微波消解样品-电感耦合等离子体原子发射光谱法测定铅精矿中铅、砷、镉、汞

采用微波消解样品-电感耦合等离子体原子发射光谱法同时测定铅精矿中主体元素铅及有毒有害元素砷、镉、汞的含量。0.20g试样置于消解罐中,先后加入硝酸9mL、盐酸3mL、氟硼酸2mL及过氧化氢2.5mL,密闭罐盖按设定的微波消解程序进行消解。试验选择铅、砷、镉和汞的分析线分别为220.351,189.042,228.802,184.950nm以消除基体干扰。铅、砷、镉、汞的检出限分别为16.0,2.2,0.4,0.8μg.g-1。方法用于铅精矿标准样品(GBW 07617)和铅精矿实际样品分析,此方法的测定值与认定值及原子吸收光谱法或原子荧光光谱法的测定值相一致。方法的相对标准偏差(n=10)在0.15%～3.9%之间。     

电感耦合等离子体质谱法测定水产品中铬、铜、锌、砷、镉、铅的含量北大核心CSCD

取水产品样品0.500 0 g,加入硝酸5 mL、水2 mL、30%(质量分数)过氧化氢溶液1 mL,按微波消解程序进行消解,将消解液于100℃蒸发至1~2 mL,用水定容至25 mL。采用电感耦合等离子体质谱法测定上述溶液中铬、铜、锌、砷、镉、铅的含量。各元素测定值的相对标准偏差(n=6)在1.2%~5.9%之间,回收率在96.6%~102%之间。按上述方法分析标准物质GBW 10023、GBW 10024、GBW 10050,FAPAS质控基准物质TET012RM以及质控样品T07225QC,各元素测定值与认定值一致。     

电感耦合等离子体质谱法测定水产品中铬、铜、锌、砷、镉、铅的含量

取水产品样品0.500 0 g,加入硝酸5 mL、水2 mL、30%(质量分数)过氧化氢溶液1 mL,按微波消解程序进行消解,将消解液于100℃蒸发至1~2 mL,用水定容至25 mL。采用电感耦合等离子体质谱法测定上述溶液中铬、铜、锌、砷、镉、铅的含量。各元素测定值的相对标准偏差(n=6)在1.2%~5.9%之间,回收率在96.6%~102%之间。按上述方法分析标准物质GBW 10023、GBW 10024、GBW 10050,FAPAS质控基准物质TET012RM以及质控样品T07225QC,各元素测定值与认定值一致。     

电感耦合等离子体质谱法测定有机肥料中砷、镉、铅、铬、汞的含量

提出了用微波消解-电感耦合等离子体质谱法测定有机肥料中砷、镉、铅、铬、汞等5种元素的方法。有机肥料样品(0.200 0~0.500 0g)加入硝酸10mL和过氧化氢溶液1mL,按程序升温微波消解,将消解液蒸发至2mL,用硝酸(1+99)溶液定容至50mL。用电感耦合等离子体质谱法测定上述样液中的砷、镉、铅、铬、汞等元素。各元素的检出限(3.3s/k)为0.015~0.040mg·kg~(-1),测定值的相对标准偏差(n=6)均小于5.0%。按标准加入法进行回收试验,测得回收率在98.0%~101%之间。     

微波消解试样-火焰原子吸收光谱法测定猪肝中镉

将绞碎、混匀的猪肝试样用浓硝酸及过氧化氢在MDS 2003型微波消解仪中消解。微波输出功率为650 W,采用程序升压消解方式,即先后在0.5 MPa压力下消解2 min,在1.0 MPa消解2 min及在1.5 MPa消解1 min。将经冷却室温的无色透明的消解液移入50 mL容量瓶中,加入硝酸(1+99)溶液2 mL,加水定容,按设定的仪器工作条件用火焰原子吸收光谱法测定其镉的含量。方法的检出限(3s/k)为0.20μg.L-1。以同一试样为基体,用标准加入法对方法作回收及精密度试验,测得回收率在94.0%~116.0%之间,测定值的相对标准偏差(n=5)在0.66%~3.25%之间。     

微波消解-原子荧光光谱法测定海洋生物体中汞

应用原子荧光光谱法测定海洋生物体中汞的含量。试样用盐酸、硝酸和过氧化氢混合溶液在微波消解仪中消解处理,经试验选定消解程序为:①消解功率1 600 W;②5min升温至120℃,保持5min;③5min升温至160℃,保持10min。分析时仪器工作条件为负高压260V,灯电流为40mA,载气流量为800mL.min-1。汞的质量浓度在0.80μg.L-1以内与相应的荧光强度呈线性关系,方法检出限(3s/k)为0.002mg.kg-1。方法用于测定海洋生物体中汞的含量,测定值的相对标准偏差(n=6)在2.7%～6.0%之间,加标回收率在90%～104%之间。     

电感耦合等离子体质谱法测定卷烟用纸中铜、砷、钼、镉、铊和铅

采用电感耦合等离子体质谱法测定了卷烟纸中铜、砷、钼、镉、铊和铅等6种杂质金属元素。试样用硝酸、过氧化氢及氢氟酸在Multiwave 3000型微波消解仪中消解处理,在所得消解后的溶液中加入硼酸溶液络合过量的氢氟酸。加入含115In及209Bi各20μg.L-1的混合溶液作为内标。上述6种元素在一定浓度范围内与各相应的分析信号值之间呈线性关系,其检出限(3S/N)在0.002～0.16μg.L-1之间。按标准加入法测得方法的回收率在95.3%～113.0%之间。试验了方法的重复性,其相对标准偏差(n=5)在0.9%～4.6%之间。     

石墨炉原子吸收光谱法测定水生动物中的铬

采用硝酸和过氧化氢对匀浆过的水生动物进行微波消解,石墨炉原子吸收光谱法测定鱼肉中的铬含量。首先,对微波消解酸体系和微波程序进行了优化,硝酸用量为2.5 mL、过氧化氢用量为2.0mL,逐步升温到190 ℃,消解28 min时试剂用量少,消解效果较好;然后用石墨炉原子吸收分光光度仪对几种水生生物中的铬进行测试,方法检出限为0.02㎎/㎏,测定结果的相对标准偏差为0.010％～0.056％（n=6）,加标回收率为83％～105％。结果表明：生长期长,生活在水体底部的水生生物中的铬含量相对较高.     

电感耦合等离子体质谱法测定紫甘薯中痕量元素

用硝酸和过氧化氢在MDS-6型微波消解仪中处理紫甘薯试样,用电感耦合等离子体质谱法测定13种试样中痕量元素的含量。用动态反应池技术消除质谱测定中的光谱干扰。在优化试验条件下,方法的检出限(3S/N)在0.015～1.890μg·L~(-1)范围,方法用于紫甘薯中痕量元素的测定,加标回收率在94%～102%之间。     

微波消解样品-离子色谱法测定卷烟纸中钠、钾、镁、钙的含量

提出了离子色谱法同时测定卷烟纸中钠、钾、镁和钙含量的方法。卷烟纸试样经硝酸-过氧化氢-氢氟酸微波消解,以IonPac CS16阳离子交换柱为固定相,用0.027 mol.L-1甲烷磺酸溶液作流动相。钠、钾、镁和钙4种元素在30 min内可完全分离;各离子的检出限(3S/N)分别为13,15,8.1,97 mg.L-1。方法的加标回收率在100.9%～108.8%之间,测定值的相对标准偏差(n=5)在0.87%～3.4%之间。     

ICP–OES法测定八氧化三铀中杂质元素钨

以ICP–OES法测定八氧化三铀中杂质元素钨。采用浓HNO3–浓HCl、浓HNO–HF、3 mol/L HNO3三步酸溶方案,利用CL–TBP萃淋树脂将铀基体分离,淋洗液基质为3 mol/L HNO3,淋洗液流速为1 mL/min。弃去最初2 mL死体积淋洗液后接收10 mL,分离回收率平均值为95.93%,线性方程为y=539.71x+16.6,相关系数r2=0.999 7,4水平样品测定结果的相对标准偏差为0.39%~3.12%(n=6)。用该方法对标准物质进行测定,测定结果在参考值范围内。     

硝酸铅滴定法测定延期药中氧化铜

以硝酸和H2O2对延期药中铅化合物和氧化铜完成溶解,通过硫脲释放,采用硝酸铅滴定法测定延期药中的氧化铜。加入30 mL HNO3溶液(1+8)和15 mL六次甲基四胺控制样品溶液为pH 5～6。结果表明,方法的回收率为98.8%～99.9%,测定结果的相对标准偏差为0.12%～0.2%(n=6)。该方法准确可靠,可用于延期药中氧化铜分析。     

石墨炉原子吸收光谱法测定土壤中铅、镉含量

土壤样品经硝酸、氢氟酸和过氧化氢加热消解,采用石墨炉原子吸收光谱法测定其中铅和镉的含量。以磷酸铵作为基体改进剂,铅和镉的灰化温度分别为400℃,250℃,原子化温度分别为2 100℃,1 800℃。铅和镉的质量浓度分别在0.50～50.0,0.10～2.5μg.L-1范围内与其吸光度呈线性关系,检出限依次为6.5,0.4pg。应用此法分析了4个土壤标准样品,测定值与标准值相符,相对标准偏差(n=6)分别在1.5%～6.3%和2.3%～5.1%之间。铅、镉的加标回收率分别在85.4%～103.2%,91.5%～102.3%之间。     

Comparison of sample preparation procedures for the determination of trace heavy metals in house dust, tobacco and tea samples by atomic absorption spectrometry

The effect of wet ashing, dry ashing and microwave procedure for the determination of trace metal levels was investigated in house dust, tobacco and tea samples by atomic absorption spectrometry. The study of sample preparation procedures showed that the microwave method was the best. The recovery of trace metals was very good and precision and accuracy were compatible with standard reference material. The relative standard deviations for all measured metal concentrations were lower than 10%. The digestions of HNO3/H2SO4/HClO4 (4: 1: 1) mixture for house dust, HNO3/H2SO4/H2O2 (2: 2: 2) mixture for tea and HNO3/H2O2 (4: 2) mixture for tobacco were very efficient.     

电热原子吸收光谱法测定水中总钼

建立电热原子吸收法测定水中总钼的含量。样品采用硝酸–过氧化氢消解,热解涂层石墨管减小记忆效应,塞曼背景校正消除背景噪声。检测了27种共存离子的干扰影响。经6家实验室对标准物质和实际样品检测验证,方法检出限为0.6μg/L,能够满足微量检测要求。钼测定结果相对误差最大值为–6.2%,实验室内相对标准偏差为4.5%~7.6%(n=6),实验室间相对标准偏差为4.3%~5.7%(n=6),加标回收率为91.8%~104.0%。该方法精密度和准确度满足我国地下水和废水监测技术规范的质控要求。     

蒸馏-催化极谱法测定复杂物料中微量砷

提出了用催化极谱法测定复杂物料中微量砷的含量。选择测定的溶液介质中含碲(Ⅳ)硫酸溶液5mL和150g.L-1碘化钾溶液5mL。仪器扫描速率为250mV.s-1,并采用二阶导数测定。试样(0.01～1.0g)用氯酸钾0.5g、氢氟酸5滴、硝酸5～10mL溶解,用蒸馏法分离其中的砷。砷的质量浓度在0.4mg·L-1以内与相应的峰电流呈线性关系。按此方法测定了12个矿样中砷含量,其测定值与已知值相符。方法的回收率在97%～100%之间,相对标准偏差(n=6)在2.3%～7.2%之间。     

微波消解样品-电感耦合等离子体原子发射光谱法测定竹叶中9种必需微量元素

竹叶样品置于聚四氟乙烯罐中,加入硝酸及过氧化氢后在微波消解仪中按设定程序加热消解。所得样品溶液定容至25mL后用电感耦合等离子体原子发射光谱法测定其中铬、锌、镍、钴、铁、硼、锰、铜和锶等9种元素的含量。9种元素的质量浓度在0.05～2.00mg.L-1范围内与其发射强度呈线性关系,方法的检出限(3s)在0.04～0.50μg.g-1之间。方法应用于分析了一种杨树叶标准物质(GBW 07604),所得9种元素的测定结果与证书值相符。方法的回收率在87.0%～107.6%之间。     

微波消解-GFAAS法测定菠菜粉和蘑菇粉中微量镉的研究

应用微波消解-石墨炉原子吸收光谱法对菠菜粉和蘑菇粉中微量镉的含量进行测定。菠菜粉和蘑菇粉经HNO3+H2O2微波消解体系消解后,采用磷酸二氢铵作为基体改进剂,灰化温度为900℃,原子化温度为1 350℃,镉含量在0~2 ng/mL范围内与吸光度呈线性关系,线性相关系数为0.999 4,检出限为0.02 mg/kg。该法测定结果的相对标准偏差小于4%(n=6),加标回收率为96.7%~103.2%。     

Microwave assisted digestion of atmospheric aerosol samples followed by inductively coupled plasma mass spectrometry determination of trace elements

A microwave digestion method in a closed vessel was developed for the determination of trace metals in atmospheric aerosols using inductively coupled plasma mass spectrometry (ICP-MS). A recovery study for the elements V, Cr, Mn, Fe, Co, Ni, Cu, Zn, As, Se, Cd, Sb, and Pb was conducted using multi-elemental standard solutions, NIST 1633b Trace Elements in Coal Fly Ash, and NIST 1648 Urban Particulate Matter. A simple digestion method using only HNO3/H2O2 gave good recoveries (90%-108%) for all elements except Cr in SRM 1648, but yielded low recoveries for SRM 1633b. A more robust method using HNO3/H2O2/HF/H3BO3 yielded higher recoveries (82%-103%) for the lighter elements (V-Zn) in SRM 1633b, and improved the Cr recovery in SRM 1648, but decreased the Se recovery in both SRMs. A comparative analysis of aerosol samples obtained at a remote mountain location Nathiagali, Pakistan (2.5 km above mean sea level), and Mayville, New York, downwind from the highly industrialized Midwestern United States, was carried out using Instrumental Neutron Activation Analysis (INAA) for the elements Cr, Mn, Fe, Co, Zn, As, Se, and Sb. The simple digestion method yielded excellent agreement for Cr, Fe, Zn, As, Se, and Sb, with slopes of the ICP-MS vs. INAA regressions of 0.90-1.00 and R2 values of 0.96-1.00. The regressions for Mn and Co had slopes of 0.82 and 0.84 with R2 values of 0.83 and 0.82, respectively. Addition of HF/H3BO3 did not improve the correlation for any of the elements and degraded the precision somewhat. The technique provides sensitivity and accuracy for trace elements in relatively small aerosol samples used in atmospheric chemistry studies related to SO2 oxidation in cloud droplets. The ability to determine concentrations of a very large number of elements from a single analysis will permit source apportionment of various trace pollutants and hence strategies to control the sources of air pollution. This is particularly important as the health effects of particulate matter are increasingly recognized.     

Use of microwave digestion and atomic absorption spectrophotometry to determine chromic oxide as a digestibility marker in feed, feces, and ileal content.

Most conventional digestion procedures, such as dry ashing and wet ashing, are tedious and labor intensive. Microwave digestion is a good alternative, because microwave dissolution is faster, safer, and simpler, and provides more controlled reproducible conditions than conventional methods. The purpose of this study was to develop a microwave digestion method for mineralizing meat and bone meal diets, feces, and ileal contents. Each sample was heated on a hot plate for 10 min, dry ashed at 65 degrees C for 4 h, and transferred into microwave vessels. Then, 10 mL 70% HNO3 was added. Samples were digested for 7, 10, and 20 min at 95, 90, and 85% power, respectively. After the heating cycle, 6 mL 30% H2O2 was added, and samples were returned to the microwave for a second heating cycle of 1 and 7 min at 95% and 90% power, respectively. Finally, chromium concentration was determined by flame atomic absorption spectrophotometry. The digestion method was validated by using a standard reference material, SRM domestic sludge 2781, with a certified chromium value of 195 +/- 9 micrograms/g. The value obtained in this study was 178 +/- 11 micrograms/g, for a difference of 17 micrograms/g. Spike recovery experiments resulted in 103.16 and 100.35% recoveries of chromium from diet and feces samples, respectively. Coefficients of variation were 10.8 and 7.8%, respectively.