Abstract:The determination of As and Se in soil by inductively coupled plasma mass spectrometry (ICP-MS) can be severely interfered by polyatomic ions such as argon compounds, chlorides, oxides and double charges, leading to high difficulty in determination of As and Se in soil. The soil samples were digested by aqua regia in the graphite digester. In the MS/MS mode, the mass charge ratio (m/z) of the first quadrupole mass filter (Q1) was set to 75 and 80, respectively. Accompanied by the introduction of oxygen into the collision/reaction cell, 75As+ and 80Se+ were converted to 75As16O+ and 80Se16O+, while the interfering ions could not react with oxygen. The m/z of the second quadrupole mass filter (Q3) was set to 91 and 96, respectively, so that 75As16O+ and 80Se16O+ could pass through and enter the detector, avoiding the mass spectrometry interferences in the sample. Accordingly, a method for the determination of As and Se in soil by graphite digestion-inductively coupled plasma tandem mass spectrometry (ICP-MS/MS) was established. The oxygen flow rate was optimized and 1.0 mL/min was selected. The experimental results showed that the linear range of As and Se was 0.500-100 μg/L. The linear correlation coefficients were 0.999 93 and 0.999 98, the limits of detection were 0.008 mg/kg and 0.001 mg/kg, and the limits of quantification were 0.032 mg/kg and 0.004 mg/kg, respectively. The contents of As and Se in certified reference materials and actual samples of soil were determined according to the experimental method. The results showed that the measured values of As and Se were consistent with the certified values for the certified reference materials. The relative standard deviations (RSD, n=6) were 2.0%-4.4% and 2.6%-7.8% for As and Se, respectively. For the actual samples of soil, the measured results were basically consistent with those obtained by atomic fluorescence spectrometry. The RSDs (n=6) were 2.3%-4.5% and 3.7%-7.9%, respectively.
刘跃, 王记鲁, 李静, 王鑫, 林冬. 氧气反应模式-电感耦合等离子体串联质谱法测定土壤中砷和硒[J]. 冶金分析, 2022, 42(10): 30-37.
LIU Yue, WANG Jilu, LI Jing, WANG Xin, LIN Dong. Determination of arsenic and selenium in soil by inductively coupled plasma tandem mass spectrometry at oxygen reaction mode. , 2022, 42(10): 30-37.
[1] 生态环境部.土壤环境监测分析方法[M].北京:中国环境出版集团,2019. [2] 李蕾,苏园,陈楚国,等.微敞开体系快速石墨消解-原子荧光法测定食品及土壤中的硒[J].环境化学,2020,39(4):1098-1104. LI Lei,SU Yuan,CHEN Chuguo,et al.Fast determination of selenium in food and soils by micro-open graphite digestion-atomic fluorescence spectrometry[J].Environmental Chemistry,2020,39(4):1098-1104. [3] 林海兰,朱日龙,于磊,等.水浴消解-原子荧光光谱法测定土壤和沉积物中砷、汞、硒、锑和铋[J].光谱学与光谱分析,2020,40(5):1528-1533. LIN Hailan,ZHU Rilong,YU Lei,et al.Determination of arsenic,mercury,selenium,antimony and bismuth in soil and sediments by water bath digestion-atomic fluorescence spectrometry[J].Spectroscopy and Spectral Analysis,2020,40(5):1528-1533. [4] 赵小学,位志鹏,王建波,等.王水水浴消解/ICP-MS法测定土壤及水系沉积物中As、Se、Sb、Hg、Bi的适用性研究[J].中国测试,2021,47(9):61-69. ZHAO Xiaoxue,WEI Zhipeng,WANG Jianbo,et al.Study on determination of As,Se,Sb,Hg and Bi in soil and sediment by ICP-MS with water bath[J].China Measurement & Test,2021,47(9):61-69. [5] 赵宗生,赵小学,姜晓旭,等.原子荧光光谱测定土壤和水系沉积物中硒的干扰来源及消除方法[J].岩矿测试,2019,38(3):333-340. ZHAO Zongsheng,ZHAO Xiaoxue,JIANG Xiaoxu,et al.Interference sources and elimination methods for the determination of selenium in soil and water sediment by atomic fluorescence spectrometry[J].Rock and Mineral Analysis,2019,38(3):333-340. [6] 马万平,温汉捷,叶琴,等.巯基棉富集分离-原子荧光光谱法测定高碳高硫地质样品中痕量硒[J].岩矿测试,2021,40(4):550-560. MA Wanping,WEN Hanjie,YE Qin,et al.Determination of trace selenium in high-carbon and high-sulfur geological samples by thiol cotton fiber separation-atomic fluorescence spectrometry[J].Rock and Mineral Analysis,2021,40(4):550-560. [7] 文典,陈楚国,李蕾,等.微敞开体系快速全消解ICP-MS法测定土壤中总砷[J].环境化学,2020,39(8):2317-2320. WEN Dian,CHEN Chuguo,LI Lei,et al.Determination of total arsenic in soils by semi-open full digestion coupled ICP-MS[J].Environmental Chemistry,2020,39(8):2317-2320. [8] 闫学全.一种自动石墨消解-ICP-MS法监测工业区土壤中微量砷、汞、硒、锑元素残留方法的建立[J].中国测试,2018,44(11):77-80. YAN Xuequan.Automatic graphite digestion-ICP-MS method for detection of arsenic,mercury,selenium and antimony elements in industrial soil[J].China Measurement & Test,2018,44(11):77-80. [9] 屈明华,陈雄弟,倪张林,等.DRC-ICP-MS法测定土壤硒前处理方法研究[J].土壤通报,2019,50(3):698-703. QU Minghua,CHEN Xiongdi,NI Zhanglin,et al.Pretreatment for determination of soil selenium by ICP-MS with dynamic reaction cell[J].Chinese Journal of Soil Science,2019,50(3):698-703. [10] Jefferson Rodrigues de Souza,Lilian da Silva,Márcia Silva da Rocha,et al.Dynamic reaction cell-ICP-MS as a powerful tool for quality control of a Se-enriched dietary supplement[J].Food Analytical Methods,2017,10:3088-3097. [11] 王振伟,王维宇,郭朝,等.电感耦合等离子体串联质谱氨气模式测定土壤中的银[J].环境化学,2021,40(4):1285-1287. WANG Zhenwei,WANG Weiyu,GUO Zhao,et al.Determination of silver in soil by ICP tandem mass spectrometry ammonia mode[J].Environmental Chemistry,2021,40(4):1285-1287. [12] 郭红巧,胡净宇,侯艳霞,等.电感耦合等离子体串联质谱法测定高温合金中痕量砷[J].冶金分析,2021,41(5):35-40. GUO Hongqiao,HU Jingyu,HOU Yanxia,et al.Determination of trace arsenic in superalloys by inductively coupled plasma tandem mass spectrometry[J].Metal-lurgical Analysis,2021,41(5):35-40. [13] 赵志飞,任小荣,李策,等.氧气反应模式-电感耦合等离子体串联质谱法测定土壤中的镉[J].岩矿测试,2021,40(1):95-102. ZHAO Zhifei,REN Xiaorong,LI Ce,et al.Determination of cadmium in soil samples by ICP-MS/MS using oxygen reaction mode[J].Rock and Mineral Analysis,2021,40(1):95-102. [14] 迟清华,鄢明才.应用地球化学元素丰度数据手册[M].北京:地质出版社,2007. [15] Agilent 8800 Triple Quadrupole ICP-MS:Understanding oxygen reaction mode in ICP-MS/MS[EB/OL].[S.l.]:Agilent Technologies.[2012-12-20].https://www.agilent.com.cn/cs/library/technicaloverviews/public/5991-1708EN_TechOverview_ICP-MS_8800_ORS_mode.pdf. [16] 林立,王琳琳.采用ICP-MS/MS对硒和砷检测的质谱干扰[J].分析试验室,2016,35(3):344-348. LIN Li,WANG Linlin.Study on the interference of selenium and arsenic in different detecting conditions by ICP-MS/MS[J].Chinese Journal of Analysis Laboratory,2016,35(3):344-348. [17] 中华人民共和国环境保护部.HJ 680—2013 土壤和沉积物 汞、砷、硒、铋、锑的测定 微波消解/原子荧光法[S].北京:中国环境科学出版社,2014.