氢化物发生-冷原子吸收光谱法测定化妆品中汞

介绍用氢化物发生-冷原子吸收光谱法在重铬酸钾-硝酸溶液存在下测定化妆品中汞的含量。方法空白值低、灵敏、准确、精密度好，特别适合于化妆品中汞的测定。     

氢化物发生-原子吸收光谱法测定大米中微量砷

砷是一种毒性很大的元素，对人的心肺、呼吸、神经、生殖、造血、免疫系统都有不同程度的损伤作用]。由于大气、地下水、土壤、肥料和农药等污染，砷会在粮食的可食部分积累，因此砷的测定已成为食品和环境监测的必测项目。测砷的常规方法有砷斑法、银盐法。目前，氢化物原子吸收光谱法，氢化物原子荧光法已有报道。本文采用氢化物发生—原子吸收光谱法测定大米中砷，本法具有灵敏度高，干扰少，操作简便等特点，结果满意。     

氢化物发生-原子吸收光谱法测定萤石粉中砷

提出了以氢化物发生-原子吸收光谱法测定萤石粉中砷的方法,研究了酸介质、还原剂、载气流量等因素对测定的影响,并选择出最佳工作条件.砷的检出限为0.052μg·g-1,线性范围为0.10～6.00 μg·L-1,回收率在90.0%～102.0%之间,相对标准偏差为9.8%.     

流动注射氢化物发生-原子吸收光谱法测定中药中的微量砷

探讨了流动注射氧化物发生-原子吸收光谱法测定微量砷的最佳条件,建立了中药中微量砷的流动注射氧化物发生-原子吸收光谱分析方法。砷的检出限为0.59μg/L,线性范围为0～30μg/L,线性回归方程为A=0.02228c 6.282×10~(-3),相关系数r=0.9992,相对标准偏差为2.6％～4.4％,回收率为91％～103％。方法操作简便、快速,灵敏度及自动化程度高。     

流动注射氢化物-原子吸收光谱法测定人发中砷

砷是一种对人体有害的元素,砷的测定方法报道较多。对发砷的测定,本文在文献[1,2]的基础上采用流动注射氢化物 原子吸收光谱法,方法操作简便快捷,提高了灵敏度和准确度,是一种较好的测定生物样品中砷的分析技术。1　试验部分1.1　仪器与试剂WFX 1D型原子吸收分光光度计(北京第二光学仪器厂)高性能砷空心阴极灯,WHG 102A型流动注射氢化物发生器,电热式T型石英管原子化器(北京翰时制作所)。砷标准储备液:1.00mg·ml-1,称取As2O3(于110℃烘干2h)0.1320g,加200g·L-1NaOH溶液2.0ml,加水50ml溶解后,加盐酸10ml,定容至100ml。使用时稀释…     

流动注射-氢化物发生-原子吸收光谱法测定中草药中砷

中草药样品经硝酸-高氯酸-硫酸消化处理后,在酸性条件下用硫脲和抗坏血酸将砷(Ⅴ)还原为砷(Ⅲ),然后再以硼氢化钾为还原剂,稀盐酸为载液,用流动注射氢化物发生原子吸收光谱法测定砷含量.砷的质量浓度在1.6～32.0 μg·L-1范围内与其吸光度呈线性关系,检出限(3s/k)为0.32 μg·L-1.用此方法分析了3种草药样品,砷的测定值的相对标准偏差(n=6)在5.1%～8.1%之间,加标回收率在91.4%～106.1%之间.     

流动注射氢化物发生原子吸收光谱法测定酱油中砷

采用紫外消化技术处理样品 ,流动注射氢化物发生原子吸收光谱法测定酱油中砷。方法的检出限为 0 .14ng·ml- 1,线性范围为 0 .80～ 2 4 .0ng·ml- 1,相对标准偏差为 3.5 %～ 8.4 % ,样品加标回收率为 96 .9%～ 10 6 .5 %。方法的灵敏度高 ,选择性好 ,试剂及样品用量少 ,操作方便 ,分析快速 ,每小时可分析 6 0个样品 ,适于推广应用     

HG-FAAS法测定雄黄染毒小鼠肝及肾脏中的砷含量

建立了氢化物发生-火焰原子吸收法(HG-FAAS)测定雄黄染毒小鼠肝及肾脏中砷含量的方法 .结果表明,该方法准确、灵敏、可靠、检出限低.雄黄染毒小鼠肝、肾脏中砷的分布水平相当.同时对氢化物发生条件进行了优化.     

氢化物发生-原子吸收光谱法测定食盐中微量铅

食盐中铅测定采用萃取-原子吸收光谱法，方法使用有机试剂，操作也复杂。采用石墨炉原子吸收光谱法直接测定，氯化钠干扰很大。本文提出氢化物发生-原子吸收光谱法测定食盐中铅。采用WHG-102A2型流动注射氢化物发生器与原子吸收光谱仪配合，载气压力作为自动化能源，流动注射方     

氢化物发生–原子吸收光谱法测定铅粉中痕量砷、锑

建立氢化物发生–原子吸收光谱法联用测定铅粉中痕量砷、锑的方法。试样用稀硝酸溶解,用5%抗坏血酸溶液作为砷(Ⅴ)、锑(Ⅴ)的预还原剂,5%的硫脲溶液作为其它元素的掩蔽剂,选用1%硼氢化钠溶液作为还原剂,氢化物反应在10%盐酸介质中进行。在优化的试验条件下,砷、锑的质量浓度在0~20 ng/m L范围内与吸光度线性相关,相关系数r2分别为砷0.999 6,锑0.993 8,方法的检出限分别为砷0.40 ng/m L,锑0.75 ng/m L。砷、锑测定结果的相对标准偏差分别为4.96%,6.27%(n=6),铅粉样品加标回收率分别为砷87.6%,锑79.3%。该方法准确可靠,可用于测定铅粉中痕量砷、锑。     

Determination of trace arsenic in hydrofluoric acid by hydride generation and atomic absorption spectrometry

Practical procedures are given for determination of arsenic(III) and (V) in hydrofluoric acid by means of hydride generation and atomic absorption spectrometry. Arsenic(III) can be determined by direct generation of arsine with sodium borohydride in hydrochloric/hydrofluoric acid medium, arsenic(V) being only slightly reduced under the conditions used. For its determination, arsenic(V) has to be prereduced with potassium iodide, and even then its reduction to arsenic(III) and then arsine is far from complete. It is possible to determine it in presence of arsenic(III) by a difference method, but this is recommended only if the As(V)/As(III) ratio is greater than 1. Total arsenic can be determined after oxidation of As(III) and evaporation of most of the hydrofluoric acid. The limit of determination is 5 g/l for arsenic(III) and 0.25 g/l for total arsenic; the relative standard deviation is about 10%.     

氢化物-原子吸收光谱法测定冶金企业废水中的砷

采用HNO3/HClO4(体积比10∶1)消解冶金废水样品,经6mol.L-1 HCl溶液酸化后,加入碘化钾(3%)、抗坏血酸(1%)及硫脲(1%)混合溶液进行还原,用氢化物-原子吸收光谱法(HG-AAS)测定了样品中的As含量.结果表明,该方法的检出限为0.297μg/L,相对标准偏差RSD为5.463%,样品加标回收率为93%～108%;其操作方便、选择性好、灵敏度高、干扰少,适合于复杂废水中微量和痕量As的测定.     

Improvement in arsenic speciation,using hydride generation and atomic absorption spectrophotometry

Improvements in arsenic speciation in sea-water using hydride generation, cold trapping and AAS are reported. Progressive addition of sodium tetrahydroborate and pH optimization are essential to obtain reliable results. The response factor for As^III, As^v, methylarsonic acid and dimethylarsinic acid is nearly the same when sulphuric acid is used for the hydride generation step.     

Determination of toxic and non-toxic arsenic species in urine by microwave assisted mineralization and hydride generation atomic absorption spectrometry

Flow injection — microwave oven — hydride generation — atomic absorption spectroscopy (FI-MO-HG-AAS) has been optimized for the determination of the total and toxic arsenic in urine with and without persulfate, respectively. With microwave oven assisted digestion of urine with 5% (w/v) K₂S₂O₈ and 5% (w/v) NaOH all arsenicals completely can be converted to arsenate, which is determined by HG-AAS to give the total concentration of the six species present in urine. The detection limits of 4–6 g l^–1, the relative standard deviation of 3–7% and the high sample throughput make the methods suitable for rapid routine on-line determination. Application of the proposed procedures to the analysis of urine from people on a diet rich in seafood revealed a significant increase in total urinary arsenic due to the rapid excretion of organoarsenicals. Efficient decomposition and quantitative recovery of all arsenic species in spiked urine is achieved by using 5% K₂S₂O₈ in 5% NaOH at 4.6 ml min^–1, microwave power of 700 W and a 1.5 m coil.     

Indirect determination of arsenic by flotation spectrophotometry

An indirect method of arsenic determination in the submicrogram range via the determination of molybdenum is presented here. High sensitivity is achieved by combination of the chemical amplification during formation of dodecamolybdoarsenic acid (arsenic: molybdenum ratio 1 12) with multiplication due to the formation of ion-association complexes during flotation-spectrophotometric molybdenum determination with crystal violet (molar ratio 1 2). Thus, the amplification factor relating to arsenic is 24.Dodecamolybdoarsenic acid is formed in a weakly acidic medium and is quantitatively extracted byn-butanol. Back extraction of the heteropoly acid to the aqueous phase and its simultaneous destruction provides the basis for the reaction of released molybdate ions with thiocyanate ions. The molybdenum-thiocyanate complex forms a sparingly soluble ion-association complex with crystal violet which can be floated with toluene on the phase boundary (film flotation). After separation of the aqueous phase the floated molybdenum compound is dissolved in acetone and the resulting free crystal violet ions are subjected to photometric determination at 590 nm as equivalent of the concentration of arsenic. The molar absorptivity of crystal violet is 3.2 · 10⁵1 · mol^–1 · cm^–1. Beer's law is obeyed in a concentration range from 0.01 to 1 g Mo · ml^–1 (0.001–0.1 g As · ml^–1). The resulting detection limit for arsenic is 1 ng · ml^–1.     

Speciation of inorganic arsenic by electrochemical hydride generation atomic absorption spectrometry

A simple procedure was developed for the speciation of inorganic arsenic by electrochemical hydride generation atomic absorption spectrometry (EcHG–AAS), without pre-reduction of As(V). Glassy carbon was selected as cathode material in the flow cell. An optimum catholyte concentration for simultaneous generation of arsine from As(III) and As(V) was 0.06 mol l⁻¹ H₂SO₄. Under the optimized conditions, adequate sensitivity and difference in ratio of slopes of the calibration curves for As(III) and As(V) can be achieved at the electrolytic currents of 0.6 and 1 A. The speciation of inorganic arsenic can be performed by controlling the electrolytic currents, and the concentration of As(III) and As(V) in the sample can be calculated according to the equations of absorbance additivity obtained at two selected electrolytic currents. The calibration curves were linear up to 50 ng ml⁻¹ for both As(III) and As(V) at 0.6 and 1 A. The detection limits of the method were 0.2 and 0.5 ng ml⁻¹ for As(III) and As(V) at 0.6 A, respectively. The relative standard deviations were of 2.1% for 20 ng ml⁻¹ As(III) and 2.5% for 20 ng ml⁻¹ As(V). The method was validated by the analysis of human hair certified reference material and successfully applied to speciation of soluble inorganic arsenic in Chinese medicine.     

Determination of arsenic in fly ash by hydride generation in a slurry

We have studied the generation of arsenic hydride on a fly ash slurry from a thermal power plant burning lignite. The conditions for the formation of the slurry were optimized and the influence of the presence of various surfactants on the formation and stability of slurry (particle size-analytical signal ratio) were investigated.The As content in the ash was 78.7 g/g, with an rsd of 5.6% and a detection limit of 2.8 ng. The proposed method was successfully applied to the determination of arsenic in a certified ash sample (BCR-38). This method was applied to fly ash from a thermal power plant burning anthracite.     

氢化物发生原子荧光光谱法测定磷酸中的砷

采用HCl处理H3PO4试样，氢化物发生原于荧光光谱法测定As，对仪器条件、HCl酸度、预还原剂用量、还原剂用量、共存干扰进行了试验，方法的检出限为0．18ng／mL，测定精密度1．9％-3．0％，回收率为96．0％-98．0％。     

氢化物发生/原子吸收分光光度法测定食盐中铅

采用氢化物／原子吸收光谱法测定食盐中痕量铅，使用流动注射氢化物发生器，自动吸入试样和NaBH4溶液，空气／乙炔火焰加热石英管原子化器。对测定条件及共存元素的允许量进行了研究，采用K3[Fe(CN)6]作氧化剂。方法的灵敏度是0．28n/mL/1％吸收，检出限为0．10ng/mL，回收率在94％－102％之间，RSD为2．1％－5．3％。