery reduces concentrate flow and increases the concentration of retained salts. This can raise osmotic pressure and scaling risk. It may also change observed rejection and element loading.

The ideal concentration factor is calculated from recovery. Real systems may depart from that ideal because of salt passage, blending, recirculation, sampling position, unequal stage loading, or measurement error. The mass-balance section helps expose such inconsistencies.

Individual ion rejection

Total dissolved solids can hide important chemical behavior. Calcium, sulfate, silica, boron, nitrate, and other species may have different passage rates. Nanofiltration membranes can show especially large differences between monovalent and multivalent ions.

Ion-specific results help evaluate product-water limits and scaling risks. They also support process troubleshooting when total conductivity appears acceptable but one regulated or operationally important species remains high.

Normalization and trend interpretation

Raw performance values should be compared carefully. Temperature, pressure, salinity, recovery, and membrane condition all influence output. Normalized performance attempts to remove expected operating-condition effects so long-term trends become clearer.

This application provides a simplified temperature adjustment and baseline comparison. It is intended for screening, education, and routine operational review. Manufacturer software or a validated engineering model should be used for warranty, design, contractual acceptance, and safety-critical decisions.

Common causes of declining rejection

Declining rejection may result from oxidant damage, abrasion, seal leakage, telescoping, poor interconnector seating, membrane aging, excessive pressure, biological attack, pH exposure, incompatible cleaning chemicals, or instrument problems. A sudden change often suggests leakage, damage, sampling error, or analyzer error.

A gradual change may indicate fouling, scaling, compaction, or aging. Review normalized flow and pressure drop alongside rejection. A complete diagnosis should include pretreatment records, differential pressure, cleaning history, feed chemistry, permeate quality, and vessel-level sampling.

Data-quality recommendations

Use calibrated instruments and consistent sampling points. Allow the system to stabilize before sampling. Record temperature, pressure, flow, recovery, pH, and conductivity at the same time. Rinse sample containers and avoid contamination.

Compare results against the correct membrane specification and its stated test conditions. A rated rejection value measured with one salt, concentration, pressure, temperature, pH, and recovery may not match field performance under different conditions.

Frequently asked questions

A good value depends on membrane technology, membrane model, feed chemistry, test conditions, system design, and product-water requirements. Compare normalized field performance with the applicable specification and a stable baseline.

Negative rejection occurs when the permeate measurement exceeds the feed measurement. Check units, sample labels, stabilization, instrument calibration, blending, recirculation, and possible contamination.

Conductivity can support fast operational checks when feed and permeate samples are comparable. It does not provide the same information as a complete ionic analysis and can be affected by temperature and ion composition.

Temperature changes water viscosity, permeate flux, diffusion, and salt passage. Raw values measured at different temperatures should not be compared without appropriate normalization.

High passage may indicate unfavorable operating conditions, membrane damage, seal leakage, oxidation, fouling, scaling, aging, or inaccurate measurements. Review normalized trends and vessel-level data.

The calculator applies the overall salt mass balance using feed, permeate, and concentrate flows. The estimate is only as reliable as the synchronized measurements supplied.

Common causes include unit errors, unsynchronized readings, inaccurate flowmeters, sampling from different operating states, concentration conversion assumptions, recirculation, or an incorrect concentrate value.

No. It provides performance calculations and screening insights. Complete design requires hydraulic modeling, membrane projections, feed analysis, scaling evaluation, pretreatment design, pressure-vessel configuration, and manufacturer limits.

No. The built-in correction is intentionally simplified. Use validated manufacturer or engineering normalization software for formal performance evaluation.

Enter feed and permeate values for each ion using the selected row unit. The calculator converts molar values using the stored molecular weight for that species.
Technical disclaimer: This calculator is an engineering aid, not a substitute for manufacturer projection software, laboratory analysis, professional design review, regulatory compliance testing, or site-specific operating procedures.

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Important Note: All the Calculators listed in this site are for educational purpose only and we do not guarentee the accuracy of results. Please do consult with other sources as well.