电感耦合等离子体-质谱法测定高纯硫粉末中17种痕量杂质

建立电感耦合等离子体-质谱(ICP-MS)法测定高纯硫粉中Si、P、V、Cr、Mn、Ni、Co、Cu、As、Zn、Zr、Cd、In、Sb、Te、Pb、Bi等17种痕量金属杂质含量的方法。样品用HClO4溶解后挥发硫基体,使样品中杂质元素得到富集,各杂质元素的方法检出限为0.1～50ng/g。方法加标回收率为83%～117%。各杂质元素均为10ng/mL的混合标准溶液平行7次测定的相对标准偏差均小于5%。该方法能够满足纯度为99.999%～99.9999%的高纯硫样品中杂质测定的需要。     

电感耦合等离子体质谱法测定高纯金属铋中痕量杂质元素

采用电感耦合等离子体质谱法测定了高纯金属铋中14种痕量杂质元素。考察了基体效应对测定元素的干扰影响,通过铋基体元素的分离和以Sc、In、Eu作为内标,有效克服了干扰现象。方法的检出限在0．1～4．7ng/mL;精密度在1．4％～5．0％;加标回收率在89％～114％范围。本法可满足99．999％以上金属铋中痕量杂质测定的要求。     

电感耦合等离子体质谱法测定高纯镓中痕量杂质

采用电感耦合等离子体质谱（ICP-MS）测定高纯镓中痕量杂质元素,以Rh作为内标补偿校正镓基体的抑制效应,采用异丙醚萃取分离镓与ICP-MS技术联用,拓展分析方法应用范围,可满足99.9999%-99.99999%超高纯镓分析方法要求。方法检出限为0.006-0.062μg/L;加标回收率为86.8%-121.4%之间;RSD为1.1%-8.6%。     

电感耦合等离子体质谱法测定烟酰胺药物元素杂质

建立了烟酰胺药物中30种元素杂质的ICP-MS分析方法,并根据USP< 233>进行了验证,在优化的实验条件下,本方法的检出限在4.0×10-4～0.4μg/L之间,加标回收率在86.3％～116.0％之间,与ICP-OES检测结果基本一致.用所建立方法对烟酰胺以及稳定性样品进行了元素杂质检测,根据样品制备工艺初步判断元素杂质的来源.     

离子交换色谱-电感耦合等离子体质谱法测定高纯钛中痕量杂质元素

建立了离子交换色谱-电感耦合等离子体质谱(ICP-MS)测定高纯钛中Mg、Cr、Fe、V、Mn、Co、Ni、Cu、Zn、Sr、Cd、Ba、Tl、Pb等痕量杂质元素分析方法,并对ICP-MS工作参数及条件进行了优化和选择.高纯钛用HF和HNO3溶解后进入离子色谱的阳离子交换柱,经HF(3+97)淋洗后,用HNO3洗脱,洗脱下来的溶液进入电感耦合等离子体质谱检测.方法的检出限在0.00099～0.85 μg/L之间,测定下限为0.0033～2.8 μg/L,各元素的回收率在90%～110%之间.利用本方法对纯度＞99.99%高纯钛样品的杂质元素进行分析,结果表明,其精密度和准确度均满足痕量分析的要求.     

电感耦合等离子体质谱法测定烟酰胺药物元素杂质

建立了烟酰胺药物中30种元素杂质的ICP-MS分析方法,并根据USP< 233>进行了验证,在优化的实验条件下,本方法的检出限在4.0×10-4～0.4μg/L之间,加标回收率在86.3％～116.0％之间,与ICP-OES检测结果基本一致.用所建立方法对烟酰胺以及稳定性样品进行了元素杂质检测,根据样品制备工艺初步判断元素杂质的来源.     

高纯金属镱中杂质元素的电感耦合等离子体质谱法测定

利用电感耦合等离子体质谱仪(ICP—MS)直接测定了金属镱中除Tm、Lu外其他稀土及非稀土杂质元素;通过P507萃淋树脂色层柱,分离绝大部分Yb基体,避免了基体元素对Tm、Lu的测定干扰?定量加入内标元素Sc、Cs,有效克服了基体效应所带来的偏差。稀土杂质元素的检出限0．010～0．032μg／g,非稀土杂质元素的检出限为0.12～5．0μg／g。加标回收率为83％～105％。方法适用于纯度为99．99％～99．999％的高纯金属镱产品中杂质元素的测定。     

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。     

电感耦合等离子体质谱法测定高纯铝中杂质元素

高纯铝样品经盐酸(1+1)溶液微波消解,采用电感耦合等离子体质谱法测定所得样品溶液中钛、铁、铜、锌、镓、银、镉、铟和铅等杂质元素的含量。选择适当的待测元素的同位素克服了质谱干扰,定量加入50μg·L~(-1)铯和锗内标元素有效地校正了基体效应。选用碰撞室技术消除了多原子离子对部分被测元素的干扰。结果表明:方法的检出限(3s)在0.003～0.042μg·L~(-1)之间。高纯铝样品中9种元素测定结果的相对标准偏差(n=10)在2.9%～9.5%之间。方法用于精铝标准样品(R11C)的测定,结果与认定值基本相符。     

电感耦合等离子体质谱法测定高纯铌中20种痕量杂质元素北大核心CSCD

高纯铌样品0.050 0g中加入适量的水,缓慢加入1mL氢氟酸和2mL硝酸,低温加热使其溶解,冷却至室温,用水定容至100mL。采用电感耦合等离子体质谱法测定所得溶液中20种痕量杂质元素,以内标法定量。结果表明:20种元素的检出限(3s)为0.005～0.20μg·g-1,回收率为95.0%～110%。按所提出方法分析铌锭样品,所得结果与辉光放电质谱法所得结果相符。     

Direct determination of rare earth impurities in high purity erbium oxide dissolved in nitric acid by inductively coupled plasma mass spectrometry

A novel method was developed for the direct determination of trace quantities of rare earth elements (REEs) in high purity erbium oxide dissolved in nitric acid by inductively coupled plasma mass spectrometry (ICP-MS) in this work. The mass spectra overlap interferences arose from Er matrix on the neighbouring and monoisotopic analytes of ¹⁶⁵Ho(100) and ¹⁶⁹Tm(100) were eliminated by adjusting instrumental peak resolution value from 0.7 to 0.3 amu. The matrix suppression effect of Er on the ion peak signals of REEs impurities was effectively compensated with spiking In as internal standard element. The limit of quantitation (LOQ) of REEs impurities was from 0.0090 to 0.025 μg g⁻¹, the recoveries of spiked sample for REEs were found to be in the range of 90.3-107% through using the proposed method and relative standard deviation (R.S.D.) varied between 2.5% and 6.7%. The novel methodology had been found to be suitable for the direct determination of trace REEs impurities in 99.999-99.9999% high purity Er₂O₃ and the results obtained from this method keep in good agreement with that acquired from high resolution ICP-MS.     

萃取分离-ICP-MS测定高纯铝中痕量元素

利用吡咯烷二硫代氨基甲酸铵(APDC)-CHCl_3萃取分离体系结合ICP-MS对高纯铝中的Co、As、Mo、In、Sn、Sb、Cd、Ag、Pd、Au进行测定,建立了测定高纯铝中痕量元素的方法.实验分别考察了仪器工作参数,萃取酸度,络合剂用量对于杂质元素测定结果的影响,选择了最佳实验条件.各元素的回收率在77.6%～112.2%之间,检出限0.02～0.6 ng/mL,RSD为1.6%～7.2%.     

电感耦合等离子体质谱法测定高纯氧化钽中28种痕量杂质元素

建立了用电感耦合等离子体质谱仪(ICP-MS)测定高纯氧化钽中28种痕量杂质元素的方法。讨论了质谱干扰及接口效应,采用标准加入法消除基体效应。各元素的方法检出限为0.001~0.1μg/g,回收率为90%~115%,方法适用于纯度为99.999%的高纯氧化钽中痕量杂质元素的测定。     

Direct determination of impurities in high purity silicon carbide by inductively coupled plasma optical emission spectrometry using slurry nebulization technique

A novel method for the determination of Al, Ca, Cr, Cu, Fe, Mg, Mn, Ni and Ti in high purity silicon carbide (SiC) using slurry introduction axial viewed inductively coupled plasma optical emission spectrometry (ICP-OES) was described. The various sizes of SiC slurry were dispersed by adding dispersant polyethylene imine (PEI). The stability of slurry was characterized by zeta potential measurement, SEM observation and signal stability testing. The optimal concentration of PEI was found to be 0.5 wt% for the SiC slurry. Analytical results of sub-μm size SiC by the slurry introduction were in good accordance with those by the alkaline fusion method which verified that determination could be calibrated by aqueous standards. For μm size SiC, results of most elements have a negative deviation and should be calibrated by the Certified Reference Material slurry. Owing to a rather low contamination in the sample preparation and stability of the slurry, the limits of detection (LODs), which are in the range of 40-2000 ng g⁻¹, superior to those of the conventional nebulization technique by ICP-OES or ICP-MS.     

电感耦合等离子体质谱法测定高纯钼中12种杂质元素

采用反应池技术消除了复合离子对Ca、Fe和Si等元素的干扰,以内标校正法直接测定了其它9种元素。优化选择了测定同位素和内标元素,考察了基体效应对测定结果的影响,建立了电感耦合等离子体质谱测定了高纯钼中12种杂质元素含量的方法。方法测定下限介于0.10～0.37μg/g之间,加标回收率为93％～105％,RSD＜10％。...     

电感耦合等离子体质谱法测定高纯金中铝、砷、铋、铬、铁、铅、锑、硒、碲、铱痕量元素

建立了微波消解-内标法-标准加入-ICP-MS法测定高纯黄金中铝、砷、铋、铬、铁、铅、锑、硒、碲、铱等痕量元素的分析方法.从试样溶解方式、内标元素及同位素的选择、仪器检测模式的优化及降低基体抑制效应等方面进行优化.实验加标回收率为99.5％ ～110％,相对标准偏差(RSD)为0.050％ ～6.5％.实验的准确度和精...     

Determination of impurities in strontium titanate ceramics by inductively coupled plasma mass spectrometry

The determination of impurities in SrTiO₃ by ICPMS was investigated. The sample was decomposed with hydrochloric and hydrofluoric acids in a PTFE pressure vessel. The internal standard method using Au was selected to eliminate an ion count suppression by the Sr and Ti matrix. Impurities at sub g/ml level in SrTiO₃ were determined. The detection limits were in the range of 0.008 to 0.01 g/g.     

Radionuclide determination in environmental samples by inductively coupled plasma mass spectrometry

The determination of naturally occurring and anthropogenic radionuclides in the environment by inductively coupled plasma mass spectrometry has gained recognition over the last fifteen years, relative to radiometric techniques, as the result of improvement in instrumental performance, sample introduction equipment, and sample preparation. With the increase in instrumental sensitivity, it is now possible to measure ultratrace levels (fg range) of many radioisotopes, including those with half-lives between 1 and 1000 years, without requiring very complex sample pre-concentration schemes. However, the identification and quantification of radioisotopes in environmental matrices is still hampered by a variety of analytical issues such as spectral (both atomic and molecular ions) and non-spectral (matrix effect) interferences and instrumental limitations (e.g., abundance sensitivity).The scope of this review is to highlight recent analytical progress and issues associated with the determination of radionuclides by inductively coupled plasma mass spectrometry. The impact of interferences, instrumental limitations (e.g., degree of ionization, abundance sensitivity, detection limits) and low sample-to-plasma transfer efficiency on the measurement of radionuclides by inductively coupled plasma mass spectrometry will be described. Solutions that overcome these issues will be discussed, highlighting their pros and cons and assessing their impact on the measurement of environmental radioactivity. Among the solutions proposed, mass and chemical resolution through the use of sector-field instruments and chemical reactions/collisions in a pressurized cell, respectively, will be described. Other methods, such as unique sample introduction equipment (e.g., laser ablation, electrothermal vaporisation, high efficiency nebulization) and instrumental modifications/optimizations (e.g., instrumental vacuum, radiofrequency power, guard electrode) that improve sensitivity and performance will also be examined.