ICP-MS Determination of Combination States of Heavy Metal Elements in Solidified Materials of Cement-Based Sediment with Separation by Modified BCR Sucessive Extraction
摘 要
为测定水泥基河道底泥固化材料中4种重金属元素(Pb、Cu、Cr、Zn)的形态,作如下试验:将普通硅酸盐水泥与河道底泥按质量比2:8进行混合,并注装于模具中干燥成型后,于湿度>95%,温度为(20±0.5)℃条件下的养护箱内分别湿式养护3,7,14,28,45,60 d,制得一系列固化材料样品。作为分析用样品,须将固化块样破碎至通过75 μm孔径的网筛并充分混匀。测定上述样品中重金属元素总量时,取此经破碎的样品0.100 g,用硝酸3 mL,过氧化氢1 mL和氢氟酸1 mL进行微波消解。所得消解液于150℃加热蒸发赶酸,冷却后加水溶解并定容为50.0 mL。用电感耦合等离子体质谱法(ICP-MS)测定此溶液中4种重金属元素的含量。另取0.800 g样品,按改进的BCR连续提取法先后分离出上述4种重金属元素的4种结合形态,依次为酸可提取态(F1)、可还原态(F2)、可氧化态(F3)和残渣态(F4)。分离所得4种形态的样品溶液用ICP-MS分别测定其中重金属元素的含量。在ICP-MS分析中,用Sc、Ge、In和Bi作为内标,以校正响应信号的变化和消除仪器的漂移及基体效应。试验结果表明,所用方法具有较好的准确度和精密度。根据改进的BCR连续提取法分离后,ICP-MS的分析结果得到了固化过程中4种重金属元素迁移性变化的特征和规律。
Abstract
For determination of combination state of 4 heavy metal elements (i.e., Pb, Cu, Cr, Zn) in solidified materials of cement-based river sediment, testing samples were prepared as follows:cement was mixed thoroughly with river sediment by the mass ratio of 2 to 8, and the mixture was dried and moulded into solid cubes, which were then wet-cured in curing boxes for 3, 7, 14, 28, 45 and 60 days at (20±0.5)℃ with relative humidity of >95%. For use as an analytical sample, the solid cube should be crashed to pass through sieve with pore of 75 μm. For determination of total content of the 4 heavy metal elements. 0.100 g of the crashed sample was taken and digested with 3 mL of HNO3 and 1 mL each of H2O2 and HF in a microwave oven. The digested solution was then heated at 150℃ to expel acids, and after cooling the solution was diluted to 50.0 mL with water and used for ICP-MS determination. Another portion of 0.800 g of the sample was taken and treated by the modified BCR successive extractions to obtain 4 sample solutions containing the 4 heavy metal elements in 4 combination states, i.e., (F1) acid extractable state, (F2) reducible state, (F3) oxidizable state and (F4) residual state, and contents of the 4 heavy metals were determined by ICP-MS in the same way. In the MS analysis, Sc, Ge, In and Bi were chosen as internal standards to calibrate changes of response signals and to eliminate instrumental drifts and matrix effects. It was shown that the proposed method gave results satifactory in accuracy and precision, and that characteristics and regulations of migrations of the 4 elements during the course of solidification were found, based on data of ICP-MS analysis with separation by the modified BCR successive extraction method.
中图分类号 O657.63 DOI 10.11973/lhjy-hx201904006
所属栏目 工作简报
基金项目 国家自然科学基金项目(51679140);上海市级大学生创新创业训练计划(SH2017122);上海理工大学科技发展项目(2018KJFZ109)
收稿日期 2018/5/23
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备注李默挺,硕士研究生,主要从事固体废弃物处理研究
引用该论文: LI Moting,TAO Hong,SUN Yan,WANG Yixin,LI Feipeng,LI Danyan. ICP-MS Determination of Combination States of Heavy Metal Elements in Solidified Materials of Cement-Based Sediment with Separation by Modified BCR Sucessive Extraction[J]. Physical Testing and Chemical Analysis part B:Chemical Analysis, 2019, 55(4): 401~407
李默挺,陶红,孙燕,王怡心,李飞鹏,李丹妍. 改进的BCR连续提取法-电感耦合等离子体质谱法分析水泥基底泥固化材料中重金属形态[J]. 理化检验-化学分册, 2019, 55(4): 401~407
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【2】顾竹珺,陈夷萍,冯嘉萍,等.城市河道底泥基于固化/稳定化处置技术的发展瓶颈与可持续利用途径[J].净水技术, 2017(6):22-29.
【3】CONNER J R, HOEFFNER S L. A critical review of stabilization/solidification technology[J]. C R C Critical Reviews in Environmental Control, 1998,28(4):397-462.
【4】SUMAN RAJ D S, APARNA C, REKHA P, et al. Stabilization and solidification technologies for the remediation of contaminated soils and sediments-an overview[J]. Land Contamination and Reclamation, 2005,13(1):23-48.
【5】GUO B, LIU B, YANG J, et al. The mechanisms of heavy metal immobilization by cementitious material treatments and thermal treatments:A review[J]. Journal of Environmental Management, 2017,193:410-422.
【6】刘甜田,何滨,王亚韩,等.改进BCR法在活性污泥样品重金属形态分析中的应用[J].分析试验室, 2007,26(z1):17-20.
【7】KUCUKSEZGIN F, ULUTURHAN E, BATKI H. Distribution of heavy metals in water, particulate matter and sediments of Gediz River (Eastern Aegean)[J]. Environmental Monitoring and Assessment, 2008,141(1/3):213-225.
【8】WANG Y, HAN F, MU J. Solidification/stabilization mechanism of Pb(Ⅱ), Cd(Ⅱ), Mn(Ⅱ) and Cr(Ⅲ) in fly ash based geopolymers[J]. Construction & Building Materials, 2018,160:818-827.
【9】雷鸣,廖柏寒,秦普丰,等.矿区污染土壤Pb、Cd、Cu和Zn的形态分布及其生物活性的研究[J].生态环境学报, 2007,16(3):807-811.
【10】CHEN Q Y, TYRER M, HILLS C D, et al. Immobilisation of heavy metal in cement-based solidification/stabilisation:a review[J]. Waste Management, 2009,29(1):390-403.
【11】毛凌晨,施柳,叶华,等.沉积物中重金属形态分析技术的适用范围[J].理化检验-化学分册, 2017,53(9):1109-1116.
【12】QUEVAUVILLER P, RAURET G, GRIEPINK B. Single and sequential extraction in sediments and soils[J]. International Journal of Environmental Analytical Chemistry, 2006,51(1/4):231-235.
【13】RAURET G, LÓPEZSÁNCHEZ J F, SAHUQUILLO A, et al. Improvement of the BCR three step sequential extraction procedure prior to the certification of new sediment and soil reference materials[J]. Journal of Environmental Monitoring Jem, 1999,1(1):57-61.
【14】张朝阳,彭平安,宋建中,等.改进BCR法分析国家土壤标准物质中重金属化学形态[J].生态环境学报, 2012(11):1881-1884.
【15】YAN M, ZENG G, LI X, et al. Incentive effect of bentonite and concrete admixtures on stabilization/solidification for heavy metal-polluted sediments of Xiangjiang River[J]. Environmental Science & Pollution Research, 2017,24(1):892-901.
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【21】陈英旭,何增耀.土壤中铬的形态及其转化[J].环境科学, 1994(3):53-56.
【22】邵孝侯,邢光熹.连续提取法区分土壤重金属元素形态的研究及其应用[J].土壤学进展, 1994(3):40-46.
【23】徐明岗,张青,曾希柏.改良剂对黄泥土镉锌复合污染修复效应与机理研究[J].环境科学, 2007,28(6):1361-1366.
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