Abstract
This study investigated the feasibility of using granular activated carbon (GAC) to remove bromate (BrO3-) from drinking water through batch experiments, rapid small-scale column tests (RSSCT) and a pilot-scale study. The results indicated that the GAC capacity for BrO3- removal was dependent on the GAC surface characteristics and empty-bed contact time (EBCT). The GAC with a high number of basic groups and higher pHpzc values showed an increased BrO3- removal capacity. On the other hand, BrO3- removal was improved by increasing EBCT. In the GAC pilot plant, a GAC column (operating with 15 min EBCT) preload for 12 months achieved a BrO3- and assimilable organic carbon (AOC) removal rate ranging between 7 and 96 % and between 41 and 85 %, respectively. The amount of BrO3- removed was found to be proportional to the influent BrO3- concentration. Based on the results of our long-term experiment, the BrO3- and AOC removal rate during the transition from initial GAC to biological activated carbon (BAC) was calculated as 0.12 % w/w and 0.27 % w/w, respectively. However, the BrO3- removal rate apparently decreased with increasing operating time (after 3 months). This may be a result of the contribution of the bacterial biomass being adsorbed on the GAC surface which hindered BrO3- reduction by GAC, either by blocking the pores or adsorbing on the activated sites for BrO3- reduction. WaterSA Vol.30 (3) 2004: 369-375
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