微波消解-电感耦合等离子体质谱(ICP-MS)法同时测定土壤中11种金属元素

称取0.25g样品加入5 mL硝酸和2 mL氢氟酸,用微波消解技术对样品进行前处理.以Re作为As、Pb、Tl的内标,Rh作为Cd、Co、Cr、Ni的内标,Bi作为Be、Cu、Zn的内标,Tb作为V的内标,建立了KED模式下微波消解电感耦合等离子体质谱(ICP-MS)法同时测定土壤中Be、As、Cd、Co、Cr、Cu、...     

微波消解-电感耦合等离子体质谱(ICP-MS)法同时测定土壤中11种金属元素

称取0.25g样品加入5mL硝酸和2mL氢氟酸,用微波消解技术对样品进行前处理。以Re作为As、Pb、Tl的内标,Rh作为Cd、Co、Cr、Ni的内标,Bi作为Be、Cu、Zn的内标,Tb作为V的内标,建立了KED模式下微波消解电感耦合等离子体质谱(ICP-MS)法同时测定土壤中Be、As、Cd、Co、Cr、Cu、Ni、Pb、Tl、V、Zn等11种金属元素的方法。方法线性关系良好,线性相关系数均在0.999以上,检出限为0.002～0.054mg/kg。检测土壤标准物质GSS-17、GSS-18验证方法准确性,结果显示测定值均在标准差允许范围内,相对标准偏差在0.29%～5.3%,是一种快速、可靠的土壤中多种金属元素同时检测方法。     

电感耦合等离子体质谱法测定铝钪合金中的稀土元素

通过酸溶快速分解铝钪合金,电感耦合等离子体质谱法(ICP-MS)测定铝钪合金中的La,Ce,Pr,Nd,Sm,Y,Eu,Gd,Tb,Dy,Ho,Er,Tm,Yb,Lu 15种稀土元素。对样品的前处理方式,仪器的工作条件,内标浓度等条件进行了考察。以103Rh,185Re作为内标校正铝的基体效应,考察了稀土元素的质谱干扰。在优化条件下各个元素的方法检出限为0.01~0.07μg/g,通过加标回收试验测得15个元素的回收率为96%~124%,相对标准偏差为0.74%~7.5%。     

微波消解-电感耦合等离子体质谱法(ICP-MS)同时测定土壤中11种金属元素

称取0.25 g样品加入5ml硝酸和2ml氢氟酸,用微波消解技术对样品进行前处理。以Re作为As、Pb、Tl的内标,Rh作为Cd、Co、Cr、Ni的内标,Bi作为Be、Cu、Zn的内标,Tb作为V的内标,建立了KED模式下可同时测定土壤中Be、As、Cd、Co、Cr、Cu、Ni、Pb、Tl、V、Zn 11种金属元素的微波消解ICP-MS方法。该方法线性关系良好,线性相关系数均在0.9990以上,检出限为0.002mg/kg-0.054 mg/kg。检测土壤标准物质GSS-17、GSS-18验证方法准确性,结果显示测定值均在标准差允许范围内,相对标准偏差在0.29%-5.33%,是一种快速、可靠的土壤多种金属元素检测方法。     

电感耦合等离子体质谱法测定高纯铼中26种痕量杂质元素

以电感耦合等离子体质谱法(ICP-MS)测定了高纯铼中26种杂质元素含量。应用反应池技术消除了复合离子对K、Ca、Fe等元素的干扰,采用干扰方程校正技术消除了Re氧化物对Tl的质谱重叠干扰,未受干扰的其它杂质元素采用内标校正法直接测定。考察了溶液酸度、基体效应等条件对测定的影响,优化选择了测定同位素和内标元素。方法测定下限介于0.12～5.0μg/g,加标回收率在90%～110%之间,相对标准偏差小于10%。方法可以满足4N5高纯铼的测定。     

ICP-MS同时测定植物性食品中稀土元素的方法研究

建立了植物性食品中16种稀土杂质(Sc、Y、La、Ce、Pr、Nd、Sm、Eu、Gd、Tb、Dy、Ho、Er、Tm、Yb和Lu)元素的电感耦合等离子体质谱(ICP-MS)的分析方法.考察了基体效应及质谱干扰,应用In内标,有效地补偿基体效应所引起的测量偏差,建立修正公式校正质谱干扰.对照分析了参考标准物质.对所测定元素,校正曲线的相关系数为＞0.9990,方法的检出限低于2.2 pg/g(Sc为95pg/g),回收率为92%～106%,RSD优于3.2%(n=7).     

高分辨电感耦合等离子体质谱仪测定中亚山地冰川雪冰中超痕量元素

在超净实验条件下,利用高分辨电感耦合等离子体质谱仪直接测定雪冰样品中浓度在1ng/L~100μg/L之间的多种超痕量元素Al、Fe、Mn、Co、Cu、Zn、Sr、Sb、Cd、CsBa、Tl、Pb和Bi的实验方法进展。在测定过程中灵敏度的变化可通过监测ArAr质谱峰的变化进行校正,并建立了数学校正公式。以1%HNO3为空白溶液获得了各元素的检出限(ng/L)分别为:Al40、Mn6、Fe40、Co2.74、Cu9.6、Zn20、Sr0.03、Sb0.15、Cs0.04、Ba0.4、Tl0.07、Pb0.8和Bi0.05。利用标准参考物质SLRS-4对测试方法的准确度进行了评价。研究了在硝酸含量分别为0.5%、1%、2%和4%时雪冰中超痕量元素质谱信号强度的变化特点。测定结果发现,对于污化层样品,当硝酸的含量为1%时痕量元素的质谱信号强度最大;对于非污化层样品,痕量元素的质谱信号强度在硝酸含量为0.5%时较大,但与硝酸含量为1%时的质谱信号强度相比变化率小于10%。结合中亚山地冰川雪冰中痕量元素浓度差别大的特点,确定硝酸在样品中的含量为1%为合适的酸度。并对卓奥友峰和珠穆朗玛峰雪坑样品进行了分析方法的重复性研究。     

电感耦合等离子体质谱法同时测定植物类新食品原料中14种无机元素北大核心CSCD

0.500 0g样品经硝酸3mL、过氧化氢2mL消解后,采用电感耦合等离子体质谱法同时测定样品溶液中Na、Mg、Ca、Al、Cu、Zn、Fe、Mn、Se、Pb、Cd、As、Hg和Cr的含量。采用0.5%(体积分数)硝酸的基体酸度增强分析元素的信号强度;在两次测试之间用100μg·L-1 Au-5%(体积分数)硝酸溶液清洗仪器,降低Hg的吸附效应;利用甲烷碰撞动态反应池技术消除了分析过程中的质谱干扰,选择Sc、Y、In、Bi为内标元素校正基体效应。14种元素的质量浓度在一定范围内与信号强度呈线性关系,检出限(3s)在0.003~0.039μg·L^(-1)之间。方法用于分析国家标准物质GBW 10027,各元素测定值与认定值相符,测定值的相对标准偏差(n=6)在1.6%~14%之间。     

电感耦合等离子体质谱法同时测定植物类新食品原料中14种无机元素

0.500 0g样品经硝酸3mL、过氧化氢2mL消解后,采用电感耦合等离子体质谱法同时测定样品溶液中Na、Mg、Ca、Al、Cu、Zn、Fe、Mn、Se、Pb、Cd、As、Hg和Cr的含量。采用0.5%(体积分数)硝酸的基体酸度增强分析元素的信号强度;在两次测试之间用100μg·L-1 Au-5%(体积分数)硝酸溶液清洗仪器,降低Hg的吸附效应;利用甲烷碰撞动态反应池技术消除了分析过程中的质谱干扰,选择Sc、Y、In、Bi为内标元素校正基体效应。14种元素的质量浓度在一定范围内与信号强度呈线性关系,检出限(3s)在0.003~0.039μg·L~(-1)之间。方法用于分析国家标准物质GBW 10027,各元素测定值与认定值相符,测定值的相对标准偏差(n=6)在1.6%~14%之间。     

微波消解ICP-MS快速测定生物样品中的多种元素

建立了微波辅助HNO3消解样品,ICP-MS快速测定生物样品中Ti、Cr、Mn、Fe、Co、Ni、Cu、Zn、Ge、As、Se、Sr、Mo、Ag、Cd、I、Ba、Hg、Tl、Pb、Bi共21种微量及痕量元素。通过在线加入内标来校正基体效应和信号漂移对测量所造成的影响。各元素线性相关系数在0.9990以上,RSD小于6.0%。用本方法对国家标准样品GBW07601a(头发),GBW10010(大米),GBW10016(茶叶),GBW10023(紫菜)进行分析,结果满意。方法能满足生物样品痕量分析的要求。     

二氧化钛中杂质元素ICP-MS法测定的研究

本文报道了用电感耦合等离子质谱（ICP-MS）测定二氧化钛中18种杂质元素的方法。样品用浓硫酸及固体硫酸铵溶解至清亮后,加入内标元素45Sc、115In、205Tl,用内标法直接测定。讨论了二氧化钛的基体效应及钛产生的质谱干扰对测定结果的影响。方法的检出限是0．03～12．0ng／mL,相对标准偏差是1．4～12．5％,加标回收率是92．0％～103％。该法具有简便、快速、灵敏、准确等优点。     

-电感耦合等离子体质谱法测定硅锰冶炼渣中8种金属元素

实验采用HCl-HNO₃-HF-HClO₄混合酸为消解体系对样品进行前处理,加入1.0 mL盐酸羟胺溶液(100 g/L)溶解残渣,选择合适的同位素,以¹⁰³Rh为内标测定Cr、Co、Ni、Cu、Zn和Cd,以¹⁹³Ir为内标测定Tl和Pb,建立了电感耦合等离子体质谱(ICP-MS)法测定硅锰冶炼渣中8种重金属元素的方法。实验发现,样品前处理选择HCl∶HNO₃∶HF∶HClO₄=5∶5∶5∶1,并在复溶阶段加入1.0 mL盐酸羟胺溶液(100 g/L)可以完全消解样品,实验采用KED模式和干扰系数校正法消除质谱干扰,样品中待测元素的测定结果不受基体成分的干扰。通过绘制校准曲线及测定流程空白,各元素校准曲线的相关系数均大于0.9999,方法检出限为0.006~0.19 mg/kg,方法定量限为0.018~0.57 mg/kg。对硅锰渣实际样品进行测定,各元素的相对标准偏差(RSD,n=11)在0.83%~4.1%,加标回收率为94.7%~106%;经过人员比对实验,相对偏差为-4.54%~4.24%。测定结果稳定可靠,能满足硅锰冶炼渣中8种微量金属元素含量的分析检测要求。     

Routine clinical determination of lead,arsenic, cadmium,and thallium in urine and whole blood by inductively coupled plasma mass spectrometry

For the measurement of As, Cd, Pb, and Tl in urine or whole blood, judicious choices of internal standard elements for matrix correction and the development of a refined isobaric arsenic correction are necessary to produce accurate ICP-MS results. Ga and Rh are chosen as internal standards for As and Cd respectively. Bi is better for the correction of Pb and Tl than Re. An empirically derived equation relating the measurement of ¹⁶O³⁵Cl to the ⁴⁰Ar³⁵Cl contribution to the arsenic signal at mass 75 is refined by measuring the responses at mass 51 and 75 for urines with added hydrochloric acid. Overall, ICP-MS results for blood and urine are within 6% of Zeeman GFAAS results for patient samples. For surveys, the overall average of ICP-MS results is within 3% of target.     

Calibration of laser-ablation ICP-MS. Can we use synthetic standards with pneumatic nebulization?

An approach for the determination of trace element concentrations in high purity metals, using an inductively coupled plasma mass spectrometer (ICP-MS) with a laser-ablation system for direct solid sample introduction after calibration with nebulized liquid standards was made. Due to the inherent differences in the rate of sample introduction with laser-ablation and pneumatic nebulization, a matrix element must be used as an internal standard. This is problematical for elements that have no isotope with a relative abundance of less than 0.1 %, since the ion signals would be too high for direct measurement, and reduction of the ablation rate would compromise the sensitivity for trace elements. Due to the high stability of ICP-unit and mass filter of the instrument used, it was found that the tail of a mass-peak of the matrix element could be used as an internal standard. Therefore, a position at –0.5 amu from the matrix-isotope (e.g. ^62.5Cu in copper samples) was used for internal standardization. The standard deviation of this signal in a period of 2.5 h was 3.6% RSD with no notable drift when the laser ablation was used for sample introduction. The calibration of the matrix-element by nebulizing liquid standards showed that the ion signal measured on the peak-tail is directly proportional to the element concentration in the ICP. This indicates that the peak shape is not only stable, but also independent of the peak height. The advantages of this method lie in the easy preparation of calibration standards for quantitative measurements with a laser-ablation system and access to homogeneous standards for materials, that are difficult to homogenize in the solid state. The calibration of the traces is performed relatively to a fixed concentration of the matrix element. Calibrations were carried out for trace concentrations in high purity copper and good recoveries were obtained for high-purity reference standards. Received: 23 February 1998 / Revised: 20 July 1998 / Accepted: 25 July 1998     

泡沫塑料富集–石墨炉原子吸收光谱法测定贝类水产品中痕量铊

采取微波消解的前处理手段消解样品,经泡沫塑料分离富集后,用石墨炉原子吸收光谱法测定贝类水产品中痕量铊。以1.5 mL Fe3+,2 mL H2O2和5%王水介质作为吸附体系将样品中铊分离富集,再以硝酸钯、抗坏血酸作为基体改进剂进行测定。铊的质量浓度在0～50μg/L范围内线性良好,相关系数为0.999 7,方法的检出限可达0.07μg/g。测定结果的相对别准偏差为1.53%～4.01%(n=7),加标回收率为87.1%～98.3%。泡沫塑料富集–石墨炉子吸收光谱法测定贝类水产品中痕量铊是一种准确、安全、便捷的检测方法。     

ICP-MS法测定高纯钛中痕量元素

建立了ICP-MS直接测定高纯钛中Be,V,Co,Ni,Ga,Mo,Nb,Cd,Sb,TI,Pb的分析方法,并对ICP-MS工作参数及条件进行了优化和选择.高纯钛用HF与HNO3溶解后加入Sc、Cs、Re内标,用ICP-MS直接检测.方法的检出限为0.03～0.1 ng/mL,测定下限为0.2～0.5 ng/mL,各元...     

Calibration of laser-ablation ICP-MS. Can we use synthetic standards with pneumatic nebulization?

An approach for the determination of trace element concentrations in high purity metals, using an inductively coupled plasma mass spectrometer (ICP-MS) with a laser-ablation system for direct solid sample introduction after calibration with nebulized liquid standards was made. Due to the inherent differences in the rate of sample introduction with laser-ablation and pneumatic nebulization, a matrix element must be used as an internal standard. This is problematical for elements that have no isotope with a relative abundance of less than 0.1 %, since the ion signals would be too high for direct measurement, and reduction of the ablation rate would compromise the sensitivity for trace elements. Due to the high stability of ICP-unit and mass filter of the instrument used, it was found that the tail of a mass-peak of the matrix element could be used as an internal standard. Therefore, a position at –0.5 amu from the matrix-isotope (e.g. ^62.5Cu in copper samples) was used for internal standardization. The standard deviation of this signal in a period of 2.5 h was 3.6% RSD with no notable drift when the laser ablation was used for sample introduction. The calibration of the matrix-element by nebulizing liquid standards showed that the ion signal measured on the peak-tail is directly proportional to the element concentration in the ICP. This indicates that the peak shape is not only stable, but also independent of the peak height. The advantages of this method lie in the easy preparation of calibration standards for quantitative measurements with a laser-ablation system and access to homogeneous standards for materials, that are difficult to homogenize in the solid state. The calibration of the traces is performed relatively to a fixed concentration of the matrix element. Calibrations were carried out for trace concentrations in high purity copper and good recoveries were obtained for high-purity reference standards. Received: 23 February 1998 / Revised: 20 July 1998 / Accepted: 25 July 1998     

Determination of uranium in marine sediment pore waters by isotope dilution inductively coupled plasma mass spectrometry

Inductively coupled plasma mass spectrometry (ICP-MS) was used in an isotope dilution mode to assay small-volume (0.25 ml) sediment pore waters for their uranium contents, using ²³⁶U as the spike. The only pretreatment required was a simple dilution by a factor of 20, which gave sufficient volume for three replicate analyses per sample. Rapid and accurate results were obtained for a variety of samples and standards, ranging in concentration from 0.05 to 10 ng U ml^?1. A suite of 30 samples can be analysed in less than 6 h by this method. The relative standard deviation was better than 1.9%, with a detection limit, based on 3σ background, of 2 pg U ml^?1 in solution (40 pg ml^?1 in samples). Sea water is a difficult matrix for ICP-MS and thus the method is generally suitable for uranium determinations in many other sample solutions.     

Development of a procedure for the multi-element determination of trace elements in wine by ICP-MS

An inductively coupled plasma mass spectrometric (ICP-MS) procedure has been developed for the determination of trace elements in wine. The procedure consists in simple 1+1 dilution of the wine and semi-quantitative analysis (without external calibration) using In as internal standard. Thirty-one elements at concentrations ranging from 0.1 mg mL(-1) to 0.5 ng mL(-1) can be determined by ICP-MS analysis with and without digestion. It was investigated whether a matrix effect observed for EtOH in the wine matrix can be overcome by application of a micro-concentric nebulizer with a membrane desolvator (MCN 6000). The results obtained for the MCN 6000 are compared with those obtained by use of a conventional Meinhard nebulizer. It is shown that the observed matrix effect can only be compensated by use of an internal standard for the Meinhard nebulizer, but not for the MCN 6000. Results for ICP-MS are compared with those obtained by total reflection X-ray fluorescence spectrometry (TXRF).     

液相色谱-串联质谱法测定果蔬中双三氟虫脲、四氯虫酰胺和氰虫酰胺残留

建立了蔬菜和水果中双三氟虫脲、四氯虫酰胺和氰虫酰胺3种新型杀虫剂的分散固相萃取-液相色谱-串联质谱检测方法.样品经乙腈均质提取,混合使用乙二胺-N-丙基硅烷(PSA)和C18基质分散净化剂进行净化,液相色谱-三重四极杆串联质谱(LC-MS/MS)同时进行检测.双三氟虫脲和四氯虫酰胺采用多反应监测负离子模式,氰虫酰胺采用多反应监测正离子模式.双三氟虫脲在苹果、洋葱和经微波处理的洋葱样品中均不存在基质效应,可采用纯溶剂标准外标法或者采用基质匹配标准溶液定量检测; 四氯虫酰胺和氰虫酰胺存在程度不同的基质减弱效应,采用空白基质匹配的校正标准曲线外标法定量.3种杀虫剂均在0.2～100 μg/L线性范围内具有良好的线性关系,相关系数均大于0.9990.在0.005～2.000 mg/kg范围内,平均添加回收率为81.6％～99.9％,相对标准偏差为3.6％～9.8％.氰虫酰胺、四氯虫酰胺和双三氟虫脲的检出限分别为0.064,0.048和0.001 μg/kg,定量限分别为0.210, 0.160和0.004 μg/kg.