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TECHNICAL ASSESSMENT OF PRODUCED WATER TREATMENT TECHNOLOGIES

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TECHNICAL ASSESSMENT OF PRODUCED WATER TREATMENT TECHNOLOGIES ( technical-assessment-produced-water-treatment-technologies )

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RPSEA Project 07122-12 TECHNICAL ASSESSMENT OF PRODUCED WATER TREATMENT TECHNOLOGIES 1st Edition FO membranes are capable of rejecting all particulate matter and almost all dissolved constituents (greater than 95% rejection of TDS). These attributes also allow FO to achieve very high theoretical recoveries while minimizing energy and chemical demands. An additional benefit of FO is that the process occurs spontaneously, without the need for applied hydraulic pressure. The hydraulic pressure applied in pressure driven membrane processes is responsible for compacting foulants onto the membrane, which substantially intensifies irreversible flux decline. Fouling layers that accumulate on FO membranes may be readily removed with cleaning (e.g., increasing cross-flow velocity, osmotic backwashing) or with chemicals, and irreversible flux decline is minimized [67, 72]. FO processes are capable of operating with feed TDS ranging from 500 mg/L to more than 35,000 mg/L, and may achieve recoveries in excess of 96% when treating brackish water [67]. FO membranes may be packaged in flat sheet or spiral-wound configurations. These packages allow for relatively small process footprints, but are still not optimized to the extent of pressure driven processes. Osmotically driven membrane processes have not yet been tested on produced waters. However, multiple lab scale experiments have been conducted with FO, and have utilized feed water supplies ranging from seawater and brackish water to municipal and industrial wastewater [67, 73-76]. FO has also been employed in a pilot and full-scale studies with industrial and municipal wastewaters, but the FO process was coupled with RO to reconcentrate the draw solution (see Hybrid FO/RO systems). A summary of the technical assessment for FO is listed in Table 17. Table 17. Summary of technical assessment of FO Criteria Status of technology Description/Rationale Emerging osmotically driven membrane technology. FO has not been previously employed for produced water treatment. Feed water quality bins TDS application range is controlled by the osmotic pressure differential between the feed solution and draw solution. The TDS range is between 500 mg/L to greater than 35,000 mg/L. FO has equivalent solute rejection performance to existing pressure driven processes for monovalent and divalent electrolytes, metals, and organics. Product water quality The product of FO is a diluted draw solution (typically composed of NaCl). To obtain pure water from the process a secondary system is required to extract pure water from the draw solution, and to reconcentrate the draw solution. This is typically accomplished with RO. FO membranes have similar solute rejection as NF (>90% TDS, >80% ammonia, low rejection of boron). Recovery Product water recoveries have exceeded 96% in hybrid RO/FO systems. Energy use FO is an osmotically driven process that occurs spontaneously without the need for substantial energy input. The process requires only enough power to circulate the draw solution and feed solution across the FO membrane. 43

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