| Brackish groundwater from a well | Total dissolved solids (TDS), conductivity, hardness, alkalinity, silica, iron, manganese, sulfate, chloride, and pH. Test for seasonal variation where relevant. | Reduce dissolved salts to meet the intended drinking, process, or irrigation-water specification. | Well-water chemistry can vary by location and depth. Hardness, silica, iron, or manganese may require pretreatment to limit membrane scaling or fouling. | Well yield, drawdown, daily demand, operating hours, and any applicable drinking-water limits. |
| Surface water affected by brackish intrusion | TDS and conductivity, turbidity, suspended solids, organic matter, algae, and microbiological indicators, along with major ions. | Produce water with the required salt level while managing variable source-water quality. | Surface-water quality may change after rain, during seasonal turnover, or with tidal influence. Clarification or filtration may be needed ahead of RO. | Intake conditions, seasonal ranges, turbidity history, pretreatment needs, and required production during poor-water-quality periods. |
| Municipal or industrial water with elevated salinity | TDS, conductivity, hardness, alkalinity, silica, chloride, sulfate, residual disinfectants, and any process-specific contaminants. | Meet a defined product-water target for reuse, manufacturing, or another specified application. | Confirm compatibility with upstream chemicals and disinfectants. Some membrane materials can be damaged by oxidants such as free chlorine unless appropriately removed. | Existing treatment steps, feed pressure, flow rate, operating schedule, and the product-water specification from the end user or process. |
| Water from a source with variable or uncertain salinity | Repeated TDS or conductivity readings and laboratory analysis for the ions and foulants relevant to the application. | Maintain reliable product-water quality across the expected range of feed conditions. | Base the design on representative high and low feed conditions, not a single reading. Consider monitoring and operating controls suited to changing feed water. | Historical or seasonal data, maximum expected feed salinity, minimum source flow, and acceptable product-water variation. |
| Concentrated brackish water or a challenging high-salinity feed | TDS, complete major-ion profile, scaling potential, temperature, pH, and any contaminants that may affect recovery or membrane operation. | Recover usable water while managing concentrate disposal and operating constraints. | Higher salinity generally requires greater osmotic pressure and can reduce achievable recovery. A qualified design review should assess pressure limits, scaling risk, and concentrate handling. | Feed-water analysis, permitted discharge or disposal route, recovery objectives, energy limits, and applicable environmental requirements. |
| Any source intended for drinking water | Full laboratory analysis against the applicable local drinking-water requirements, including microbial and chemical parameters. | Meet applicable drinking-water standards after treatment and any required post-treatment. | RO removes many dissolved constituents but does not by itself establish that water is safe or compliant. Disinfection, remineralization, and routine verification may be needed. | Applicable jurisdictional standards, required daily volume, storage and distribution conditions, and a testing and maintenance plan. |
| Any source intended for irrigation | TDS or electrical conductivity, sodium, calcium, magnesium, chloride, boron, and alkalinity; assess soil and crop conditions too. | Provide water suitable for the crop, soil, and irrigation method. | Low salinity alone does not determine irrigation suitability. Sodium hazard and crop-specific sensitivity can influence the target and post-treatment needs. | Crop type, soil drainage, irrigation method, local water-quality guidance, and a plan for managing RO concentrate. |