微波消解ICP-AES法测定高速工具钢中锰、磷、镍、铜、铬、钒

高速工具钢为高碳高合金工具钢,常温下样品酸溶分解较为困难。本文利用微波消解提高溶样的温度和压力,在王水、氢氟酸和硫酸介质中使样品充分消解,再用饱和硼酸溶液络合过量的氢氟酸,基体匹配消除铁基体的影响,ICP-AES法同时测定锰、磷、镍、铜、铬、钒的含量。测定高速工具钢标样,测定值与标样值相吻合,本方法的精密度在0.55%～4.06%。加标回收率在95.6%～114.8%,满足测定要求。     

分类消解-电感耦合等离子体原子发射光谱法测定环境土壤中15种金属元素的含量

测定土壤中铍、锌、钼、铊、钛、锑等6种元素以硝酸-氢氟酸-高氯酸混合酸为消解体系,采用全自动消解法进行消解;测定土壤中钒、锰、钴、镍、铜、镉、钡、铅、铬等9种元素以硝酸-氢氟酸-盐酸混合酸为消解体系,采用微波消解法进行消解。以氩为内标元素校正土壤基体的雾化效率及电离效率。电感耦合等离子体原子发射光谱法(ICP-AES)采用多向观测模式,结合多重谱线拟合技术(MSF)校正光谱干扰,测定环境土壤中上述15种元素的含量,检出限为0.1~3.7 mg·kg~(-1)。按上述方法测定标准样品GSS~(-1)0和GSS~(-1)3,各元素的测定值与认定值吻合,相对标准偏差(n=11)为0.15%~2.6%。以吉林市某河岸土壤为实际测定样品,各元素的测定值与电感耦合等离子体质谱法(ICP-MS)的测定值一致,相对标准偏差(n=11)为1.6%~4.5%。     

电感耦合等离子体原子发射光谱法测定钨钢中硅、锰、磷、铬、镍、铜、钼、钒和钨

采用电感耦合等离子体原子发射光谱法测定钨钢中硅、锰、磷、铬、镍、铜、钼、钒和钨的含量。试样用盐酸、柠檬酸铵、硝酸溶解。基体效应采用基体匹配法消除。硅、锰、磷、铬、镍、铜、钼、钒、钨的分析谱线依次为288.158,257.610,177.495,267.716,213.604,327.396,204.598,310.230,239.709nm。9种元素的质量分数在一定的范围内与其发射强度呈线性关系,方法的检出限(3s)在0.000 3%~0.004 8%之间。方法用于两种标准物质的测定,测定结果与认定值相符,测定值的相对标准偏差(n=5)在0.74%~2.1%之间。方法的回收率在95.0%~107%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镍精矿中10种金属元素

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镍精矿样品中铝、钙、钴、铬、铜、锰、镁、镍、铅、锌等10种金属元素的含量。0.200 0g试样置于消解罐中,先后加入盐酸2mL、硝酸6mL及氢氟酸1mL,密闭罐盖按设定的微波消解程序进行消解。试验选择铝、钙、钴、铬、铜、镁、锰、铅、锌和镍的分析线分别为308.215,317.933,228.616,267.716,324.745,279.079,257.610,220.353,206.200,231.604nm,配制工作曲线时采用基体匹配的方法消除基体干扰。方法用于镍钴矿标准样品(GBW 07283)和镍精矿实际样品的分析,此方法的测定值与认定值及国标方法的测定值相一致。方法的回收率在95.8%～103.1%之间,相对标准偏差(n=6)均小于4.5%。     

微波消解-电感耦合等离子体质谱法测定高纯五氧化二钒中15种杂质元素

高纯五氧化二钒样品在硝酸-氢氟酸(4+1)混合液中经微波消解处理,采用电感耦合等离子体质谱法测定样品溶液中15种杂质元素(钛、硅、铝、铬、镍、铜、铅、砷、磷、铁、锰、钙、镁、钾、钠)的含量。采用内标法消除基体的影响。方法的检出限(3s/k)在0.03~0.89μg·L-1之间。方法的加标回收率在90.0%~113%之间,相对标准偏差(n=8)小于5.0%。五氧化二钒5号样品中8种杂质元素的测定值与石墨炉原子吸收光谱法进行核对,测得结果互相符合。     

微波消解-电感耦合等离子体质谱法测定粮食中12种重金属元素

粮食样品用硝酸-过氧化氢微波消解处理,采用电感耦合等离子体质谱法测定样品溶液中12种重金属元素(砷、铅、镉、硒、铬、铊、锰、镍、铜、铀、钴、钒)的含量。采用内标法消除基体的影响。方法的检出限(3S/N)在0.092~17.5pg·g-1之间。方法的加标回收率在88.1%~118%之间,相对标准偏差(n=5)小于6.0%。方法用于鸡肉标准物质(GBW 10018)中重金属含量的测定,测定值与认定值相符。     

电感耦合等离子体原子发射光谱法(ICP-OES)测定含钒尾渣中钒的含量

以氢氟酸、硝酸消解样品,然后加入硫酸络合钛避免其在低酸度介质中水解,并且加热至产生三氧化硫烟以驱赶氢氟酸,以水稀释定容后采用电感耦合等离子体原子发射光谱法（ICP-OES）直接测定含钒尾渣中钒的含量。实验考察了在共存含有铁、钛、铝、铬、锰、钒等元素的含钒尾渣复杂基体中,基体效应、光谱干扰以及背景噪音等影响因素对钒测定的干扰,方法通过优选元素分析谱线、背景校正区域以及光谱仪工作条件,并且采用基体匹配法和同步背景校正法相结合的方式,消除了构成复杂且变化无常的样品基体对测定的影响。结果表明,方法可用于测定0.01%~6.0%的钒,并且样品基体在含20%~40%铁,5%~30%钛时,铝、铬、锰、钠、硅、钙、镁各元素1%~10%的变化对测定无影响,检测下限可达0.0009%;精密度RSD〈3%,加标回收率94%~106%,与高锰酸钾氧化-硫酸亚铁铵滴定化学分析法的测定结果对照一致。     

区域地球化学样品中磷、钒、铬、镍、硒等13元素的高效测定方法研究

本文采用硝酸、氢氟酸、高氯酸等三种混合酸预消解,再用王水、盐酸分两次复溶提取,电感耦合等离子体质谱仪（ICP-MS）测定钴、铜、钼、铅、镉,电感耦合等离子体发射光谱仪（ICP-OES）测定磷、钒、铬、锌、钾、镍、锰,原子荧光发射光谱仪（AFS）测定硒,最终实现区域地球化学样品中磷、钒、铬等13元素的准确、高效、组合测定。在选定的实验条件下,各元素的检出限分别为：磷8.42μg·g-1、钒2.55μg·g-1、铬2.00μg·g-1、镍0.50μg·g-1、锌2.00μg·g-1、氧化钾0.05μg·g-1、锰8.00μg·g-1、钴0.20μg·g-1、铜0.80μg·g-1、钼0.10μg·g-1、镉0.01μg·g-1、铅1.70μg·g-1、硒0.01μg·g-1;准确度分别为：砷0.000~0.011、钒0.001~0.002、铬0.001~0.002、镍0.002~0.012、锌-0.008~0.009、氧化钾-0.001~0.005、锰0.003~0.006、钴0.005~0.008、铜0.001~0.006、钼-0.003~0.002、镉0.002~0.020、铅0.003~0.007、硒-0.007~0.008;精密度分别为：磷1.11%~2.95%、钒1.91%~2.52%、铬1.02%~3.41%、镍1.89%~5.56%、锌1.37%~3.05%、氧化钾1.99%~3.47%、锰0.51%~1.98%、钴3.01%~3.28%、铜2.31%~2.77%、钼2.01%~7.20%、镉5.81%~7.76%、铅2.01%~3.65%、硒3.98~7.43%;均满足或优于《多目标区域地球化学调查规范（1：250000）》要求,该方法具有操作简单、多元素同时测定、方法检出限低、测定线性范围宽、准确度高、精密度好等优点,尤其是协同高效,大大节约水、电、试剂等特点,适合实验室广泛推广应用。     

石墨消解–火焰原子吸收光谱法测定土壤和沉积物中铜、锌、镍、铬

建立石墨消解–火焰原子吸收光谱法测定土壤和沉积物中铜、锌、镍、铬4种重金属的含量。采用盐酸–硝酸–氢氟酸–高氯酸作为消解体系对样品进行消解,铜、锌、镍以1%硝酸定容,铬以3%盐酸定容,采用火焰原子吸收光谱仪进行测定。铜、锌、镍、铬的质量浓度在0.00~1.00 mg/L范围内与吸光度均呈良好的线性关系,相关系数为0.999 4~0.999 5,方法检出限为0.7~1.5μg/g。测定结果的相对标准偏差为1.8%~3.4%(n=6),样品加标回收率为92.0%~105%。土壤和沉积物标准样品的测定值均在标准值可接受范围内。该方法操作简单、快速,结果准确、可靠,适用于土壤和沉积物样品中铜、锌、镍、铬等金属元素的测定。     

微波消解-电感耦合等离子体质谱法测定土壤中10种重金属元素

利用硝酸、盐酸、氢氟酸混合液和微波消解仪密闭消解样品，建立了一种微波消解-电感耦合等离子体质谱（ICP-MS）法同时测定土壤中铜、铅、锌、锰、钒、铬、镉、镍、锡、铊10种重金属的分析方法。取0.100 0 g土壤样品于消解罐中，采用4 mL硝酸+1 mL盐酸+1 mL氢氟酸消解体系按照设定程序进行微波消解，冷却，定容后利用电感耦合等离子体质谱法进行。结果表明，以铑元素作为内标，10种重金属元素在一定的质量浓度范围内与其信号强度呈线性关系，线性相关系数均不小于0.999 8，检出限为0.010～0.92 mg/kg。对3种标准物质进行测定，测定值的相对标准偏差为2.89%～7.72%(n=10)，相对偏差为-5.95%～4.11%。该方法分析流程简单，工作效率高，检出限低，适合大批量土壤样品的多元素同时分析。     

电感耦合等离子体原子发射光谱法测定植物中钾、钠、钙和镁

采用硝酸–高氯酸湿法消解或硝酸–双氧水微波消解植物样品,以电感耦合等离子体原子发射光谱法同时测定样品溶液中钾、钠、钙和镁含量。用该法测定灌木枝叶和茶叶标准样品,测定值均在标准值范围内,测定结果的相对标准偏差为0.45%~4.05%(n=8)。钾、钠、钙、镁的加标回收率分别为94.4%~107.6%,92.6%~107.9%,93.7%~105.4%,92.9%~107.2%。该方法操作简便,测量精密度和准确度完全满足植物中钾、钠、钙和镁含量的测定要求。     

An evaluation of analytical techniques for determination of lead, cadmium, chromium, and mercury in food-packaging materials

Closed microwave digestion and a high-pressure asher have been evaluated for wet-oxidation and extraction of lead, cadmium, chromium, and mercury from a range of typical packaging materials used for food products. For the high-pressure asher a combination of nitric and sulfuric acids was efficient for destruction of a range of packaging materials; for polystyrene, however, nitric acid alone was more efficient. For microwave digestion, a reagent containing nitric acid, sulfuric acid, and hydrogen peroxide was used for all materials except polystyrene. Use of the high-pressure asher resulted in the highest recoveries of spiked lead (median 92%), cadmium (median 92%), chromium (median 97%), and mercury (median 83%). All samples were spiked before digestion with 40 microg L(-1) Cd, Cr, and Pb and 8 microg L(-1) Hg in solution. The use of indium as internal standard improved the accuracy of results from both ICP-MS and ICP-AES. Average recovery of the four elements from spiked packaging materials was 92 +/- 14% by ICP-MS and 87 +/- 15% (except for mercury) by ICP-AES. For mercury analysis by CVAAS, use of tin(II) chloride as reducing agent resulted in considerably better accuracy than use of sodium borohydride reagent.     

土壤中铅的分析方法比对

对不同的样品消解方法及电感耦合等离子体质谱、电感耦合等离子体原子发射光谱、石墨炉原子吸收光谱法测定土壤中铅的测定结果进行比对。采用电热板、微波及水浴3种加热方式,选择硝酸、氢氟酸、双氧水、王水、高氯酸、盐酸的不同组合进行土壤样品消解,通过分析测定值的精密度和准确度,考察消解体系对电感耦合等离子体质谱、电感耦合等离子体发射光谱、石墨炉原子吸收光谱法测定结果的影响。结果表明采用电感耦合等离子体质谱法测定土壤中的铅,最适宜的消解体系是硝酸-氢氟酸-高氯酸(微波加热),采用电感耦合等离子体原子发射光谱法测定最适宜的消解体系是硝酸(电热板加热),采用石墨炉原子吸收光谱法测定最适宜的消解体系是硝酸-盐酸-高氯酸(微波加热)。电感耦合等离子体质谱法的精密度和准确度优于另外两种方法。     

重量法-电感耦合等离子体原子发射光谱法联用测定无取向硅钢磷酸盐体系环保涂层液中二氧化硅含量

二氧化硅是无取向硅钢环保涂层液的核心成分,其含量直接影响硅钢涂层的固化工艺及涂层产品的磁性能。因此为保证涂覆过程的顺利进行,对涂层液中二氧化硅含量的检测是十分必要的。本方法采用样品中分别加入硝酸、双氧水及高氯酸,置于电热板上进行消解处理,处理后的样品经酸溶、过滤步骤,以重量法计算沉淀中二氧化硅的含量,采用电感耦合等离子体原子发射光谱（ICP-AES）仪测定滤液中可溶性硅含量,则样品中二氧化硅含量为重量法和电感耦合等离子体原子发射光谱法测定结果的合量。从而建立了重量法-电感耦合等离子体原子发射光谱法联用测定无取向硅钢磷酸盐体系环保涂层液中二氧化硅含量的方法。讨论了样品前处理用消解酸及消解温度、滤液中可溶性硅及含量、ICP-AES仪器检测时的元素干扰。结果表明：按照本实验方法测定无取向硅钢磷酸盐体系环保涂层液中二氧化硅含量,检测结果的相对标准偏差（RSD,n=12）在0.76%~1.08%之间,加标回收率在97.00%~104.0%之间。该方法可广泛应用于各检测部门对无取向硅钢磷酸盐体系环保涂层液中二氧化硅含量的监控。     

微波消解电感耦合等离子体发射光谱法测定塑料中铅和镉

采用微波消解技术溶样，ICP-AES法测定了塑料中的铅和镉。通过对消解试剂和微波温度程序的研究，建立了塑料样品的微波消解方法。该方法与传统马弗炉高温灰化消解方法比较，具有准确、简便、快速、省试剂、污染少、消解完全等优点。方法回收率为93％～106％，相对标准偏差(n=7)均小于2％。实际样品对比分析结果表明，方法具有良好的准确度，适于多种塑料材料中铅和镉的快速分析。     

Determination of metal concentrations in lichen samples by inductively coupled plasma atomic emission spectroscopy technique after applying different digestion procedures

Three digestion procedures have been tested on lichen samples for application in the determination of major, minor and trace elements (Al, Ca, Cd, Cr, Cu, Fe, K, Mg, Mn, Na, Ni, Pb, V and Zn) in lichen samples collected in Aegean Region of Turkey by inductively coupled plasma atomic emission spectrometer (ICP-AES). The acid mixture of concentrated HNO₃, H₂O₂ and HF were used. The instrument was optimized using lichen matrix considering RF power, nebulizer pressure, auxiliary flow rate and pump rate. The accuracy of the overall analyses was first estimated by analysis of two certified reference materials. Good agreement between measured and reference values were found for almost all elements. As the second way of determining the accuracy, results obtained from independent analytical techniques (ICP-AES and instrumental neutron activation analysis (INAA)) were compared for all elements by analyzing real samples. Correlation coefficients of two techniques for the elements ranged between 0.70 (Mg) and 0.96 (Fe). Among the three digestion systems, namely microwave, open vessel and acid bomb, microwave digestion system gave the best recovery results. The method detection limit (MDL) was computed using reagent blanks of microwave digestion system since it provides cleaner sample preparation. Detection limit is adequate for all elements to determine the elements in lichen samples. The precision was assessed from the replicate analyses of reagent blanks of microwave digestion system and was found to be less than 1.5% relative standard deviation (R.S.D.).     

湿式消化-ICP-AES法测定航空润滑油中镍钛镁铬钼锡

研究采用硝酸-高氯酸混合酸湿式消化法,建立ICP-AES法同时测定航空润滑油中痕量金属元素镍、钛、镁、铬、钼、锡。样品消化完全、快速,检出限分别为(μg．L^-1)：镍4．1、钛2．1、镁4．2、铬3．2、钼3．6、锡24．4,RSD小于5％,回收率为96．0％～104．0％。     

Microwave heated vapor-phase digestion method for biological sample materials

A microwave heated, vapor-phase nitric acid-hydrogen peroxide digestion method for pulverized, biological sample materials was developed. Sample masses up to 200 mg were digested using calibrated quartz inserts inside first generation type, low-pressure, Teflon-PFA microwave vessels. In the first step, samples were digested in the vapor-phase for 80 min using a progressive heating pattern. Three mL of 70% nitric acid and 0.5 mL of 30% hydrogen peroxide were used as digestion reagents. In the second step, the small residue left after first step digestion was dissolved in 1.4% nitric acid or additionally with 0.5% hydrofluoric acid by heating for 15 min. The digestion method was optimized using pike (Esox lucius) muscle as a test material. The method was further optimized using three certified reference materials. Ca, Cu, Fe, Mg and ¶Zn were determined from NIST-SRM 1577a bovine liver by ICP-AES. Cr and Ni were determined from NIST-SRM 8433 corn bran and NRCC DOLT-2 dogfish liver by GFAAS. For all elements the values obtained were close or within certified limits. Spike recoveries were between 96 to 107%. Digestion efficiency ranged from 91 to 99%.     

Microwave heated vapor-phase digestion method for biological sample materials

A microwave heated, vapor-phase nitric acid-hydrogen peroxide digestion method for pulverized, biological sample materials was developed. Sample masses up to 200 mg were digested using calibrated quartz inserts inside first generation type, low-pressure, Teflon-PFA microwave vessels. In the first step, samples were digested in the vapor-phase for 80 min using a progressive heating pattern. Three mL of 70% nitric acid and 0.5 mL of 30% hydrogen peroxide were used as digestion reagents. In the second step, the small residue left after first step digestion was dissolved in 1.4% nitric acid or additionally with 0.5% hydrofluoric acid by heating for 15 min. The digestion method was optimized using pike (Esox lucius) muscle as a test material. The method was further optimized using three certified reference materials. Ca, Cu, Fe, Mg and Zn were determined from NIST-SRM 1577a bovine liver by ICP-AES. Cr and Ni were determined from NIST-SRM 8433 corn bran and NRCC DOLT-2 dogfish liver by GFAAS. For all elements the values obtained were close or within certified limits. Spike recoveries were between 96 to 107%. Digestion efficiency ranged from 91 to 99%.