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

天然丝光沸石表面重构改性及其在水中去除重金属的应用

王喆, 谭科艳, 梁明会, 蔡敬怡, 侯士田, 王悦, 江鹏. 天然丝光沸石表面重构改性及其在水中去除重金属的应用[J]. 岩矿测试, 2018, 37(6): 678-686. doi: 10.15898/j.cnki.11-2131/td.201802110018
引用本文: 王喆, 谭科艳, 梁明会, 蔡敬怡, 侯士田, 王悦, 江鹏. 天然丝光沸石表面重构改性及其在水中去除重金属的应用[J]. 岩矿测试, 2018, 37(6): 678-686. doi: 10.15898/j.cnki.11-2131/td.201802110018
Zhe WANG, Ke-yan TAN, Ming-hui LIANG, Jing-yi CAI, Shi-tian HOU, Yue WANG, Peng JIANG. Surface Modification of Natural Mordenite and Its Application in Removal of Heavy Metals from Aqueous Solution[J]. Rock and Mineral Analysis, 2018, 37(6): 678-686. doi: 10.15898/j.cnki.11-2131/td.201802110018
Citation: Zhe WANG, Ke-yan TAN, Ming-hui LIANG, Jing-yi CAI, Shi-tian HOU, Yue WANG, Peng JIANG. Surface Modification of Natural Mordenite and Its Application in Removal of Heavy Metals from Aqueous Solution[J]. Rock and Mineral Analysis, 2018, 37(6): 678-686. doi: 10.15898/j.cnki.11-2131/td.201802110018

天然丝光沸石表面重构改性及其在水中去除重金属的应用

  • 基金项目:
    中国地质科学院基本科研业务费项目(YYWF201722;YYWF201617)
详细信息
    作者简介: 王喆, 硕士研究生, 从事地球化学和环境修复研究。E-mail:495953116@qq.com
    通讯作者: 谭科艳, 博士, 副研究员, 主要从事环境地球化学和环境污染修复研究。E-mail:tankeyan2017@163.com
  • 中图分类号: P578.974;O613.72

Surface Modification of Natural Mordenite and Its Application in Removal of Heavy Metals from Aqueous Solution

More Information
  • 天然丝光沸石作为一种绿色廉价多孔材料广泛应用于环境治理中去除重金属,目前报道的天然沸石对重金属的去除率多在60%~90%,提升其去除效率已成为研究热点。本文采用正硅酸乙酯对天然丝光沸石进行表面重构改性,通过TEM、XRD、BET等手段表征其形貌和结构。结果表明:正硅酸乙酯水解生成的SiO2可与天然丝光沸石复合形成新颖的"SiO2/丝光沸石",原沸石表面包覆了新生纳米SiO2孔结构,同时没有损坏原始沸石的多孔结构,使改性沸石材料兼具了天然丝光沸石和纳米SiO2孔结构优点,增强了对重金属离子的吸附能力。该改性材料对水中Pb2+、Cd2+、Zn2+和Mn2+的最高吸附率为99.3%、97.1%、98.3%和97.0%,且极少解吸,性能稳定。考虑经济成本并保证合适吸附率的情况下选择吸附效率最佳的投加量,得到改性材料对初始浓度10 mg/L的Pb2+、Cd2+、Zn2+、Mn2+溶液的最佳投加量分别为0.5 g/L、2 g/L、2 g/L、5 g/L,可为中试和规模应用提供参考。较之焙烧、酸、碱、盐和有机改性,本改性方式对多种重金属均有高的吸附率,并显现出操作简便、成本低和环境友好等优势,具有较好应用前景。
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  • 图 1  改性丝光沸石合成图

    Figure 1. 

    图 2  天然丝光沸石(a)和改性丝光沸石(b)的透射电镜图

    Figure 2. 

    图 3  天然丝光沸石样品X射线衍射图谱

    Figure 3. 

    图 4  水解SiO2、天然丝光沸石和改性丝光沸石的X射线衍射图谱

    Figure 4. 

    图 5  水解SiO2(a)、天然丝光沸石(b)和改性丝光沸石(c)的氮气吸附-脱附等温线及孔径分布

    Figure 5. 

    图 6  吸附时间对改性丝光沸石、天然丝光沸石和水解SiO2吸附去除Pb2+、Cd2+、Zn2+和Mn2+的影响

    Figure 6. 

    图 7  不同投加量下改性丝光沸石对Pb2+、Cd2+、Zn2+和Mn2+吸附1 h效果

    Figure 7. 

    表 1  不同天然沸石改性方法吸附去除水溶液中重金属效果比较

    Table 1.  Comparison of adsorption capacity of different modified methods of zeolites for removal of heavy metals from aqueous solution

    天然沸石改性方法 改性过程或主要步骤 改性材料投加量 吸附率 参考文献
    焙烧改性 沸石300℃焙烧1.5 h 10 g/L Pb:98%
    Co:40%
    [26]
    盐酸改性 10%盐酸浸泡24 h,再去离子水冲洗,105℃烘干 100 g/L Pb:95% [27]
    氢氧化钠改性 2 mol/L氢氧化钠溶液浸泡,室温振荡2.5 h,抽滤,冲洗至中性,烘干 10 g/L Cd:99% [28]
    氢氧化钠改性 2 mol/L氢氧化钠溶液浸泡,室温振荡2.5 h,抽滤,冲洗至中性,烘干 5 g/L Zn:95%
    Cd:97%
    [29]
    氯化钠改性 2 mol/L氯化钠溶液浸泡24 h,烘干 1 g/L Pb:90%
    Cd:90%
    Ni:90%
    [30]
    硫酸/硫酸铜复合改性 1 mol/L硫酸浸泡10 h后洗净,105℃下烘干,再1 mol/L硫酸铜溶液浸泡10 h,105℃下烘干 40 g/L Cr:94% [31]
    接枝氨基 沸石先酸碱活化,后与3-氨丙基三甲氧基硅烷混合于甲苯中80℃搅拌24 h,洗涤,干燥 Ni:1 g/L
    Cu:1 g/L
    Zn:1.6 g/L
    Pb:0.6 g/L
    Ni:90%
    Cu:20%
    Zn:34%
    Pb:90%
    [25]
    本研究
    (正硅酸乙酯表面改性)
    沸石粉末与硅酸-乙酯溶液在乙醇中常温搅拌5 h,洗涤,烘干 Pb:0.5 g/L
    Zn、Cd:2 g/L
    Mn:5 g/L
    Pb:99.3%
    Cd:97.1%
    Zn:98.3%
    Mn:97.0%
    本研究
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出版历程
收稿日期:  2018-02-11
修回日期:  2018-04-10
录用日期:  2018-05-07

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