ICP-MS法对国标小麦粉中15种稀土元素的定值研究

本文报道采用HNO_3+HClO_4溶样,小麦粉标样GBW 08503中15种超痕量稀土元素定值的ICP-MS应用研究.选择了仪器最佳操作参数.选用Re作内标可补偿基体效应.方法检出限为0.007—0.026ng·ml~(-1)加标回收率为95—103%.RSD为2.5—48%,方法快速、灵敏、准确.     

ICP-MS半定量分析及其应用

ICP-MS具有等离子发射光谱检测能力高、测量速度快、测量元素多等特点,能对样品中存在元素进行定性及半定量分析,半定量分析准确度为±30%.同时还能快速确定样品中存在的元素及浓度范围.     

应用ICP-MS直接测定近岸高盐排污口水样中重金属方法研究

利用带八极杆碰撞/反应池(ORS)和屏蔽炬技术的电感耦合等离子体质谱(ICP-MS)直接测定近岸高盐排污口样品中的V、Cr、Mn、As、Mo、Ag、Cd、Pb、Th和U等多种重金属元素.通过向碰撞池中引入He气,消除高盐基体可能带来的多原子离子干扰.样品用1%HNO3稀释后直接测定,用标准物质进行方法验证,连续分析样品4h,以检验仪器的长期稳定性.测定绝大多数元素的相对标准偏差在5%以内,加标回收率为88.32%～118.5%.     

水中硼测定方法比对研究

对姜黄素分光光度法、甲亚胺-H分光光度法和电感耦合等离子体-质谱法测定硼的方法性能进行了比对研究,为硼的测定方法的选择提供了良好的科学依据。     

Grain size partitioning of platinum-group elements in road-deposited sediments: implications for anthropogenic flux estimates from autocatalysts

Twelve road-deposited sediment samples were analyzed for platinum-group elements (PGEs) and Pb in the <63 microm fraction of an urban watershed in Hawaii. Three samples were further fractionated into five size classes, from 63-125 microm to 1000-2000 microm, and these were analyzed for PGEs and Pb. Concentrations in the <63 microm fraction reached 174 microg/kg (Pt), 101 microg/kg (Pd), 16 microg/kg (Rh), and 1.3 microg/kg (Ir). Enrichment ratios followed the sequence Rh>Pt=Pd>Ir. Iridium was geogenic in origin, while the remaining PGEs indicated significant anthropogenic contamination. Palladium, Pt and Rh concentrations and enrichment signals were consistent with PGE bivariate ratios and PGE partitioning in three-way catalysts. Size partitioning indicated that the <63 microm fraction had the lowest PGE concentrations and mass loading percentages. These data suggest that autocatalyst PGE flux estimates into the environment will be significantly underestimated if only a fine grain size fraction is analyzed.     

等离子发射光谱-质谱(ICP-MS)直接用于饮用水中的砷、锑、硒测定研究

用等离子发射光谱和等离子发射光谱-质谱作比较,等离子发射光谱-质谱用于饮用水As、Sb、Se的测量时需考虑校正系数,通过不确定度分析,确定了ICP-MS测定方法不确定度大小,得出结论:不要氢化物发生器,不加EDTA作为掩蔽剂,也可以直接用于实际.     

等离子发射光谱法及其在环境监测中的应用

介绍了ＩＣＰ－ＡＥＳ在环境监测中的应用．重点介绍了ＵＳＥＰＡ、ＡＰＨＡ－ＡＷＷＡ－ＷＰＣＥ和ＪＩＳ采用的ＩＣＰ－ＡＥＳ的方法。并对近几年发展起来的ＩＣＰ－ＭＳ、ＭＩＰ和ＭＩＰ－ＭＳ法进行了概述。引用１９８６年～１９９３年的主要文献共１４篇。     

ICP—MS法测定饮用水中的铅

采用ICP—MS法对饮用水中的铅进行了分析测定。并进行了载气流量的选择、定量离子质荷比的选择和内标的选择等实验．本实验铅的质荷比选用206，207和208三个加在一起计算。方法的检测限为0．5×10-3mg／L，精密度实验的变异系数为3．25％～7．63％。     

Phytoextraction of lead and its relationship with histidine in six plant species using ICP-MS and HPLC-MS

High-performance liquid chromatography-mass spectrometry and inductively coupled plasma mass spectrometer (ICP-MS) methods were used for determination of histidine and lead in leaves of six plant species taken from industrial areas, including Gaziantep and Bursa cities, Turkey. For extraction of histidine from plant samples, ultrapure water was used at 90°C for 30?min. Using optimum conditions of 0.2?mL?min^?1, 70?V, 15?µL and 20°C, concentrations of histidine (in mg?kg^?1) were found to be between 2 and 9 for Morus L., 6 and 13 for Robinia pseudoacacio L., 2 and 10 for Populous nigra L., 3 and 10 for Thuja, 1 and 11 for Cupressus arizonica and 4 for Cedrus libani. Concentrations of lead were in the ranges of 4–378?mg?kg^?1 for Morus L., 1–122?mg?kg^?1 for R. pseudoacacio L., 1–14?mg?kg^?1 for P. nigra L., 1.6–224?mg?kg^?1 for Thuja (Cupressaceae), 1.5–57?mg?kg^?1 for C. arizonica and 1.8?mg?kg^?1 for C. libani. Related with correlation coefficient, significant linear correlation for Thuja (Cupressaceae) (r?=?0.81) and insignificant linear correlation for P. nigra L. (r?=?0.50) were seen. Further, the leaves of Morus L., Thuja and R. pseudoacacio L. have a potential as biomonitor and/or hyperaccumulator for Pb because the rates of their maximum/minimum concentrations were found higher than 90.     

板蓝根水煎液中13种金属元素形态分析

利用电感耦合等离子体-质谱仪（ICP-MS）测定板蓝根原药材和水煎液中13种元素的含量。形态研究采用高速离心和滤膜分离水煎液中的溶解态和颗粒态,元素的溶解态再用树脂XAD-4、树脂D001、树脂D301和树脂D751分别区分非极性吸附态、阳离子交换态、阴离子交换态和螯合吸附态。结果表明,板蓝根药材含有微量Cu、Pb和Cd等重金属,同时含有丰富的Mg、Ca、Fe、Al等大量元素,其中Ca含量最高,为2739 mg·kg-1;Zn、Mg、Ca、Mn、Al和Fe的浸出率较高,在42.9%到81.9%之间;Pb和Cu的浸出率最低,只有10%左右。Zn、Mg、Ca、Mn和Pb元素颗粒态比例在0%到9.3%之间,其他元素颗粒态比例在14.3%到85.7%之间。在溶解态当中,所有元素都具有阴离子交换态;Cu、Sn、Cr和Al没有或者很少有阳离子交换态,其余元素的阳离子交换态在32.4%到98.3之间;Al、Fe、Cu、Cr和Sn没有或者很少螯合吸附态,其余元素在54.9%到98.4%之间;Zn、Cu、Sn、Cd和Pb有非极性吸附态,其余元素没有。