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

微波碱性体系消解-电感耦合等离子体发射光谱法测定固体废物中的六价铬

赵庆令, 李清彩, 谭现锋, 安茂国, 陈娟, 毛秀丽. 微波碱性体系消解-电感耦合等离子体发射光谱法测定固体废物中的六价铬[J]. 岩矿测试, 2021, 40(1): 103-110. doi: 10.15898/j.cnki.11-2131/td.201907290114
引用本文: 赵庆令, 李清彩, 谭现锋, 安茂国, 陈娟, 毛秀丽. 微波碱性体系消解-电感耦合等离子体发射光谱法测定固体废物中的六价铬[J]. 岩矿测试, 2021, 40(1): 103-110. doi: 10.15898/j.cnki.11-2131/td.201907290114
ZHAO Qing-ling, LI Qing-cai, TAN Xian-feng, AN Mao-guo, CHEN Juan, MAO Xiu-li. Determination of Hexavalent Chromium in Solid Waste by Inductively Coupled Plasma-Optical Emission Spectrometry with Microwave Digestion[J]. Rock and Mineral Analysis, 2021, 40(1): 103-110. doi: 10.15898/j.cnki.11-2131/td.201907290114
Citation: ZHAO Qing-ling, LI Qing-cai, TAN Xian-feng, AN Mao-guo, CHEN Juan, MAO Xiu-li. Determination of Hexavalent Chromium in Solid Waste by Inductively Coupled Plasma-Optical Emission Spectrometry with Microwave Digestion[J]. Rock and Mineral Analysis, 2021, 40(1): 103-110. doi: 10.15898/j.cnki.11-2131/td.201907290114

微波碱性体系消解-电感耦合等离子体发射光谱法测定固体废物中的六价铬

  • 基金项目:
    山东省地质勘查项目(鲁国土资字[2016]328号)
详细信息
    作者简介: 赵庆令, 硕士, 高级工程师, 从事地质实验测试及环境地质工作。E-mail: zqlzb@126.com
    通讯作者: 谭现锋, 硕士, 研究员, 从事环境地质工作。E-mail: geotan1977@126.com
  • 中图分类号: O614.242;O657.31

Determination of Hexavalent Chromium in Solid Waste by Inductively Coupled Plasma-Optical Emission Spectrometry with Microwave Digestion

More Information
  • 六价铬Cr (Ⅵ)是建设用地土壤及固体废物环境监测的必测指标之一,为了配套现行土壤环境质量标准,建立操作简便、准确精密的Cr (Ⅵ)前处理和分析测定方法势在必行。本文采用0.1mol/L磷酸氢二钠溶液(pH=9.0)作为提取剂,微波炉消解,在优化的微波消解温度和时间内,保证了对固体样品基体的破坏作用,将晶格中的Cr (Ⅵ)全部释放到溶液中,并有效抑制了Cr (Ⅲ)氧化。用0.45μm滤膜在pH=9.0条件进行过滤后,可以将六价铬(溶液)与三价铬(沉淀)分离,借助电感耦合等离子体发射光谱法(ICP-OES)完成样品溶液中Cr (Ⅵ)的定量。结果表明:当样品量为1.00g,微波消解温度为90℃,消解时间为20min时能够保证固体废物中Cr (Ⅵ)的完全提取及准确测定。方法检出限为0.057mg/kg,相对标准偏差(n=7)低于3.20%,与HJ 687标准方法进行比对,测得的相对偏差介于-5.6%~7.6%;实际固体废物中Cr (Ⅵ)的加标回收率为94.3%~96.6%。与前人相关的电感耦合等离子体发射光谱法(检出限0.83mg/kg,加标回收率均值87.2%)相比,本方法的检出限更低,样品前处理时间更短,自动化程度高,可应用于环境监测领域。

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  • 图 1  铬元素的pH-Eh相图(据文献[1]修改)

    Figure 1. 

    图 2  微波消解时间与Cr(Ⅵ)浓度的关系

    Figure 2. 

    图 3  微波消解温度与Cr(Ⅵ)浸出浓度的关系

    Figure 3. 

    图 4  三氧化二铬(Cr2O3)对Cr(Ⅵ)测定的影响

    Figure 4. 

    表 1  消解试剂的选择

    Table 1.  Selection of digestion reagents

    消解试剂 铬盐 溶解度
    (g/mL)
    在含Cr(Ⅲ)水溶液中的反应 适用性
    硫酸钠 Cr2(SO4)3 220 Cr3++3H2O→Cr(OH)3↓+3H+ 不适用
    碳酸钠 Cr2(CO3)3 不存在 3CO32-+2Cr3+ +3H2O→2Cr(OH)3↓+3CO2 适用
    磷酸氢二钠 CrPO4 < 6.3×10-31 Cr3++HPO42-→CrPO4↓+H+
    Cr(OH)3+HPO42-→CrPO4↓+H2O+2OH-
    较适用
    下载: 导出CSV

    表 2  方法精密度及加标回收率试验

    Table 2.  Precision and recovery tests of the method

    测试项目 试样浓度A 试样浓度B 试样浓度C
    7次测定值
    (mg/kg)
    19.83  19.08
    20.43  19.38
    20.67  20.40
    19.37
    696.2  735.5
    722.9  714.8
    719.3  701.4
    694.3
    5567  5476
    5436  5551
    5523  5552
    5528
    平均值(mg/kg) 19.88 712.1 5519
    标准偏差(mg/kg) 0.62 15.30 46.97
    RSD(%) 3.14 2.15 0.85
    HJ 687测定值(mg/kg) 18.42 721.9 5837
    相对偏差(%) 7.62 -1.37 -5.60
    Cr(Ⅵ)加标量(μg) 20 500 5000
    加标后测定值(mg/kg) 38.91 1195 10232
    加标回收率(%) 95.2 96.6 94.3
    下载: 导出CSV
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出版历程
收稿日期:  2019-07-29
修回日期:  2020-11-12
录用日期:  2020-12-06
刊出日期:  2021-01-28

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