Desalination of Brackish Water Reverse Osmosis

Desalination of Brackish Water Reverse Osmosis

Desalination of Brackish Water Reverse Osmosis

Is already widespread in the mid-eighties when the RO membrane manufacturer developed a strong membrane that can withstand cleaning, biofouling and high operating pressure for years.

We manufacture both skid mounted and containerized BWRO systems, tailored to your needs.

We can analyze water samples and design the right system according to your needs.

Problems With Reverse Osmosis

Scaling occurs on Desalination of Brackish Water Reverse Osmosis (RO) membranes) when the concentration of scale-forming species exceeds saturation, producing additional solids within the Desalination of BWRO feedwater. Scalants include such chemical species as calcium carbonate, calcium sulfate, barium sulfate, strontium sulfate, and reactive silica. Since these species have very low solubilities, they are difficult to remove from BWRO (RO membranes). Scaling decreases the effectiveness of the membranes in reducing the solids and causes more frequent cleanings. A scale on a membrane provides nucleation sites that increase the rate of formation of additional scale.

Methods to minimize scaling

Magnesium hydroxide tends to absorb silica, another scalant.  Another softening procedure involves zeolite in an ion exchange process.
Often used with acidification, or by itself, are antiscalants. Antiscalants are chemicals added to wastewater to minimize scale carbonate or sulfate based scale. They consist of acrylates and phosphonates which inhibit the precipitation of carbonate or sulfanates.

Methods to prevent fouling

The second problem with Desalination of Desalination of Brackish Water Reverse Osmosis is with the fouling of membranes. Fouling occurs when suspended solids, microbes and organic material deposit on the surface of the membrane. Another problem is from colloidal sulfur, which when oxidized from H2S can foul RO membranes.
Coagulation is one technique that neutralizes the negative surface of the suspended solids, allowing the particles to cometogether. These large particles are then easy to remove from the water using filtration. The most common coagulants used are cationic polymers, inorganic salts, and aluminum and iron salts. Inorganic solvents tend to form large particles, while catonionic polymers require much less product for coagulation. Similar to coagulation is the clarification method, which destablizes suspended particles through charge neutralization. This is generally done by oxidizing iron and manganese and physically removing the precipitates in the manganese greensand bed.