Periodic feedwater reversal and air sparging as antifouling strategies in reverse electrodialysis

Renewable energy can be generated using natural streams of seawater and river water in reverse electrodialysis (RED). The potential for electricity production of this technology is huge, but fouling of the membranes and the membrane stack reduces the potential for large scale applications. This research shows that, without any specific antifouling strategies, the power density decreases in the first 4 h of operation to 40% of the originally obtained power density. It slowly decreases further in the remaining 67 days of operation. Using antifouling strategies, a significantly higher power density can be maintained. Periodically switching the feedwaters (i.e., changing seawater for river water and vice versa) generates the highest power density in the first hours of operation, probably due to a removal of multivalent ions and organic foulants from the membrane when the electrical current reverses. In the long term, colloidal fouling is observed in the stack without treatment and the stack with periodic feedwater switching, and preferential channeling is observed in the latter. This decreases the power density further. This decrease in power density is partly reversible. Only a stack with periodic air sparging has a minimum of colloidal fouling, resulting in a higher power density in the long term. A combination of the discussed antifouling strategies, together with the use of monovalent selective membranes, is recommended to maintain a high power density in RED in short-term and long-term operations.

Fouling in reverse electrodialysis under natural conditions

Renewable energy can be generated from mixing salt water and fresh water in reverse electrodialysis. The potential for energy generation from mixing seawater and river water is enormous. To investigate the effect of fouling when such natural feed waters are used, the performance of three different setups for reverse electrodialysis was evaluated for 25 days using seawater and river water as feed water, with no other (pre-)treatment than a 20 μm filter. Due to the absence of other anti-fouling treatments, a mixture of fouling is observed on the membranes, composed of remnants of diatoms, clay minerals, organic fouling and scaling. The fouling type was dependent on the different membrane types. The anion exchange membranes attract mainly diatoms and clay minerals, whereas scaling was only found on the cation exchange membranes. As a reference, plastic sheets without charge were used, which results in significant cleaner surfaces. Additionally, the setups without spacers in between the membranes (i.e. profiled membranes) appear significant less sensitive to fouling. This was quantified by the pressure drop over the feed waters and the power density obtained from the membrane piles. The pressure drop increases four times slower and the power density remains higher when profiled membranes are use instead of flat membranes with spacers. Although the obtained power density reduced with approximately 40% in the first day under these conditions, caused by organic fouling, several strategies are available to maintain a high power output using reverse electrodialysis.