反应液温度对氢化物生成过程的影响及氢化物稳定性的考察

自1969年Holak把氢化物发生技术用于原子吸收光谱分析以来,在各个领域均已得到广泛应用。在此期间,一些工作者对影响氢化物生成的条件,原子化机理,干扰及其消除等方面做了研究,但有关反应液温度对氢化物生成过程的影响及氢化物稳定性方面的报导甚少。本文对此进行了系统考察,并对实验结果进行了探讨。实验 1.仪器与装置:岛津AA-610s原子吸收分光光度计;自制的手动注射式氢化物发生     

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-电感耦合等离子体质谱联用技术研究

运用自制的接口，实现了氢化物发生与电感耦合等离子体质谱的联用。考察了连续流动氢化物发生器、气动型断流式氢化物发生器及气动型流动注射氢化物发生器与电感耦合等离子体质谱仪的联用性能。确定了仪器的最佳参数，研究了系统的分析性能，实现了能生成氢化物的8种元素的定量测定。     

氢化物发生-原子吸收半自动流动注射分析法测定环境样品中痕量砷

本文研究将半自动流动注射分析体系用于氢化物发生-原子吸收法测定环境样品中μg/L水平的砷。分析速度可达220样/小时。文中讨论了砷的价态及试样中共存离子对测定的影响。分析NBS标准参考物质取得了与推荐值比较一致的结果。     

流动注射在线离子交换预富集-氢化物发生原子荧光光谱法测定痕量碲的研究

研究了流动注射在线离子交换预富集及在线氢化物发生法与原子荧光光谱法的联用技术。设计了双柱交替正向富集和反向洗脱的在线离子交换流路系统。在采样频率为３０次／ｈ下，灵敏度较常规流动注射氢化物发生原子荧光光谱法提高１１倍。应用于环境水样中痕量碲的分析，获得了满意的结果。     

二乙基二硫代氨甲酸银体系流动注射法测定砷

本文设计了一种ＡｇＤＤＣ流动注射－分光光度法测定砷的系统。该系统采用自制的氢化物发生及吸装置，将液体流路和载气流路结合在一起。     

流动注射氢化物发生-原子吸收光谱法测定食品中的无机砷

探讨并建立了流动注射氢化物发生-原子吸收光谱(FI-HAAS)法测定食品中无机砷的样品前处理方法.该法简便快捷,用6种国家标准参考样品进行考察,分析结果可靠.     

流动注射在线离子交换预富集—氢化物发生原子荧光光谱法测定痕量…

研究了流动注射液在线离子交换预富集及在线氢化物发生法与原子荧光光谱法的联用技术，设计了双柱交替正向富集和反向洗脱的在线离了交换流路系统。在采样频率为３０次／ｈ下，灵敏度较常流动注射氢化物发生原子荧光光谱法提高了１１倍，应用于环境水样痕量碲的分析，获得了满意的结果。     

流动注射在线共沉淀分离富集HG—AFS测定痕量锗

提出了一种流动注射在线共沉淀-氢化物发生-原子荧光光谱法测定痕量锗的分析方法。设计了在线共沉淀及氢化物发生流路和操作程序,选择了各项化学条件和流路参数。方法操作简便快速,分析速度为30/h,检出限为0.11ng,相对标准偏差（n=5)为5.6%,经国家一级地质标样分析验证,方法可靠实用。     

底泥中汞的流动注射-氢化物原子吸收光谱法检测

流动注射分析系统与氢化物发生原子吸收光谱仪联用，测定底泥中的汞、操作简便，稳定性较好，而且样品和试剂消耗量较少，可用来进行痕量样品的测定。方法的线性范围为1－20μg/L,检出限为0.005mg/kg。     

Decomposition of organoarsenic compounds by using a microwave oven and subsequent determination by flow injection-hydride generation-atomic absorption spectrometry

Environmentally important organoarsenicals such as arsenobetaine, arsenocholine and tetramethylarsonium ion do not form volatile hydrides under the commonly used analytical conditions on treatment with borohydride and it has been difficult to determine their concentrations without further derivatization. This paper describes a rapid method which completely decomposes and oxidizes these arsenicals to arsenate by using potassium persulphate and sodium hydroxide with the aid of microwave energy. The quantitative decomposition of these species permits their determination at low nanogram levels, by hydride generation atomic absorption spectromety (HG AA). A new hydride generator which has high efficiency and minimum dead volume and therefore is suitable for flow injection analysis (FIA) is also described. A system combining flow injection analysis, online microwave oven digestion, and hydride generation followed by atomic absorption measurement, is developed. This system is capable of performing analysis at a sample throughput of 100-120 per hour. Calibration curves were linear from 10 to 200 ng cm^?3 of arsenic and the detection limit was 5 ng cm^?3 for a 100-μ injection or 0.5 ng of arsenic. All ten organoarsenic compounds studied gave arsenate as the decomposition product, which was confirmed by using molybdenum blue photometric measurement.     

流动注射-氢化物发生-电感耦合等离子体发射光谱法测定环境样品中的砷

采用流动注射－氢化物发生－电感耦合等离子体发射光谱法测定环境样品中的砷。对测定条件及干扰因素进行了研究。在选定条件下，方法的检出限为0.0002mg/L，测定结果的相对标准偏差为1.25%。对几种国家标准物质进行测定，测定结果较准确。     

Continuous flow hydride generation for the preconcentration and determination of arsenic and antimony by GFAAS

A method has been developed for the determination of arsenic and antimony at sub-ppb level using hydride preconcentration inside the graphite furnace. The influence of the quality of the graphite surface, of its modification with palladium coating and of the ways of introducing hydride into the furnace on the analytical signal is discussed. After optimization of system parameters, detection limits of 25 and 36 pg were obtained for arsenic and antimony. Characteristic masses (for arsenic and antimony, respectively) were 31 and 33 pg/0.0044 A·s for direct injection GFAAS and 69 and 57 pg/0.0044 A·s for hydride in situ preconcentration and atomization in the palladium coated graphite tube. Therefore the overall efficiency of the hydride generation and trapping was estimated to be 45 and 58% for arsenic and antimony, respectively.     

High performance liquid chromatography hydride generation in situ trapping graphite furnace atomic absorption spectrometry: A new way of performing speciation analysis using GFAAS as detector

A new procedure for the speciation analysis of hydride forming elements using GFAAS as detector is proposed. The separation of the species is performed by HPLC and the eluent flow is merged with HCl and NaBH₄ solutions moved by peristaltic pumps controlled by a flow injection apparatus. As the species emerges from the column, its respective hydride is formed and carried through the autosampler capillary to an Ir treated graphite tube pre-heated at 300 °C, where it is trapped. After the hydride collection, the autosampler arm is moved from the tube and atomization takes place. The sequence is repeated for the next emerging species. The feasibility of the system was evaluated for the speciation of As (III) and As (V) in waste water samples. The retention times were previously determined using a more concentrated mixed analytical solution and a quartz tube as atomizer. The analytical curves obtained by the proposed procedure showed similar slopes for both species as well as coefficient of regression better than 0.99. Limits of detection were 0.2 ng/mL for both species, 50 times better then the same assembly using a quartz tube atomizer. In the analysis of certified reference materials the sum of the As (III) and As (V) species concentrations were in close agreement with the arsenic concentration certified for total arsenic.     

Arsenic and antimony determination by on-line flow hydride generation–glow discharge–optical emission detection

Hollow cathode (HC) and conventional flat cathode (FC) glow discharge (GD) optical emission spectrometry (OES) were used as detectors for the determination of arsenic and antimony by on-line hydride generation (HG) in a flow system. Both radiofrequency (rf) and direct current (dc) sources were investigated to produce the discharge. The design of the HC and FC and also the parameters governing the discharge (pressure, He flow rate, voltage, current and delivered power) and the HG (sodium borohydride concentration and reagent flow rates) were investigated using both cathodes. The analytical performance characteristics of HG–GD–OES with HC and FC were evaluated for some emission lines of arsenic (193.7, 200.3, 228.8 and 234.9 nm). The best detection limit (0.2 μg l⁻¹) was obtained when the emission line of 228.8 nm was used with FC. Under the same arsenic optimized experimental conditions, the system was evaluated to determine antimony at 259.7, 252.7 and 231.1 nm, 252.7 nm being the emission line which produced the best detection limit (0.7 μg l⁻¹). The rf-HC–GD–OES system was applied successfully to the determination of arsenic in freeze-dried urine in the standard reference material 2670 from NIST. Finally, a flow injection system was assayed to determine arsenic at 228.8 nm, using a dc-GD with both FC and HC. The results indicated that for low volumes of sample, the HC discharge allows better analytical signals than the FC.     

Automated system for on-line determination of dimethylarsinic and inorganic arsenic by hydride generation–atomic fluorescence spectrometry

A multisyringe flow-injection approach has been coupled to hydride generation-atomic fluorescence spectrometry (HG-AFS) with UV photo-oxidation for dimethylarsinic (DMA), inorganic As and total As determination, depending on the pre-treatment given to the sample (extraction or digestion). The implementation of a UV lamp allows on-line photo-oxidation of DMA and the following arsenic detection, whereas a bypass leads the flow directly to the HG-AFS system, performing inorganic arsenic determination. DMA concentration is calculated by the difference of total inorganic arsenic and measurement of the photo-oxidation step. The detection limits for DMA and inorganic arsenic were 0.09 and 0.47 μg L(-1), respectively. The repeatability values accomplished were of 2.4 and 1.8%, whereas the injection frequencies were 24 and 28 injections per hour for DMA and inorganic arsenic, respectively. This method was validated by means of a solid reference material BCR-627 (muscle of tuna) with good agreement with the certified values. Satisfactory results for DMA and inorganic arsenic determination were obtained in several water matrices. The proposed method offers several advantages, such as increasing the sampling frequency, low detection limits and decreasing reagents and sample consumption, which leads to lower waste generation.     

Advances in On-Line Hydride Generation Atomic Spectrometric Determination of Arsenic

Flow analysis has played a major role in many areas of chemical analysis, making operations more robust and precise. It facilitates experimental studies opening new areas of research. In the field of arsenic research, there are various examples of surveys concerning arsenic determination and its species with the use of flow injection analysis (FIA) and sequential injection analysis (SIA). The increasing concern over the human exposure to arsenic and its species has necessitated the development of rapid, highly sensitive, precise, and accurate analytical methods for its determination in trace levels in environmental and biological samples. This review provides a literature survey on the automatic on-line hydride generation methodologies coupled to atomic spectrometry for determination of inorganic and organic arsenic species, during the last decades. All advances in on-line manifolds are categorized and highlighted. There are several reports of manifolds and setup instrumentation concerning hydride generation including continuous flow analysis (CFA), FIA, SIA, lab-on-valve (LOV), multicommutation flow systems, and hyphenated techniques. On-line preconcentration and pretreatment methodologies coupled with hydride generation such as solid phase extraction, co-precipitation and trapping are also discussed, as they are of particular interest in the development of fully automated methods.     

Exploiting in situ hydride trapping in tungsten coil atomizer for Se and As determination in biological and water samples

A flow injection hydride manifold was coupled to a 150 W tungsten coil electrothermal atomizer for in situ hydride collection followed by selenium and arsenic determination by ET AAS. Rhodium (200 μg), thermally reduced over the double layer tungsten atomizer, was very efficient at collecting selenium or arsenic hydrides. Prior to analysis, biological samples were digested in closed-vessels microwave digestion system. Prior to the hydride formation, both selenium and arsenic were reduced to valence state (IV) and (III), respectively. The detection limit was 35 ng L⁻¹ for selenium and 110 ng L⁻¹ for arsenic. Sample throughput was 70 h⁻¹ using 30 s of hydride trapping time. Method accuracy was evaluated by analyzing biological-certified reference materials from the National Institute of Standard and Technology (SRM-1577a and SRM-1577b “bovine liver” and RM-8414 “bovine muscle powder”) and from the International Agency for Energy Atomic (A-13 “animal blood”) and one water-certified reference material from the National Institute of Standard and Technology (SRM-1640 trace elements in natural water). By applying a t-test, there was no significant difference at the 95% probability level between the results obtained with the proposed method and those certified values.     

Differential determination of arsenic (III) and total arsenic with L-cysteine as prereductant using a flow injection non-dispersive atomic absorption device

Speciation of arsenic in environmental samples gains increasingly importance, as the toxic effects of arsenic are related to its oxidation state. A method was developed for the determination of trace amounts of arsenic (III) and total arsenic by flow injection hydride generation coupled with an in-house made non-dispersive AAS device. The total arsenic is determined after prereduction of arsenic (V) to arsenic (III) with L-cysteine in a low concentration of hydrochloric, acetic or nitric acid. The conditions for the prereduction, hydride generation and atomization were systematically investigated. A quartz tube temperature of 800 degrees C was found to be optimum in view of peak shape and baseline stability. Pb(II), Ni(II), Fe(III), Cu(II), Ag(I), Al(III), Ga(II), Se(IV), Bi(III) were checked for interfering with the 2 microg/L As(V) signal. A serious signal depression was only observed for Se(IV) and Bi(III) at a 150-fold excess. With the above system, arsenic was determined at a sampling frequency of about 1/min with a detection limit (3sigma) of 0.01 microg/L using a 0.5 mL sample. The reagent blank was 0.001+/-0.0003 absorbance units and the standard deviation of 10 measurements of the 2 microg/l As signal was found to be 1.2%. Results obtained for standard reference materials and water samples are in good agreement with the certified values and those obtained by ICP-MS