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Membrane and Desalination Technologies - TCE Moodle Website

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466 J. Qin <strong>and</strong> K.A. Kekre<br />

Fig. 10.17. Conductivity of RO feed <strong>and</strong> permeate vs. time from November 2003 to February 2004 (46).<br />

Fig. 10.18. pH of RO feed <strong>and</strong> permeate vs. time from November 2003 to February 2004 (46).<br />

was replaced <strong>and</strong> CIP on the RO membranes was conducted on 6 January 2004, the permeate<br />

conductivity recovered to 35–75 mS/cm. At the end of the study, the salt rejection of RO<br />

membrane remained 96%, indicating that the RO membrane had performed well <strong>and</strong> tolerated<br />

organics from industrial wastewater.<br />

Figure 10.18 shows pH (online) of the RO feed <strong>and</strong> permeate as a function of time from<br />

November 2003 to February 2004. It can be seen that the RO feed pH was generally in the<br />

range of 6.8–7.6. The RO permeate pH ranged of 5.5–6.6, which was 1.0–1.3 unit lower than<br />

that of the RO feed. The situation of a lower permeate pH than the feed pH in an RO process<br />

appears to be quite a common occurrence in water <strong>and</strong> wastewater treatment (18, 48–51),<br />

which has been explained by the influence of HCO 3 elsewhere (50–51).

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