电感耦合等离子体原子发射光谱法测定镍基单晶高温合金中Mo、W、Ta、Re、Ru时元素之间相互干扰的消除与校正的研究

称取镍基单晶高温合金0.100 0g于聚四氟乙烯烧杯中,先令其与盐酸9mL和硝酸1mL加热反应,待反应缓慢时滴加氢氟酸2mL并继续加热使样品完全溶解。加入500g·L^-1酒石酸溶液2mL,冷却至室温,在塑料容量瓶中加水定容至100.0mL。按仪器工作条件采用电感耦合等离子体原子发射光谱法测定其中5种合金元素(Mo、W、Ta、Re、Ru)的含量,选择分析谱线依次为204.598,207.911,240.063,197.312,240.272nm。结果发现:除了Re外,其余4种元素的测定中均受共存元素的光谱干扰,严重影响了测定结果的准确性。为克服其干扰,除了采用基体匹配法消除镍的基体干扰外,试验采用混合校正系数矩阵法对测定结果进行校准。通过一系列试验计算得到混合校准系数矩阵K,并应用于模拟样品的分析。结果表明:经过矩阵K的校准,所测定的5种元素的准确度显著提高,达到了消除共存元素之间光谱干扰的目的。通过精密度试验,测得上述5种元素测定值的相对标准偏差(n=11)均在1.5%以下,并通过标准加入法进行回收试验,测得5种元素的回收率为97.0%~105%。     

Chemical analysis of uranium and titanium niobotantalate metamict minerals by ion-exchange chromatography and spectrophotometric procedures

An ion-exchange separation followed by spectrophotometric determinations is applied to some metamict minerals. These minerals, containing very high amounts of elements which present some problems to the analyst, such as uranium, titanium, niobium and rare-earth elements, are fused with potassium bisulphate, and the cooled melts dissolved in sulphuric acid. The solutions are passed through a series of three ion-exchange columns to separate those mineral-forming elements for which the colorimetric procedures suffer interference from the elements listed above. The procedure has been tested with a synthetic solution and with solutions of the minerals.     

微波消解-电感耦合等离子体原子发射光谱法测定催干剂中金属元素含量

应用电感耦合等离子体原子发射光谱法(ICP-AES)测定了不同种类催干剂中9种金属元素,即钴、锰、铅、钙、锌、钒、锆、镧和铈。样品置于聚四氟乙烯溶样罐中加入浓硝酸及高氯酸,盖紧罐盖后按预设程序分两步进行微波加热,加压消解,所得溶液稀释至一定体积供ICP-AES分析。对上述元素的谱线中选择合适的谱线作分析线,达到了9元素的同时测定。同混合标准溶液制备各元素的工作曲线,其线性范围均在100.0 mg·L~(-1)以内。以一催干剂样品为基体,用标准加入法作回收试验,测得回收率在93.8%～109.9%之间,测定值的相对标准偏差(n=6)在0.11%～1.56%之间。不同来源的5个催干剂样品的分析结果表明所测得的金属元素的类别和含量显著差异。试验还证实所提出的方法具有操作快速、简单、方便,适合应用于日常分析工作。     

Spectrophotometric determination of tantalum in ores and mill products with brilliant green after separation by methyl isobutyl ketone extraction of tantalum fluoride

A method for determining ~ 0.001% or more of tantalum in ores and mill products is described. After fusion of the sample with sodium carbonate, the cooled melt is dissolved in dilute sulphuric-hydrofluoric acid mixture and tantalum is separated from niobium and other matrix elements by methyl isobutyl ketone extraction of its fluoride from 1M hydrofluoric acid-0.5M sulphuric acid. The extract is washed with a hydrofluoric-sulphuric acid solution of the same composition to remove co-extracted niobium, and tantalum is stripped with dilute hydrogen peroxide. This solution is acidified with sulphuric and hydrofluoric acids and evaporated to dryness, and the residue is dissolved in oxalic-hydrofluoric acid solution. Tantalum is ultimately determined spectrophotometrically after extraction of the blue hexafluorotantalate-Brilliant Green ion-association complex into benzene from a 0.05M sulphuric acid-0.5M hydrofluoric acid-0.2M oxalic acid medium. The apparent molar absorptivity of the complex is 1.19 x 10(4) l.mole(-1).mm(-1) at 640 nm, the wavelength of maximum absorption. Common ions, including iron, aluminium, manganese, zirconium, titanium, molybdenum, tungsten, vanadium, tin, arsenic and antimony, do not interfere. Results obtained by this method are compared with those obtained by an X-ray fluorescence method.     

A scheme for the analysis of monazite and monazite concentrates

A scheme using ion-exchange methods is described for the analysis of monazites and monazite concentrates. The sample is opened up with concentrated sulphuric acid, and the resultant solution is applied to a column of Zeocarb 225 resin. After phosphate has been washed out, lead, aluminium, titanium, iron, uranium, calcium and magnesium are eluted with N hydrochloric acid and determined by specific, mainly spectrophotometric, methods. Rare earth elements are eluted with 3 N hydrochloric acid. Cerium is separated from the other rare earths by solvent extraction of its nitrate with methyl iso-butyl ketone; both groups are determined gravimetrically. Thorium is eluted from the ion-exchange resin with 3.6 N sulphuric acid and determined spectrophotometrically with thorin.The sulphuric acid-insoluble minerals are brought into solution by a double fusion method, and the determinations are carried out by a combination of ion-exchange and photometric procedures. Silica, phosphorus pentoxide, tin and chromium are determined by photometric methods, using separate portions of the sample.Lanthanum, yttrium and ytterbium are determined in a 1 M perchloric acid solution of the mixed rare earth oxides (less cerium) using flame photometry. Samarium, praseodymium and neodymium are determined by spectrophotometry.     

Determination of total tin in river water by hydride generation-atomic absorption spectrometry

Summary The total tin in river water was determined by hydride generation-atomic absorption spectrometry in sulphuric acid medium. The water was concentrated with nitric and sulphuric acids. Interference from copper and iron was eliminated by extracting copper with a carbon tetrachloride solution of zinc dibenzyldithiocarbamate and by complexing iron with 1,10-phenanthroline in solution. The acidities of the sample solutions were checked by weighing the residue in the flasks during the acid digestion so that the acidities of the sample solutions became approximately equal to those of the calibration solutions. When a 1,000 mg/l tin(IV) solution was diluted with water, the hydrolysed tin could not be determined entirely as the total tin by acidification with sulphuric acid, but it could be recovered completely by digestion even after 5 days. Thus digestion is essential when determining the total tin in water.     

Determination of cobalt,molybdenum and vanadium in austrian mineral waters by ICP-AES after ion-exchange separation and preconcentration

A method is described for the determination of cobalt, molybdenum and vanadium in mineral water samples by inductively coupled plasma-atomic emission spectroscopy (ICP-AES) after separation of these elements from the matrix by ion exchange. The samples are acidified with concentrated hydrochloric acid (10 ml/l) and the elements are adsorbed as thiocyanate complexes. Elution is performed with a mixture 2M in perchloric acid and 1M in hydrochloric acid and subsequently with 1M hydrochloric acid. After evaporation of the eluates and dissolution of the residue the volume of the measuring solution for ICP-AES is 10 ml. The recoveries for Co, Mo and V at a concentration level of 1 g/1 in mineral waters were approximately 99%. A concentration factor of 100 is achieved by this procedure.     

Determination of silver, bismuth, cadmium, copper, iron, nickel and zinc in lead- and tin-base solders and white-metal bearing alloys by atomic-absorption spectrophotometry

A simple atomic-absorption spectrophotometry method is described for the determination of silver, bismuth, cadmium, copper, iron, nickel and zinc in lead- and tin-base solders and white-metal bearing alloys, with use of a single sample solution. The sample is dissolved in a mixture of hydrobromic acid and bromine, then fumed with sulphuric acid. The lead sulphate is dissolved in concentrated hydrochloric acid. The method is particularly suitable for the determination of silver and bismuth, which are co-precipitated with lead sulphate. The other elements can also be determined after removal of the lead sulphate by filtration.     

A simple method for dissolution of tantalum pentoxide

A simple and reproducible procedure has been developed for the dissolution of tantalum pentoxide. The oxide is fused with potassium nitrate and potassium carbonate in the ratio of 2:5:5. The cooled melt is dissolved in concentrated sulphuric acid. If a tartaric acid solution is desired the sulphuric acid is evaporated and the residue dissolved in 20% tartaric acid solution.     

The equilibria between TLA in toluene and mixtures of HCl−H2SO4

The extraction of hydrochloric and sulphuric acid from their mixture by tri-n-dodecyl amine in toluene was studied. The equilibria were investigated at high acid concentrations, so that only amine bisulphate and chloride were formed in the organic solution. They were characterized by the stability constant ratios of the above salts.     

电感耦合等离子体原子发射光谱法(ICP-OES)测定地下水中多种元素

应用电感耦合等离子体原子发射光谱法(ICP-OES)测定地下水中钾、钠、钙、镁、铁、锰元素的含量,使用分光光度法测定氟的含量,测定的相对标准偏差为0.7%~2.8%,加标回收率为92.1%~105.2%。结果表明,大部分地区地下水中钠和氟化物的含量均偏高,常量与微量元素的组成含量差别不大。     

Volatilization of methyl borate in iron matrix. Determination of boron in steel by ICP atomic emission spectrometry

A rapid and reliable method for the determination of boron by ICP-AES in steels is described. The procedure is based on a discontinuous generation of methyl borate, in concentrated sulphuric acid and phosphoric acid medium, after injecting 45 microl of methanol in 20 microl of sample. The gaseous methyl borate and excess methanol are fed into the ICP torch via the intermediate tube by a flow of 430 ml/min Ar carrier gas, without disturbing the discharge. This work simplifies drastically the existing methodology of boron analysis in steels. Acid-soluble boron has been determined, but acid-insoluble boron can also be determined. The determination is carried out without iron interferences, with a reproducibility of 1.90% r.s.d. for a concentration of 20 microg/ml, and an absolute detection limit of 20 ng of total boron, working with a solution volume of 20 microl.     

Determination of silver, antimony, bismuth, copper, cadmium and indium in ores, concentrates and related materials by atomic-absorption spectrophotometry after methyl isobutyl ketone extraction as iodides

Methods for determining ~ 0.2 mug g or more of silver and cadmium, ~ 0.5 mug g or more of copper and ~ 5 mug g or more of antimony, bismuth and indium in ores, concentrates and related materials are described. After sample decomposition and recovery of antimony and bismuth retained by lead and calcium sulphates, by co-precipitation with hydrous ferric oxide at pH 6.20 +/- 0.05, iron(III) is reduced to iron(II) with ascorbic acid, and antimony, bismuth, copper, cadmium and indium are separated from the remaining matrix elements by a single methyl isobutyl ketone extraction of their iodides from ~2M sulphuric acid-0.1M potassium iodide. The extract is washed with a sulphuric acid-potassium iodide solution of the same composition to remove residual iron and co-extracted zinc, and the extracted elements are stripped from the extract with 20% v v nitric acid-20% v v hydrogen peroxide. Alternatively, after the removal of lead sulphate by filtration, silver, copper, cadmium and indium can be extracted under the same conditions and stripped with 40% v v nitric acid-25% v v hydrochloric acid. The strip solutions are treated with sulphuric and perchloric acids and ultimately evaporated to dry ness. The individual elements are determined in a 24% v v hydrochloric acid medium containing 1000 mug of potassium per ml by atomic-absorption spectrophotometry with an air-acetylene flame. Tin, arsenic and molybdenum are not co-extracted under the conditions above. Results obtained for silver, antimony, bismuth and indium in some Canadian certified reference materials by these methods are compared with those obtained earlier by previously published methods.     

The determination of alumina in silicates (Rocks and Refractories)

New procedures have been developed for determining the alumina contents of silicate material (rocks and refractories). The material is first taken into solution by a peroxide sinter technique, followed by dissolving the sinter in warm water and the addition of sufficient hydrochloric acid to render the solution acid to litmus. A different technique is used for silicates containing less than 5% alumina. The majority of the silica is first removed by treating with hydrofluoric-sulphuric acids and the residue is fused with potassium bisulphate. Extractions with cupferron are next employed to remove iron, titanium, zirconium etc., and the aluminium is subsequently separated from other sample constituents by precipitating as its insoluble benzoate. After filtration the aluminium benzoate is dissolved in hydrochloric acid and the aluminium concentration determined volumetrically with ethylenediaminetetraacetic acid.     

气相色谱法测定烟气中拟除虫菊酯杀虫剂在卷烟滤嘴中的残留量

用符合ISO 30008标准要求的吸烟机按标准条件抽吸卷烟样品,抽吸完毕后,取下滤嘴,用乙酸乙酯-环己烷(1+1)混合溶剂超声提取30min。将提取液经无水硫酸钠干燥后旋转蒸至近干,残渣溶于正己烷2mL中,所得溶液经石墨炭黑小柱进行净化。小柱用丙酮-正己烷(2+8)混合溶剂淋洗2次,收集洗脱液,旋转蒸发浓缩后,将溶液用上述混合溶剂定容至1.5mL,供气相色谱分析,采用Agilent HP-5色谱柱进行分离和电子捕集检测。测定了4种拟除虫菊酯,相对标准偏差(n=5)均小于6%,于20个滤嘴样品中加入相当于20μg的4种拟除虫菊酯混合标准溶液,回收率均大于92%。     

Comparative instrumental multi-element analysis I: Comparison of ICP source mass spectrometry with ICP atomic emission spectrometry, ICP atomic fluorescence spectrometry and atomic absorption spectrometry for the analysis of natural waters from a granite region

Summary Multi-element analysis by ICP source mass spectrometry for practically matrix-free natural waters, coming from a granitic area and, therefore, rich in trace elements, has been compared with ICP-atomic emission, ICP atomic fluorescence and atomic absorption spectrometry. The following elements have been investigated and their concentrations are in the decreasing order: Ca, Si, Na, Mg, K, Al; Sr, Mn, Ba, Fe, Rb, Zn, B, U, Y, Li, La, Be, Cs, Co, Cr, V, Sb, Bi, Th, Cu, Cd, Ni, Se, Pb, As, Hg, Mo, Tl, Sn. The concentration ranges were between 10 ppm and <0.01 ppb.As a measure of agreement between the different methods under investigation, two criteria have been used (a) the relative variation coefficient VK (%) of the mean element concentration of an element, determined by different methods in all the 98 water samples and (b) the linear, logarithmic and Spearman rank correlation coefficients between ICP-MS and each of the other methods. Detection limits are given from literature for about 32 elements using different methods.The elements Ca, Na, Mg, K, Mn, Sr, Zn, Fe, Li, Cu have been determined with ICP-MS, ICP-AES and AAS; Al, Ba with ICP-MS and ICP-AES; Si only with ICP-AES, whereas B, Be, Bi, Co, Cr, Cs, Hg, La, Mo, Ni, Pb, Rb, Sb, Sn, Th, Tl, U, V, Y only with ICP-MS. In all 34 of the investigated 36 elements could be analysed by ICP-MS, 14 (from about 20 possible) by AAS, 13 by ICP-AES and 12 by ICP-AFS.The agreement between ICP-MS and ICP-AES as well as between ICP-MS and AAS in most cases is remarkably good according to (a). VK (%) for each element in 98 water samples is in the range from ±2.6 to 10% for Na, Mg, Ca, K, Fe, Sr, Ba, Cu, Li (increasing order). Cd and Zn have unexpectedly higher values (±17.3 and ±20.5%); Cd concentrations are, however, near the detection limit.Comparing the different methods on the basis of correlation coefficients according to (b), gives for the Spearman rank correlation coefficient over the whole range of concentrations, respectively for ICP-MS/ICP-AES, AAS, ICP-AFS in case of Ca: 0.998; 0.984; 0.899; Na: 0.993; 0.991; 0.978; Mg: 0.997; 0.993; 0.959; K: 0.986; 0.942; 0.677; Al: 0.987; -; -; Fe: 0.864; 0.974; 0.701; Mn: 0.989; 0.990; 0.198; Sr: 0.988; 0.992; -; Zn: 0.894; 0.819; 0.300; Cu: -; 0.977; 0.202; Li: -; 0.907; 0.586.It is evident from these trace element concentrations as well as the electrical conductivities, that only about three fourths of the investigated samples are typical granitic waters and the remaining ones are associated with different geological background. The samples have been mainly radon waters with more than 18 nCi/l of Rn-222.

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Vergleichende Instrumentelle Multielementanalyse I: Vergleich von ICP-Massenspektrometrie mit ICP-Atomemissionsspektrometrie, ICP-Atomfluorescenzspektrometrie und Atomabsorptionsspektrometrie zur Analyse natürlicher Wässer aus einem Granitgebiet

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6th Contribution to the principles of trace analysis of elements and radionuclides

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Dedicated to Professor Dr. H. Kelker, Frankfurt, on the occasion of his 65th birthday     

电感耦合等离子体原子发射光谱法测定五氧化二钒中19种杂质元素

采用盐酸消解五氧化二钒样品及其中所含可溶性杂质,再以无水碳酸钾与硼酸高温熔融不可溶性杂质,然后以盐酸溶解熔块,合并溶液后以用电感耦合等离子体原子发射光谱法测定杂质元素铌、锆、钛、钨、硅、铝、钼、钴、铬、镍、铜、铅、镉、砷、磷、铁、锰、钙和镁的含量。试验了基体元素和共存元素对测定的干扰,优化各元素的分析谱线,运用同步背景校正消除基体影响。19种元素的检出限在10～225μg.L-1之间,背景等效浓度在5～150μg.L-1之间。方法用于分析五氧化二钒样品,测定结果与其它化学分析方法测定值一致;分析五氧化二钒标准样品(GSBH 42015-96)的测定值与标准值相一致。     

Determination of metals in small samples by atomic absorption and emission spectrometry with discrete nebulization

Eight elements in NBS-SRM 1577 bovine liver and other biological standards are determined by flame atomic absorption (Ca, Cu, Fe, Mg, Mn and Zn) and emission (K and Na) spectrometry. Samples (2 mg) weighed into a 3.8-ml teflon vessel are decomposed with 40 μl of (5 ÷ 1) nitric—perchloric acids in a sealed teflon vessel. A 75-μl or 100-μl aliquot of the diluted sample solution is injected into a small teflon funnel coupled directly to the nebulizer needle of the spectrometer. The results obtained agree well with certified values: the standard deviation is about 2%.     

电感耦合等离子体原子发射光谱法测定磷铁中磷、锰、钛和铝

提出了用硝酸-氢氟酸溶解磷铁样品后经高氯酸冒烟除氟,在硝酸(1+99)溶液中,采用电感耦合等离子体原子发射光谱法测定其中的磷、锰、钛和铝等成分。选择波长为213.618,257.610,334.941,308.215nm的4条谱线依次作为磷、锰、钛和铝测定的分析线。应用此方法分析了4个磷铁样品,其中包括一个国家标准物质GBW 01429,测得结果与化学法的测定结果或与认定值相符。磷、锰、钛和铝测定值的相对标准偏差(n=6)分别为0.49%,0.43%,0.83%,9.0%。     

Rapid estimation of metallization in reduced iron oxide ores

A simple and accurate method is described for the determination of degree of metallization in reduced iron oxide ores. Both metallic iron and total iron are determined in a single sample. The metallic iron is selectively dissolved in copper sulphate solution and the oxides are filtered off. The filtrate is titrated with potassium dichromate solution. The residue is dissolved in dilute sulphuric acid in presence of excess of copper powder and after filtration is titrated with the same dichromate solution. The first value gives the metallic iron content and the second value gives the iron content of the oxide residue. From these two values, the degree of metallization is computed.