首页> 外文期刊>Water >Effect of Organic Matter on Cr(VI) Removal from Groundwaters by Fe(II) Reductive Precipitation for Groundwater Treatment
【24h】

Effect of Organic Matter on Cr(VI) Removal from Groundwaters by Fe(II) Reductive Precipitation for Groundwater Treatment

机译:Fe(II)还原沉淀法处理地下水中有机物对地下水中Cr(VI)的去除

获取原文
           

摘要

Due to its toxicity, Cr(VI) is undesirable in groundwater. Its chemical reduction to Cr(III) species, followed by precipitation is the most widely practiced treatment technique for the removal of Cr(VI) from polluted waters. The resulting Cr(III) species present low solubility, is much less toxic, and can be subsequently removed either by precipitation, or by adsorption onto iron oxy-hydroxides and co-precipitation. The effects of several parameters, such as the pH value of water to be treated, the applied Fe(II) dose, and the presence of appropriate mineral surfaces, are well investigated and understood. However, the impact of the presence of humic acids (HAs) in this process has only been considered by rather few studies. The main aim of this study was to determine the effect of humic substances on Fe(II) reductive precipitation of Cr(VI) within a pH range relevant for drinking water treatment. Jar test experiments were performed, using artificial groundwater of defined composition and initial Cr(VI) concentration 100 μg/L, ferrous sulphate dosages 0.25–2 mg Fe(II)/L, and pH values 6.5–8. It was found that Cr(VI) and total chromium (Cr(total)) can be reliably removed in the absence of HAs in the tested pH range with the addition of Fe(II) dosage of 1 mg Fe(II)/L. Further on, the results indicated that the reduction of Cr(VI) is only slightly affected by the presence of HAs. However, increased residual total Cr concentrations were found at lower Fe(II) dosages and/or higher pH values. Additionally, the removal of the Cr(III) species formed during Cr(VI) reduction was strongly inhibited by the presence of HAs under the examined experimental conditions, since residual concentrations higher than 60 μg/L were determined. The results of this study will have implications to the ongoing discussion of a new, stricter, European Union regulation limit, regarding the presence of total chromium in drinking water.
机译:由于其毒性,Cr(VI)在地下水中是不可取的。其化学还原成Cr(III)物种然后沉淀的方法是从污染水中去除Cr(VI)的最广泛实践的处理技术。所得的Cr(III)物质溶解度低,毒性低得多,可以随后通过沉淀或吸附在羟基氧化铁上并共沉淀除去。很好地研究和理解了几个参数的影响,例如待处理水的pH值,所施加的Fe(II)剂量以及适当的矿物表面的存在。但是,只有很少的研究才考虑到腐殖酸(HAs)在此过程中的影响。这项研究的主要目的是确定腐殖质对与饮用水处理有关的pH范围内的Cr(VI)的Fe(II)还原性沉淀Cr(VI)的影响。进行罐子试验实验,使用限定成分的人造地下水,初始Cr(VI)浓度为100μg/ L,硫酸亚铁的剂量为0.25-2 mg Fe(II)/ L,pH值为6.5-8。发现在添加的Fe(II)剂量为1 mg Fe(II)/ L的情况下,在测试pH范围内不存在HA的情况下,可以可靠地除去Cr(VI)和总铬(Cr(总))。此外,结果表明,HAs的存在仅对Cr(VI)的还原影响很小。但是,在较低的Fe(II)剂量和/或较高的pH值下,发现总残留Cr浓度增加。此外,在检测的实验条件下,HA的存在强烈抑制了Cr(VI)还原过程中形成的Cr(III)物种的去除,因为确定的残留浓度高于60μg/ L。这项研究的结果将对正在进行的有关饮用水中总铬含量的新的,更严格的欧盟法规限制的讨论产生影响。

著录项

相似文献

  • 外文文献
  • 中文文献
  • 专利
获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号