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Arsenic removal to < 1 μg L~(-1) by coprecipitation with in-situ generated pe(III) precipitates with and without advanced pre-oxidation

机译:通过与原位产生的PE(III)沉淀到原位生成的PE(III)沉淀到<1μgL〜(-1)砷去除(III),没有先进的预氧化

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The aim of this study is to investigate removal of low As concentrations from groundwater at a Drinking Water Treatment Plant (DWTP) in The Netherlands in order to achieve <1 μg L~(-1) As in produced drinking water.Two iron based emerging technologies,both relying on in-situ generated Fe(III) precipitates for As adsorption,were investigated.These include:1) Advanced Oxidation-Coprecipitation-Filtration (AOCF) and 2) Coprecipitation prior to ultrafiltration (C-UF).We show that most of the As removal occurs in the top half of a Rapid Sand Filter (RSF) bed.In this part we also observe the conversion of As(IIl) into As(V).The mechanism of As(III) oxidation to As(V) in the RSF is still not understood,however we hypothesize that either the manganese oxides or the biological activity in the filter bed may be responsible for this conversion.In agreement with this observation,we also notice that drinking water only contains As(V) and that the levels of As(III) are negligible.The experiments have shown that both AOCF and C-UF are promising emerging technologies to reduce arsenic levels to below 1 μg L~(-1) which is the agreed target in The Netherlands between the Dutch water companies.
机译:本研究的目的是调查荷兰饮用水处理厂(DWTP)的地下水的低至浓度的浓度,以实现<1μgL〜(-1),如生产的饮用水中的铸铁。基于熨斗的新兴研究了依赖于原位生成的Fe(III)沉淀为吸附的技术。这些包括:1)在超滤(C-UF)之前的晚期氧化 - 共沉淀过滤(AOCF)和2)共沉淀。我们展示即大部分作为拆卸在快速砂过滤器(RSF)床的上半部分中发生。在这部分方面,我们也观察到AS(II)的转换为(v)。作为(iii)氧化的机制(v)在RSF中尚未理解,然而,我们假设过滤床中的氧化锰或生物活性可能是这种转化的原因。在与这种观察中协议,我们还注意到饮用水仅含有( v)并且(III)的水平可以忽略不计。实验HAV E表明,AOCF和C-UF都希望出现新兴技术,以将砷水平降低到1μgL〜(-1)以下是荷兰水公司之间的荷兰商定的目标。

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