利用差分光谱法研究硬度离子Ca2+/Mg2+对混凝剂铁盐与溶解性有机物络合的影响

谢亚萍, 程继夏, 晏明全. 利用差分光谱法研究硬度离子Ca2+/Mg2+对混凝剂铁盐与溶解性有机物络合的影响[J]. 环境工程学报, 2019, 13(5): 1056-1062. doi: 10.12030/j.cjee.201912209
引用本文: 谢亚萍, 程继夏, 晏明全. 利用差分光谱法研究硬度离子Ca2+/Mg2+对混凝剂铁盐与溶解性有机物络合的影响[J]. 环境工程学报, 2019, 13(5): 1056-1062. doi: 10.12030/j.cjee.201912209
XIE Yaping, CHENG Jixia, YAN Mingquan. Effect of hardness cations on the complexation between coagulant ferric ion and dissolved organic matter by differential UV-visible absorbance spectroscopy[J]. Chinese Journal of Environmental Engineering, 2019, 13(5): 1056-1062. doi: 10.12030/j.cjee.201912209
Citation: XIE Yaping, CHENG Jixia, YAN Mingquan. Effect of hardness cations on the complexation between coagulant ferric ion and dissolved organic matter by differential UV-visible absorbance spectroscopy[J]. Chinese Journal of Environmental Engineering, 2019, 13(5): 1056-1062. doi: 10.12030/j.cjee.201912209

利用差分光谱法研究硬度离子Ca2+/Mg2+对混凝剂铁盐与溶解性有机物络合的影响

  • 基金项目:

    国家自然科学基金资助项目 51578007

    国家自然科学基金资助项目(51578007)

Effect of hardness cations on the complexation between coagulant ferric ion and dissolved organic matter by differential UV-visible absorbance spectroscopy

  • Fund Project:
  • 摘要: 硬度离子Ca2+/Mg2+在水体中广泛存在,而其对水处理混凝工艺去除溶解性有机物(DOM)的影响并不是很清楚,这主要是由于缺乏可用于表征混凝环境条件下DOM、混凝剂、硬度离子之间相互作用过程的方法。采用差分光谱法,定量表征在pH为7时Ca2+或Mg2+对混凝剂Fe3+与DOM络合过程的影响。结果表明,Ca2+或Mg2+的存在会显著影响Fe3+与DOM的络合过程,随着Ca2+或Mg2+的浓度增大,对Fe3+与DOM络合产生的抑制越显著,尤其是Mg2+。研究为深入认识混凝去除DOM的机理提供了新方法与新视角。
  • 加载中
  • [1] 李悦宁, 贺凯, 王婷等. 日本消毒副产物及其前体物的现状及研究进展[J]. 环境化学, 2018, 37(8): 1820-1830.
    [2] 赵玉丽, 李杏放. 饮用水消毒副产物: 化学特征与毒性[J]. 环境化学, 2011, 30(1): 20-33.
    [3] GAO B Y, WANG Y, YUE Q Y, et al. The size and coagulation behavior of a novel composite inorganic-organic coagulant[J]. Separation & Purification Technology, 2008, 62(3): 544-550.
    [4] 杨雪. 新生态三价铁混凝处理松花江水的效果与机理研究[D]. 哈尔滨: 哈尔滨工业大学, 2011.
    [5] 张华, 崔柳华, 吴百春. 国内外除硬技术现状研究[J]. 工业水处理, 2011, 31(12): 5-8.
    [6] AHN W Y, KALINICHEV A G, CLARK M M. Supramolecular aggregation of natural organic matter promoted by complexation with Ca2+, Mg2+, and Na+ ions in aqueous solutions[J]. Geochimica Cosmochimica Acta, 2008, 72(12): A10.
    [7] LU Y F, ALLEN H E. Characterization of copper complexation with naturaldissolved organic matter (DOM)-link to acidic moieties of DOM and competition by Ca and Mg[J]. Water Research, 2002, 36(20): 5083-5101.
    [8] STUMM W, MORGAN J J. Aquatic chemistry: An introduction emphasizing chemical equilibria in natural waters[J]. Ecological Modelling, 1981, 19(3): 227-230.
    [9] USEPA. Enhanced coagulation and enhanced precipitative softening guidance manual[S]. Washington D C: EPA, Office of Water and Drinking Ground Water, 1998.
    [10] MOTA A, RATO C, BRAZIA C, et al. Competition of Al3+ in complexation of humic matter with Pb2+: A comparative study with other ions[J]. Environmental Science & Technology, 1996, 30(6): 1970-1974.
    [11] NORDEN M, EPHRAIM J H, ALLARD B. Europium complexation by an aquatic fulvic acid: Effects of competing ions[J]. Talanta, 1997, 44(5): 781-786.
    [12] TOWN R M, POWELL H K J. Ion-selective electrode potentiometric studies on the complexation of copper(II) by solid-derived humic and fulvic acids[J]. Analytica Chimica Acta, 1993, 279(2): 221-233.
    [13] GAO Y, YAN M Q, KORSHIN G. Effects of calcium on the chromophores of dissolved organic matter and their interactions with copper[J]. Water Research, 2015, 81: 47-53.
    [14] YAN M Q, KORSHIN G. Comparative examination of effects of binding of different metals on chromophores of dissolved organic matter[J]. Environmental Science & Technology, 2014, 48(6): 3177-3185.
    [15] MAURICE P A. Special issue introduction: Dissolved organic matter from the suwannee river (GA, USA)[J]. Environmental Engineering Science, 2015, 32(1): 1-3.
    [16] ZHOU Y X, YAN M Q, LIU R P, et al. Investigating the effect of hardness cations on coagulation: The aspect of neutralisation through Al(III)-dissolved organic matter (DOM) binding[J]. Water Research, 2017, 115: 22-28.
    [17] YAN M Q, MA J, JI G D. Examination of effects of Cu(II) and Cr(III) on Al(III) binding by dissolved organic matter using absorbance spectroscopy[J]. Water Research, 2016, 9: 84-90.
    [18] YAN M Q, DRYER D, KORSHIN G, et al. In situ study of binding of copper by fulvic acid: Comparison of differential absorbance data and model predictions[J]. Water Research, 2013, 47(2): 588-596.
    [19] YAN M Q, LI D C, GAO J F, et al. Influence of chlorination on metal binding by dissolved organic matter: A study using log-transformed differential spectra[J]. Chemosphere, 2014, 103: 290-298.
    [20] YAN M Q, LU Y J, GAO Y, et al. In-situ investigation of interactions between magnesium ion and natural organic matter[J]. Environmental Science & Technology, 2015, 49(14): 8323-8329.
  • 加载中
计量
  • 文章访问数:  3325
  • HTML全文浏览数:  3250
  • PDF下载数:  127
  • 施引文献:  0
出版历程
  • 刊出日期:  2019-06-03

利用差分光谱法研究硬度离子Ca2+/Mg2+对混凝剂铁盐与溶解性有机物络合的影响

  • 1. 长安大学环境科学与工程学院,西安 710054
  • 2. 北京大学环境科学与工程学院,教育部水沙科学重点实验室,北京 100871
基金项目:

国家自然科学基金资助项目 51578007

国家自然科学基金资助项目(51578007)

摘要: 硬度离子Ca2+/Mg2+在水体中广泛存在,而其对水处理混凝工艺去除溶解性有机物(DOM)的影响并不是很清楚,这主要是由于缺乏可用于表征混凝环境条件下DOM、混凝剂、硬度离子之间相互作用过程的方法。采用差分光谱法,定量表征在pH为7时Ca2+或Mg2+对混凝剂Fe3+与DOM络合过程的影响。结果表明,Ca2+或Mg2+的存在会显著影响Fe3+与DOM的络合过程,随着Ca2+或Mg2+的浓度增大,对Fe3+与DOM络合产生的抑制越显著,尤其是Mg2+。研究为深入认识混凝去除DOM的机理提供了新方法与新视角。

English Abstract

参考文献 (20)

目录

/

返回文章
返回