钯作基体改进剂FIA—HG—GFAAS法测定锗及其机理研究

采用钯，钯－镁作基体改进剂，ＦＩＡ－ＨＧ－ＧＦＡＡＳ法成功地测定了锗。灵敏度，精密度和分析速度都得到很大的提高，峰值吸收的特征质量８．０ｐｇ，检出限１０．９ｐｇ，相对标准偏差０．３４％，同时探讨了基体改进剂钯的稳定作用机理及锗在石墨管中的原子化机理。     

石墨炉原子吸收法测定人体血浆和尿中锗

研究了口服有机锗（Ｇｅ－１３２）后人体血浆及尿中锗的测定方法。以５％三氯乙酸溶液沉淀血蛋白，离心分离后，取上清液测定。以钯和硝酸镍混合溶液做基体改进剂，提高灰化温度至１４００℃，消除了样品中大量基体对测定锗的干扰。方法特征量为３１ｐｇ，检出限为２８ｐｇ（３σ），样品加标准回收率为：血浆９１．４％～９７．０％，尿９７．２％～１０５％。     

混合基体改进剂石墨炉原子吸收法测定锗的方法研究

石墨炉原子吸收法，涂钼热解管，Ｐｔ－Ｎｉ混合基体改进剂，Ｚｅｅｍａｎ效应扣除背景，在１４００℃灰化温度下直接测定锗，方法简单，结果满意。特征质量为２０．３ｐｇ／０．００４Ａ。     

石墨炉原子吸收法测定人体血尿和尿中锗

研究了口服有机锗后人体血浆及尿中锗的测定方法。以５％三氯乙酸溶液沉淀血蛋白，离心分离后，取上清液测定。以钯和硝酸镍混合溶液做基体改进剂，提高灰化温度至１４００℃，消除了样品中大量基体对测定锗的干扰，方法特征量为３１ｐｇ，检出限为２８ｐｇ（３σ），样品加标准回收率为：血浆９１．４％￣９７．０％，尿９７．２％￣１０５％。     

平台石墨炉原子吸收法测定高温镍基合金中砷

研究了基体改进剂，灰化，原子化温度和共存元素的干扰。采用钯作基体改进剂和匹配基体镍后，提高了灵敏度，增强了抗干扰能力。在波长１９７．２ｎｍ处，用平台石墨炉原子吸收法直接测定了高温镍基合金中砷。方法特征是为８８ｐｇ，检出限为０．２７μｇ．ｇ＾－１，相对标准偏差为３．１％－５．１％，回嵋率为８５％－１００％。     

病人血样中痕量锗,锶的石墨炉原子吸收光谱法测定

本文运用石墨炉ＡＡＳ法加基体改进技术，测定了５０岁以上病人血清及环境水样中锗和锶的含量。用０．０１ｍｏｌ／ＬＨＮＯ３－０．１％ＴｒｉｔｏｎＸ－１００稀释血清，测定精度可与火焰法媲美。锗，锶的特征量分别为２８ｐｇ和１８ｐｇ；线性范围为０－２５０ｎｇ／ｍＬ和－３５．０ｎｇ／ｍＬ；相对标准偏差（ｎ＝１０）４．１０％和２．４９％；回收率分别为９２．２％－９９．０％和９２．０％１０２％。方法快速准确，结果满     

溶剂萃取石墨炉原子吸收光谱测定盐卤中痕量铷

采用石墨炉原子吸收光谱（ＧＦＡＡＳ）研究盐卤中铷的原子化行为和机理,建立了热解石墨管,ＫＮＯ３－ＮＨ４ＮＯ３基体改进剂,１８－冠－６,溴百里香酚蓝,氯仿萃取分离ＧＦＡＡＳ测定盐卤铷的方法。用于测定盐卤中痕量铷,特征质量１．１×１０＾－１０ｇ／０．００４４,加标回收率８９％￣１１０％;相对标准偏差６．２８％（ｎ＝１３）。     

中药片仔癀,六味地黄丸中的微量铬,铅和镉石墨炉原子吸收法测定

本文采用ＧＦ－ＡＡＳ加平台技术，基体改进剂，测定了中药片仔癀，六味地黄丸中铬、铅和镉的含量，铬、铅和镉的线性范围分别为０－０．８ｎｇ／ｍＬ，０－５０ｎｇ／ｍＬ，０－５ｎｇ／ｍＬ，回收率分别为１０２－１０３％，９９－１０１％，９７．５－９８％，本方法简便快速、准确。     

平台石墨炉原子吸收法测定高温镍基合金中铋

本文用１ｍｇ／ｍＬ镍和０．２ｍｇ／ｍＬ钯作混合基体改进剂，提高了测定铋的灰化温度和抗干扰能力，且灵敏度几乎不变。可不经分离样品基体，直接用平台石墨炉原子吸收法测定高温镍基合金中铋。方法特征量为１８ｐｇ，检出限为０．０８１μｇ／ｇ。对含０．３－０．７μｇ／ｇ铋的镍基样品测定，相对标准偏差为３．０％－５．９％，回收率在８５％－１１９％之间。     

2－（2－噻唑偶氮）－5－〔N，N－二羧基甲基）氨基〕苯甲酸与钯显色反应的研究及其应用

报道了一种对钯离子具有高灵敏度和选择性的新试剂２－（２－噻唑偶氮）－５－［（Ｎ，Ｎ－二羧基甲基）氨基］苯甲酸（ＴＡＤＣＡＢ）。在０．５ｍｏｌ／ＬＨＮＯ＿３介质中，ＴＡＤＣＡＢ与Ｐｄ（Ⅱ）形成蓝色配合物，组成为Ｐｄ：ＴＡＤＣＡＢ＝１：２，最大吸收波长６５２ｎｍ。钯浓度在０～１．４μｇ／ｍＬ范围内符合比耳定律。用双波长法测定，表观摩尔吸光系数ε＿（６５２．０～５３３．６）＝８．２×１０￣４Ｌ·ｍｏｌ￣（－１）·ｃｍ￣（－１），可以允许大量金属离子共存。所确立的方法无需掩蔽剂和其它分离手段，即可直接用于Ｐｔ－Ｐｄ催化剂中微量钯的测定，结果满意。     

Determination of palladium in airborne particulate matter in a German city

The part of palladium in ambient urban air that is bound to particles and soluble in aqua regia was determined by means of sorbent extraction, coupled with graphite furnace atomic absorption spectrometry (GFAAS) and laser absorption fluorescence spectrometry (LAFS). Samples of about 200 m3 air were taken in a suburb of Berlin, Germany. The coupling of the selective and automated pre-concentration procedure for Pd as N,N-diethyl-N'-benzoylthiourea complex with the respective detection methods proved to be sufficiently sensitive. Severe interference with other matrix constituents, occurring mainly by direct LAFS detection, could be overcome and the detection limit was improved tremendously. The concentration of Pd in ambient air was determined to be in the range from 0.2 to 14.6 pg/m3.     

Analysis of palladium concentrations in airborne particulate matter with reductive co-precipitation, He collision gas, and ID-ICP-Q-MS

The concentration of platinum group elements (PGE) in the environment has increased significantly in the last 20 years mainly due to their use as catalysts in automotive catalytic converters. The quantitation of these metals in different environmental compartments is, however, challenging due to their very low concentrations and the presence of interfering matrix constituents when inductively coupled plasma-mass spectrometry (ICP-MS) is used for analysis. Previously, the research focus was on the analysis of platinum (Pt) and rhodium (Rh). However, due to the increasing use of palladium (Pd) in automotive catalytic converters, quantitation of this element in airborne particulate matter (PM) is also needed. Compared to Pt and Rh, measurements of Pd using ICP-MS are plagued by greater molecular interferences arising from elements such as copper (Cu), zinc (Zn) strontium (Sr), yttrium (Y), and zirconium (Zr). The aim of this study was to evaluate the applicability of reductive co-precipitation procedures using both mercury (Hg) and tellurium (Te) for the pre-concentration of Pd from airborne PM. Furthermore, helium (He) was tested as a collision gas for isotope dilution-inductively coupled plasma-quadrupole-mass spectrometry (ID-ICP-Q-MS) to measure Pd in the Hg and Te precipitates. Airborne PM samples (PM₁₀) were collected from Neuglobsow (Brandenburg, north-eastern Germany) and Deuselbach (Rhineland-Palatinate, south-western Germany), considered to represent background levels, and from the city Frankfurt am Main (Hesse, Germany), a high-traffic area. Samples were first digested with aqua regia in a high-pressure asher (HPA) at 320 °C and 130 bar prior to the application of reductive co-precipitation procedures. The method was validated with road dust reference material BCR-723 and the CANMET-CCRMP reference material TDB-1 and WPR-1. In airborne PM collected at the background areas Neuglobsow and Deuselbach, Pd was detected with median concentrations values of 0.5 and 0.6 pg/m³, respectively. Much higher median concentration values of 14.8 pg Pd/m³ (detection limit = 0.01 pg Pd/m³) were detected in samples collected in the city of Frankfurt am Main. Results have shown that Hg co-precipitation depletes the concentrations of interfering matrix constituents by at least one order of magnitude more, compared to Te co-precipitation, making it a more effective method for the isolation and pre-enrichment of Pd from airborne PM prior to analysis. The use of a He gas flow of 120 ml/min in the plasma further minimized interferences, particularly those arising from CuAr⁺, YO⁺, and ZrO⁺ during the determination of Pd. The results demonstrate that Hg co-precipitation and the use of He collision gas, in combination with isotope dilution, are highly effective methods for the quantitation of Pd in airborne PM using ICP-MS.      

不同基体改进剂对石墨炉原子吸收法测定土壤和沉积物中铊的影响

应用Pd(NO3)2-抗坏血酸(Vc)基体改进剂,建立了石墨炉原子吸收法(GFAA法)测定土壤和沉积物样品中铊。针对土壤和沉积物复杂基体,GFAA法测定铊元素主要受到氯离子的干扰,文中研究了常见基体改进剂(包括NH4NO3,(NH4)2SO4,La(NO3)3,Mg(NO3)2,Vc,Pd(NO3)2,Pd(NO3)2-Vc)对氯离子的抑制效果。通过研究不同基体改进剂测定含氯铊标准溶液的吸收曲线,探讨出基体改进剂测定铊的作用机理。以土壤或沉积物标准物质为研究对象,优化了应用Pd(NO3)2-Vc测定铊的灰化温度、基改剂浓度以及原子化温度。在最佳实验条件下,通过比较有无基体改进剂条件下,采用GFAA法测定不同土壤和沉积物中铊的精密度和准确度,实验结果表明,应用Pd(NO3)2-VC基体改进剂,测定土壤和沉积物标准物质中铊的测定结果都在标准值范围之内,6次平行测定的相对标准偏差范围为2.8%~8.4%,用于测定实际土壤和沉积物样品加标回收率为128.0%和92.9%。     

The formation of palladium nanocomposite catalysts on the porous silicon used as anodes of fuel cells

Palladium nanoparticles on the porous silicon were synthesized by radiation-chemical reduction in the solution of reversed micelles. The Pd nanoparticles obtained are electron deficient. The porosity, the type of conductivity, the silicon matrix pore geometry, and precursor parameters influence the size, the shape and the charge state of palladium catalysts. The mechanism of H₂ and HCOOH electrooxidation on porous silica in the presence of Pd+/Pd redox pair is proposed.     

Determination of palladium in airborne particulate matter in a German city

The part of palladium in ambient urban air that is bound to particles and soluble in aqua regia was determined by means of sorbent extraction, coupled with graphite furnace atomic absorption spectrometry (GFAAS) and laser absorption fluorescence spectrometry (LAFS). Samples of about 200 m³ air were taken in a suburb of Berlin, Germany. The coupling of the selective and automated pre-concentration procedure for Pd as N,N-diethyl-N’-benzoylthiourea complex with the respective detection methods proved to be sufficiently sensitive. Severe interference with other matrix constituents, occurring mainly by direct LAFS detection, could be overcome and the detection limit was improved tremendously. The concentration of Pd in ambient air was determined to be in the range from 0.2 to 14.6 pg/m³.     

Gold‐Palladium Nanocluster Catalysts for Homocoupling: Electronic Structure and Interface Dynamics

The gold‐palladium (Au?Pd) bimetallic nanocluster (NC) catalyst in colloidal phase performs the homocoupling reaction of various aryl chlorides (Ar?Cl) under ambient conditions. We have systematically investigated various aspects of the Au?Pd NC catalysts with respect to this homocoupling reaction by using density functional theory (DFT) calculations, genetic algorithm (GA) approaches, and molecular dynamics (MD) simulations. Our findings include the geometric and electronic structures of the Au?Pd NC, the reactive Pd sites on the NC surface, the electron‐donating effects of surrounding polymer matrix, the reaction mechanism of homocoupling reaction and rate‐determining step, the inverse halogen dependence of the reaction, and the solvation dynamics at interface region between NC and polymer matrix in aqueous solution.     

Electrodeposition and characterization of Pd nanoparticles doped amorphous hydrogenated carbon films

Palladium (0) nanoparticles incorporated hydrogenated amorphous carbon (Pd/a-C:H) films were synthesized on single crystal silicon (100) substrates by electrochemical deposition route using methanol and camphor as carbon source, and Pd nanoparticles as dopant. The characterization results indicate that Pd nanocrystalline particles with diameter in the range of 1–5 nm dispersed in the amorphous carbon matrix. Compared with pure a-C:H films, the introduction of Pd nanoparticles didn't change the structure of carbon films. At the end, the growth mechanism of the Pd/a-C:H composite films was discussed.     

X-ray photoelectron spectroscopic study of the mechanism of palladium matrix modification in the electrothermal atomic absorption spectrometric determination of lead and bismuth

The mechanism of palladium matrix modification is studied for the determination of lead and bismuth by graphite-furnace atomic absorption spectrometry. The binding energies of the charring products for lead and bismuth in the presence or absence of palladium obtained at the initial stage of atomization were measured. The binding energies indicated the formation of PbPd and BiPd bonds, thus explaining the increase in appearance temperatures of lead and bismuth in the presence of palladium.     

Determination of As, Cd, and Pb in epicuticular waxes of pine and spruce needles by ETAAS

 Waxes were separated from needles by chloroform washing, drying and dissolving the residue in tetrahydrofuran (THF). Both a THF solution of the wax and an aqueous solution of the Pd-Mg matrix modifier were sampled directly into the graphite tube. The reaction conditions were optimised for the wax concentration of 45 mg ml^-1 in THF and the Pd:Mg ratio of 1:1 in the matrix modifier. The atomisation and charring temperatures for As, Cd and Pb were the same as those recommended for analysis of aqueous solutions except the charring temperature of Cd takes 200 °C lower. The characteristic masses for As (26 pg), Cd (0.5 pg) and pb (9 pg) are also comparable to published data. The parameters of calibration curves were identical for all three elements dissolved either in clear THF or in the wax solution. Elemental concentrations were found to range from 0.1 to 1.0 mg g^-1, increasing with needle age for As, Pb but not Cd. Received: 20 September 1996 / Revised: 14 November 1996 / Accepted: 13 December 1996     

Preparation of 103Pd seeds Part II. “Molecular Plating” of 103Pd onto copper rod

A method for ¹⁰³Pd molecular plating onto the surface of the copper rod is reported. The optimal composition of the plating bath was: palladium chloride 2 g/l, ammonium hydroxide (28%) 150 ml/l, sodium hypophosphite 12 g/l, and ammonium chloride 37 g/l. The whole procedure of ¹⁰³Pd molecular plating will last 50 minutes at 40 °C. This article provides valuable experience for the preparation of ¹⁰³Pd seeds.