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金属矿山 ›› 2018, Vol. 47 ›› Issue (10): 178-183.

• 安全与环保 • 上一篇    下一篇

铁改性凹凸棒土(IMA)吸附去除Sb(Ⅲ)性能研究

刘爱平,黄阳,王维清,刘璟   

  1. 西南科技大学环境与资源学院,四川 绵阳621010
  • 出版日期:2018-10-15 发布日期:2018-11-09
  • 基金资助:

    *:四川省教育厅项目(编号:12zd1121),国家自然科学基金项目(编号:41772367)。

Adsorption Behaviors of Iron Mdified Attapulgite towards Sb(Ⅲ)

Liu Aiping,Huang Yang,Wang Weiqing,Liu Jing   

  1. College of Environment & Resources,South West University of Science & Technology,Mianyang 621010,China
  • Online:2018-10-15 Published:2018-11-09

摘要: 锑是一种有毒元素,对生物有机体有致癌性。我国锑矿区周围水体中锑含量远高于生活饮用水标准中规定的限定值。为寻求低成本处理含Sb(Ⅲ)废水的有效方法,采用FeCl3·6H2O溶液改性后的凹凸棒土为吸附剂,以K(SbO)C4H4O6·1/2H2O为Sb(Ⅲ)锑源,进行锑吸附试验,考察IMA载铁量、吸附时间和Sb(Ⅲ)初始浓度对吸附量的影响。结果表明:改性后凹凸棒土的XRD图谱中出现了羟基氧化铁(FeOOH)的特征峰;改性后凹凸棒土表面更加粗糙,比表面积增加了17%;凹凸棒土是FeOOH的优良载体;在Sb(Ⅲ)初始浓度为150 mg/L、吸附时间为720 min的条件下,IMA50对Sb(Ⅲ)的吸附量为18.51 mg/g,是天然凹凸棒土对Sb(Ⅲ)吸附量的14.9倍;IMA对Sb(Ⅲ)的吸附量随着载铁量的增加而增大,增大幅度逐渐变小;Elovich模型能较好地反映吸附动力学过程;吸附过程符合Langmuir等温模型,最大吸附量可达20.19 mg/g。对IMA50吸附Sb(Ⅲ)前后进行红外光谱分析表明,FeOOH特征吸收峰和Fe—O振动峰均向高波数方向偏移,Sb(Ⅲ)与羟基氧化铁之间发生了化学反应。试验结果对低成本处理含Sb(Ⅲ)废水有一定的指导价值。

关键词: 凹凸棒土, Sb(Ⅲ), 吸附量, 羟基氧化铁

Abstract: Antimony is a toxic element and is carcinogenic to living organism. The content of antimony in the water body around the antimony mining area in China is much higher than the standard of drinking water. In order to seek effective method for low-cost treatment of wastewater containing Sb(Ⅲ), antimony adsorption experiment was carried out by attapulgite modified with FeCl3·6H2O as adsorbent, K(SbO)C4H4O6·1/2H2O as Sb(III) antimony source. The influence of the iron load content, the adsorption time and the initial concentration of Sb(III) on the adsorption capacity of IMA was discussed. The results show that: XRD image of modified attapulgite showed characteristic peaks of hydroxyl-oxide iron (FeOOH). The surface of attapulgite was rougher after modification, therefore, the corresponding specific surface area increased by 17%, furthermore, attapulgite was an excellent carrier of FeOOH. When the initial concentration of Sb(III) was 150 mg/L and the adsorption time was 720 minutes, the adsorption capacity of IMA50 for Sb(III) was 18.51 mg/g, which was 14.9 times that of natural attapulgite. The adsorption capacity of Sb(III) by IMA increased with the increment of the amount of iron loaded. Elovich model can describe the adsorption kinetic process. The Langmuir isotherm was the best-fit adsorption isotherm model for the experimental data, and the maximum adsorption capacity is 20.19 mg/g. After adsorbed Sb(Ⅲ), the characteristic absorption peak of FeOOH and Fe—O bond absorption peak shifted to high wavenumber direction, suggested a chemical reaction between Sb (III) and hydroxyl-oxide iron. The test results for low-cost treatment of wastewater containing Sb (Ⅲ) has the certain practical significance.

Key words: Attapulgite, Sb(Ⅲ), Absorption capacity, Hydroxyl-oxide iron