中国地质学会岩矿测试技术专业委员会、国家地质实验测试中心主办

腐植酸改性强化磁铁矿吸附水体中铅镉的实验研究

邵坤, 赵改红, 赵朝辉. 腐植酸改性强化磁铁矿吸附水体中铅镉的实验研究[J]. 岩矿测试, 2019, 38(6): 715-723. doi: 10.15898/j.cnki.11-2131/td.201901250017
引用本文: 邵坤, 赵改红, 赵朝辉. 腐植酸改性强化磁铁矿吸附水体中铅镉的实验研究[J]. 岩矿测试, 2019, 38(6): 715-723. doi: 10.15898/j.cnki.11-2131/td.201901250017
Kun SHAO, Gai-hong ZHAO, Chao-hui ZHAO. Enhancement of Pb and Cd Adsorption in Water Samples by Magnetite Using Humic Acid as Modifier[J]. Rock and Mineral Analysis, 2019, 38(6): 715-723. doi: 10.15898/j.cnki.11-2131/td.201901250017
Citation: Kun SHAO, Gai-hong ZHAO, Chao-hui ZHAO. Enhancement of Pb and Cd Adsorption in Water Samples by Magnetite Using Humic Acid as Modifier[J]. Rock and Mineral Analysis, 2019, 38(6): 715-723. doi: 10.15898/j.cnki.11-2131/td.201901250017

腐植酸改性强化磁铁矿吸附水体中铅镉的实验研究

  • 基金项目:
    四川省科技计划项目(2018JY0231);中国地质调查局地质调查项目(DD20189507)
详细信息
    作者简介: 邵坤, 硕士, 工程师, 从事岩矿测试及环境化学研究。E-mail:shaokun101@163.com
  • 中图分类号: P641;P575.2

Enhancement of Pb and Cd Adsorption in Water Samples by Magnetite Using Humic Acid as Modifier

  • 磁铁矿是一种绿色廉价的矿物材料,对水体中重金属离子具有良好的吸附性,但吸附容量低,选择性差,易团聚,通过改性可以克服该缺点并提高其吸附性能。本文以腐植酸为改性剂,采用常温水相反应制备了腐植酸改性磁铁矿吸附材料。通过傅里叶红外光谱(FTIR)、扫描电镜(SEM)和X射线光电子能谱(XPS)表征研究其表面形貌和微观结构。采用静态平衡实验考察了pH、吸附时间等因素对铅、镉吸附性能的影响,探讨了吸附动力学规律,拟合了吸附等温线。结果表明:腐植酸上的羧基、羟基被成功地接枝到了磁铁矿表面。在室温下,溶液初始pH对Pb2+的吸附率几乎无影响,对Cd2+的影响较大,当pH=7时,Pb2+和Cd2+吸附率均达到了95%。对初始质量浓度为10mg/L的Pb2+、Cd2+最佳吸附平衡时间为360min,吸附过程符合准二级动力学方程。吸附等温线实验得到的竞争吸附顺序为Pb2+>Cd2+,由Langmuir等温吸附模型得到Pb2+、Cd2+饱和吸附容量分别为39.27mg/g、28.95mg/g,显著大于磁铁矿的饱和吸附容量,表明磁铁矿经腐植酸改性后增强了对水中铅镉的吸附能力。
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  • 图 1  磁铁矿(a)、腐植酸(b)和腐植酸改性磁铁矿(c)的红外光谱图

    Figure 1. 

    图 2  磁铁矿(a)和腐植酸改性磁铁矿(b)扫描电镜图

    Figure 2. 

    图 3  磁铁矿(a)和腐植酸改性磁铁矿(b)的X射线光电子能谱图

    Figure 3. 

    图 4  初始pH对腐植酸改性磁铁矿吸附Pb2+和Cd2+的影响

    Figure 4. 

    表 1  Langmuir及Freundlich模型拟合参数

    Table 1.  Fitting parameters of the Langmuir and Freundlich models

    元素 Langmuir模型 Freundlich模型
    qmax
    (mg/g)
    K(L/mg) R2 Kf
    (mg/g)
    n R2
    Pb2+ 39.27 0.454 0.972 28.41 12.85 0.791
    Cd2+ 28.95 0.960 0.986 13.60 9.09 0.843
    下载: 导出CSV

    表 2  不同改性材料对Pb2+、Cd2+的吸附性能比较

    Table 2.  Comparison of adsorption properties of Pb2+, Cd2+ with various modified minerals

    矿物材料 改性方法 pH Pb或Cd的吸附容量
    (mg/g)
    参考文献
    钒钛磁铁矿 pH 3,与腐植酸溶液振荡24h,70℃干燥24h 7 Pb2+ 14.41 [5]
    针铁矿 腐植酸溶液与针铁矿1 : 1混匀,60℃烘干 - Cd2+ 45.46 [32]
    蒙脱石 pH5,与腐植酸混合振荡20h,45℃风干 5 Cd2+ 11.87 [33]
    累托石 与腐植酸混匀,再与氯化钙和硼砂混合,50℃干燥24h 6 Cd2+ 5.97 [34]
    菱铁矿 小麦秸秆和菱铁矿500℃碳化60min 6~9 Cd2+ 19.42 [35]
    腐植酸 磺化后进行接枝反应,形成不溶性腐植酸 7~9 Pb2+ 8.24 [24]
    腐植酸 400℃加热1h,冷后2mol/L氯化钙中浸泡2h 6 Cd2+ 20.00 [36]
    磁铁矿 水洗70℃烘干,室温粉碎至20~200目 6 Pb2+ 16.98 [31]
    磁铁矿 0.5mol/L盐酸浸泡48h,150℃灼烧10min 7 Cd2+ 18.93 [29]
    磁铁矿 与腐植酸溶液混合,pH 2~3,振荡72h,60℃干燥72h 7 Pb2+ 39.27, Cd2+ 28.95 本文
    下载: 导出CSV
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收稿日期:  2019-01-25
修回日期:  2019-05-30
录用日期:  2019-07-16

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