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    Magnetic ion exchange drinking water treatment in a large-scale facility

    Access Status
    Fulltext not available
    Authors
    Warton, Benjamin
    Heitz, Anna
    Zappia, L.
    Franzmann, P.
    Masters, D.
    Joll, Cynthia
    Alessandrino, Michael
    Allpike, Bradley
    O'Leary, B.
    Kagi, Robert
    Date
    2007
    Type
    Journal Article
    
    Metadata
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    Citation
    Warton, Benjamin and Heitz, Anna and Zappia, Luke and Franzmann, Peter and Masters, David and Joll, Cynthia and Alessandrino, Michael and Allpike, Brad and O'Leary, Bernie and Kagi, Robert. 2007. Magnetic ion exchange drinking water treatment in a large-scale facility. American Water Works Association Journal 99 (1): pp. 89-101.
    Source Title
    American Water Works Association Journal
    ISSN
    15518833
    Faculty
    School of Science and Computing
    Faculty of Science and Engineering
    Department of Applied Chemistry
    URI
    http://hdl.handle.net/20.500.11937/23597
    Collection
    • Curtin Research Publications
    Abstract

    The MIEX (c) (Magnetic Ion Exchange) process, which employs an anion exchange resin for removal of dissolved organic carbon (DOC), was introduced at the Wanneroo Groundwater Treatment Plant in Western Australia in 2001. In this pilot-scale study we examined a range of operational parameters for optimisation of biofiltration of MIEX (R)-clarified waterl. Granular Activated Carbon (GAC) outperformed anthracite as a filter medium. Increasing the empty bed contact time (EBCT) from 8 to 16 minutes improved performance. The GAC biofilters removed up to 20% of DOC and up to 25% of Biodegradable Dissolved Organic Carbon (BDOC), once they had stabilised in biological mode. Chlorine demand was reduced by 51 to 55% and trihalomethane formation potential (THMFP) was reduced by 35 to 50% in GAC biofilter effluent waters at 16 minutes EBCT when compared with their MIEX (R)-treated influent water. GAC biofilters developed more biomass on the surface than anthracite biofilters and this was associated with the greatest BDOC and DOC removals. Interestingly, neither biofilters developed populations of protozoans. Use of chlorinated influent water severely restricted biomass development in all biofilters at surface. Biofilter treatment of chlorinated influent water resulted in the poorest removal of Assimilable Organic Carbon (AOC). Biofiltration improved the water quality of MIEX (R)-clarified waters.

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