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    Glyphosate Removal from Drinking Water

    Source: Journal of Environmental Engineering:;1993:;Volume ( 119 ):;issue: 006
    Author:
    Thomas F. Speth
    DOI: 10.1061/(ASCE)0733-9372(1993)119:6(1139)
    Publisher: American Society of Civil Engineers
    Abstract: Activated‐carbon, oxidation, conventional‐treatment, filtration, and membrane studies are conducted to determine which process is best suited to remove the herbicide glyphosate from potable water. Both bench‐scale and pilot‐scale studies are completed. Computer models are used to evaluate the results. The activated‐carbon results show that glyphosate adsorbs very strongly in distilled water, but has a much lower capacity in Ohio River water. The jar‐test studies with an alum coagulant show that as turbidity is removed, so is glyphosate. The majority of the glyphosate removal occurs as turbidity is reduced below 2 nephelometric turbidity units (NTUs). Powdered‐activated‐carbon treatment is ineffective. Ultrafiltration membranes and 0.45 μm filters do not remove glyphosate in Ohio River water even though the effluent turbidity is reduced below 0.2 NTU. The oxidation results indicate that glyphosate is easily destroyed by chlorine and ozone. Chlorine dioxide, permanganate, and hydrogen peroxide are less successful. These conventional‐treatment and adsorption results are confirmed by pilot‐scale studies.
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      Glyphosate Removal from Drinking Water

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    http://yetl.yabesh.ir/yetl1/handle/yetl/41854
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    contributor authorThomas F. Speth
    date accessioned2017-05-08T21:11:01Z
    date available2017-05-08T21:11:01Z
    date copyrightNovember 1993
    date issued1993
    identifier other%28asce%290733-9372%281993%29119%3A6%281139%29.pdf
    identifier urihttp://yetl.yabesh.ir/yetl/handle/yetl/41854
    description abstractActivated‐carbon, oxidation, conventional‐treatment, filtration, and membrane studies are conducted to determine which process is best suited to remove the herbicide glyphosate from potable water. Both bench‐scale and pilot‐scale studies are completed. Computer models are used to evaluate the results. The activated‐carbon results show that glyphosate adsorbs very strongly in distilled water, but has a much lower capacity in Ohio River water. The jar‐test studies with an alum coagulant show that as turbidity is removed, so is glyphosate. The majority of the glyphosate removal occurs as turbidity is reduced below 2 nephelometric turbidity units (NTUs). Powdered‐activated‐carbon treatment is ineffective. Ultrafiltration membranes and 0.45 μm filters do not remove glyphosate in Ohio River water even though the effluent turbidity is reduced below 0.2 NTU. The oxidation results indicate that glyphosate is easily destroyed by chlorine and ozone. Chlorine dioxide, permanganate, and hydrogen peroxide are less successful. These conventional‐treatment and adsorption results are confirmed by pilot‐scale studies.
    publisherAmerican Society of Civil Engineers
    titleGlyphosate Removal from Drinking Water
    typeJournal Paper
    journal volume119
    journal issue6
    journal titleJournal of Environmental Engineering
    identifier doi10.1061/(ASCE)0733-9372(1993)119:6(1139)
    treeJournal of Environmental Engineering:;1993:;Volume ( 119 ):;issue: 006
    contenttypeFulltext
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