石墨炉原子吸收光谱法测定水中镉铜铅的在线富集预处理

将流动注射在线预富集系统与石墨炉原子吸收光谱法联用 ,以C18 反相键合硅胶为柱材料,5 -磺基-8 -羟基喹啉为螯合剂 ,2mol/LHCl-0.1mol/LHNO3 为洗脱液 ,以固定体积方式测定了Cd、Cu和Pb ,富集倍数分别为22、28、26(与30μL进样量相比 ) ,检出限(3σ)分别为0.7ng/L、4.2ng/L、5.4ng/L。     

汞的形态分析研究 Ⅱ.固相萃取预富集-液相色谱分离测定不同形态的有机汞

本文报道了固相萃取预富集处理样品继以液相色谱分离测定不同形态痕量有机汞的方法.二乙基二硫代氨基甲酸钠(DDTC)作络合剂及甲醇作洗脱液的预富集系统能在线富集甲基汞(MeHg)、乙基汞(EtHg)和苯基汞(PhHg).用于测定加标海水中MeHg、EtHg和PhHg,回收率分别为96.9％、102.4％和98.0％;相对标准偏差分别为3.5％、5.0％和5.0％;检测下限分别为 1.0μg/L、1.2 μg/L和 1.2 μg/L.     

螯合树脂在线富集火焰原子吸收法测定痕量铅和镉

在pH=4.88的乙酸-乙酸钠缓冲溶液中,用螯合离子交换树脂富集铅和镉,以1.50mol/L HNO3作洗脱液,火焰原子吸收法测定洗脱液中痕量铅和镉。该方法对铅和镉的线性范围分别是4.0～80.0μg/L和2.0～30.0μg/L,检出限分别为1.3μg/L和0.7μg/L。该方法用于地表水中痕量铅和镉的测定,分析结果满意。     

功能性马丙共聚物树脂富集-分光光度法测定痕量铁(Ⅲ)

建立了功能性马来酸酐、丙烯酰胺共聚物树脂P(MA-AM)富集-分光光度法测定痕量Fe(Ⅲ)的新方法。考察了树脂对痕量Fe(Ⅲ)的吸附、洗脱行为。结果表明,在pH=3.5时,P(MA-AM)能富集Fe(Ⅲ),吸附30min时,最大吸附率达98.7%;以3.0mol/L的HCl作为洗脱液,Fe(Ⅲ)的回收率为96.2%;富集倍数可达20倍。该方法的检出限为0.02mg/L,相对标准偏差为3.0%,回收率范围为93.3%～97.6%。方法可应用于实际样品中痕量Fe(Ⅲ)的测定。     

硫代乙酰胺键合硅胶在线选择性固相萃取火焰原子吸收测定环境样品中痕量铜

以制备的硫代乙酰胺键合硅胶为微柱填充材料,建立酸性条件(pH 1 0)下流动注射微柱选择性预富集,0.6 mol/L硫脲溶液洗脱,火焰原子吸收测定环境样品中痕量铜的方法。流动注射在线固相萃取的最佳采样流速为8.0 mL/min;最佳洗脱流速为5.0 mL/min,时间为60 s。在优化的条件下,采样体积为10和50 mL时,线性范围分别为2.0～100.0μg/L和0.5～30.0μg/L;检出限(3σ)分别为0.36和0.07μg/L;富集倍数分别为80和170;相对标准偏差分别为(n=9)3.5%和2.0%。研究了环境样品中常见阴阳离子对测定的干扰。应用于灌木枝叶样品(GBW07602)、标准模拟水样(GBW08608)样品和环境样品中铜的分离与富集,取得满意结果。     

在线固相萃取预富集-原子吸收联用测定痕量Fe(Ⅱ)和总铁量

以1,10-二氮菲(1,10-phen)为配合剂,乙醇为洗脱液,在C₁₈柱上将流动注射固相萃取预富集-原子吸收光谱联用测定痕量Fe(Ⅱ)和总铁.Fe(Ⅲ)的含量可通过抗坏血酸还原后用差示法测得.本法灵敏度高,选择性好,能在线分离干扰富集Fe(Ⅱ),采样速度80次/h,富集倍数19倍,检测下限为3μg/L,相对标准偏差1.1%(n=10),可用于测定水样中痕量Fe(Ⅱ)和Fe(Ⅲ),回收率为94%105%.     

磁芯-硫脲壳聚糖微柱在线流动注射-原子吸收光谱法测定大米中痕量镉

本文将磁芯-硫脲壳聚糖作为固定相填充到自制的微柱中,采用流动注射在线分离富集与火焰原子吸收法联用对大米中痕量镉进行测定。pH=7.0的试液以3.9mL/min速率采样120s,以0.5mol/L HNO3-0.1mol/L硫脲作为洗脱液,用火焰原子吸收光谱法测定洗脱液中Cd2+,检测的线性范围为0.02~1.20μg/mL(r=0.9922),检出限(3σ)为2.5ng/mL,相对标准偏差(RSD)为0.79%(c=1.0μg/mL,n=7),加标回收率在96.0%~104.2%之间。     

流动注射在线吸附预富集-冷蒸气原子荧光法测定矿泉水中的痕量无机汞

研究了聚四氟乙烯管编结反应器(KR)在线吸附预富集技术与冷蒸气原子荧光联用测定矿泉水中痕量无机汞的方法.Hg2+与DDTC在线形成Hg2+-DDTC络合物并吸附在KR内壁上,采用电磁感应加热技术,用20% (V/V) HNO3在线加热洗脱并氧化预富集于KR内壁上的Hg2+-DDTC.洗脱液与KBH4溶液反应生成蒸气态汞,直接用冷蒸气原子荧光联用技术检测.20%(V/V)HNO3作为洗脱液的同时也为氢化发生提供了酸性介质.本方法未使用常用的有机洗脱液,具有操作简单和环保等优点.每小时可分析30个样品,最大吸附倍数为35倍,样品分析精密度RSD为2.2%(n=11),检出限(3σ)为2.0 ng/L.     

巯基葡聚糖(SDG)分离富集-原子荧光光谱法测定地球化学样品中的锡

地球化学样品中锡的测定大多采用以电弧为光源的发射光谱法,该方法为固体进样具有一定的局限性,笔者建立了采用液体进样的原子荧光光谱法测定地球化学样品中的锡弥补了前者的不足。该方法采用了三种不同的前处理过程,分别为碱熔法,酸溶加碱熔法和巯基葡聚糖（SDG）分离富集法。选择4个国家一级地球化学标准物质对碱熔法的熔剂比例、熔样温度和熔剂与样品比例等条件进行了优化,结果表明：当过氧化钠与氢氧化钠比例为5:1,熔剂与样品比例为6:1,在750℃的温度下熔样时,锡的溶出效果最好。酸溶加碱熔的条件在文章不做详述。选择3个国家一级地球化学标准物质对SDG分离富集法的过柱溶液酸度、洗脱液酸度以及洗脱液体积等条件进行了优化,得出结论：当过柱溶液酸度为1%的盐酸时锡的吸附率最高;用3mol·L-1的盐酸作为洗脱液时锡的脱附率最高,且25mL的洗脱液可以把锡完全洗脱出来。碱熔法,酸溶加碱熔法和SDG分离富集法的方法检出限分别为1.03μg·g-1、0.60μg·g-1、0.58μg·g-1,方法精密度分别为3.0%~6.0%、7.0%~9.0%、8.0%~9.0%。选择多个国家一级地球化学标准物质进行方法验证,所有样品的准确度均在90%以上。三种前处理方法均可用于地球化学样品中锡的测定。     

克百威的免疫亲和色谱分析研究

Sepharose CL-4B经碳酰二咪唑(CDI)活化后与纯化的克百威抗体共价偶联,合成了免疫亲和色谱(IAC)固定相,并用其制备了对克百威具有特异性亲和力的IAC柱。对IAC条件进行了优化,选择0.02 mol/L pH 7.2磷酸盐缓冲液(PB)作为吸附与平衡介质,60%（体积分数）甲醇水溶液作为洗脱剂。结果表明:在优化条件下,IAC柱对克百威的动态柱容量达1.58 mg/L。当标样溶液中克百威质量浓度低于 2　μg/L时,经IAC柱富集的效率高于167倍。在河水中按0.1 mg/L水平添加克百威标准品,经IAC柱分离富集,洗脱液采用包被抗体直接竞争酶联免疫吸附分析(ELISA)法检测,5次重复测定的平均回收率为89.8%,相对标准偏差为4.8%。同时采用高效液相色谱(HPLC)法测定洗脱液,与ELISA法测定结果基本一致。     

海水中铜锌铅镉的萃取-反萃取法同时提取-原子吸收光谱法测定

采用萃取-反萃取法同时提取出海水中Cu、Zn、Pb、Cd,Cu、Pb、Cd石墨炉法测定,Zn用火焰法测定.对样品的前处理方法和最佳仪器条件进行了研究,并通过加标实验验证了方法的可靠性.结果表明:萃取-反萃取法能完全满足海水中Cu、Zn、Pb、Cd的前处理要求,可节省一半前处理时间,有溶液稳定、环保、节省试剂等优点.     

Extraction as a method for preparation of vegetable samples for the determination of trace metals by atomic absorption spectrometry

An alternative, simple and rapid technique was developed for a quantitative isolation of the group of eight elements: Al, Ca, Cd, Cu, Fe, Mg, Pb and Zn from vegetable material samples in an open system with the use of acids: conc. HCl, dil. HNO₃ and hydrofluoric acids. Equivalence of both the extractants, HCl and HNO₃, was found suitable for a quantitative isolation of Ca, Cu, Mg, Zn, Pb and Cd. For lead and cadmium, however, dil. HNO₃ proved to be more suitable because these elements are determined by the graphite furnace atomic absorption spectrometry (GF-AAS) technique. A quantitative dissolution of Al and Fe requires hydrofluoric acid as an additional extractant. The proposed method allows to obviate the organic matrix destruction stage, shorten the analyte dissolution time, reduce cost, and minimize hazards of loss and contamination. Validity and versatility of the method developed was verified by the analysis of standard reference materials.     

Sorption characteristics of chelating resins

Chelating resins are used for preconcentrating metal ions in trace analysis. As part of a systematic study of sorption characteristics of the chelating resin Chelex 100, the sorption of Zn(II) and Cd(II) in different aqueous media was investigated. The distribution coefficient (DC) values for both Zn(II) and Cd(II) were extremely low (<4) in 0.5 to 6M HNO₃ and H₂SO₄ solutions. In HCl solution, theDC values for both Zn(II) and Cd(II) were higher, reaching a peak of nearly 40 in 3M HCl solutions. TheDC values for both Zn(II) and Cd(II) increased with increasing pH in chloride, nitrate, and sulfate solutions (0.1M); the value was nearly 10⁴ for both Zn(II) and Cd(II) between pH 5 and 7 and pH 6 and 8, respectively.     

Determination of cadmium and zinc in water samples by flame atomic absorption spectrometry after cloud-point extraction

The phase-separation phenomenon of nonionic surfactants occurring in an aqueous solution was used for the extraction of Cd and Zn from water samples. After complexation with 6-(4-nitrophenyl)-2,4-diphenyl-3,5-diaza-bicyclo[3.1.0]hex-2-ene (NDDBH) in hydrochloric acid medium (pH 1), the analytes were quantitatively extracted after centrifugation into the phase rich in the nonionic surfactant octylphenoxypolyethoxyethanol (Triton X-114). Tetrahydrofuran acidified with 0.1 M HCl was added to the surfactant-rich phase prior to its analysis by flame atomic absorption spectrometry. The adopted concentrations for NDDBH, Triton X-114 and hydrochloric acid were all optimized. Detection limits (3σ) of 0.33 and 0.85 ng/mL along with enrichment factors of 157 and 118 for Cd and Zn, respectively, were achieved. The proposed method was applied to the determination of Cd and Zn in acidic solutions of certified reference materials. A comparison with certified values was performed for an evaluation of the accuracy, resulting in a good agreement according to the t-test at a 95% confidence level. The high efficiency of the cloud-point extraction to carry out the determination of the studied analytes in complex matrices was, therefore, demonstrated. The text was submitted by the authors in English.     

Determination of trace metals in Nile River and ground water by differential pulse stripping voltammetry

The determination of trace metals in river water and ground water by DPSV is seriously disturbed by the presence of organic complexes. The influence of these substances can be eliminated by acidification of the samples with acids. Cd, Pb and Cu were determined at pH 1.1 (HNO₃ medium) and Zn, Cd, Pb and Cu at pH 2 (HCl medium), in both the Nile river and ground water. Zn was determined at pH 3.5 in HCl and pH 4.5 in HNO₃, after neutralizing the samples with NH₃/NH₄Cl buffer. Manganese could then be determined, after further addition of ammoniacal buffer solution up to pH 7.5 and 8.5. Ni and Co were determined in the adsorptive mode after formation of dimethylglyoximates at pH 9.2. The effect of pH on the stripping peaks of manganese was studied. Good agreement was observed between DPSV and AAS results for Zn, Cd, Pb, Cu and Mn, but the concentrations of Ni and Co were below the detection limits for AAS. Good agreement was obtained between DPSV results in HCl and HNO₃ for Ni and Co. The results indicate that decomposition of organic complexes by acidification with HNO₃ is better than in the case with HCl for Zn, Pb, Cu, Ni and Co, but HCl is better than HNO₃ for Cd and Mn.     

Simultaneous determination of Cu2+, Zn2+, Cd2+, Hg2+ and Pb2+ by using second-derivative spectrophotometry method

A new method of simultaneous determination of Cu2+, Zn2+, Cd2+, Hg2+ and Pb2+ is proposed here by using the second-derivative spectrophotometry method. In pH=10.35 Borax-NaOH buffer, using meso-tetra (3-methoxyl-4-hydroxylphenyl) porphyrin ([T-(3-MO-4-HP)P]) as chromomeric reagent, micelle solution was formed after Tween-80 surfactant was added into the solution containing Cu2+, Zn2+, Cd2+, Hg2+ and Pb2+ ions. The original absorption spectrum of the above complexes was obtained after heating in the boiling water for 25 min. The second-derivative absorption peaks of five metal-porphyrin complexes can be separated from the original absorption spectrum by using chemometric tool. In this way, Cu2+, Zn2+, Cd2+, Hg2+ and Pb2+ ions can be determined simultaneously. Under the optimal conditions, the linear ranges of the calibration curve were 0-0.60, 0-0.60, 0-0.40, 0-0.80 and 0-0.48 μg mL(-1) for Cu2+, Zn2+, Cd2+, Hg2+ and Pb2+, respectively. The molar absorptivity of these color systems were 1.38×10(5), 1.01×10(5), 3.24×10(5), 1.07×10(5) and 1.29×10(5)Lmol(-1)cm(-1). The method developed in this paper has advantages in selectivity, sensitivity, operation and can effectively resolve spectra overlapping problem. This method has been applied to determine the real samples with satisfactory results.     

Sorption of Zn(II) and Cd(II) by chelating resins: Comparison of three resins

Ion-exchange resins, especially chelating resins are used for pre-concentration of metal ions in trace analysis as well as for radiochemical separations following neutron activation of a variety of environmental samples. As part of a systematic study of the sorption characteristics of chelating resins, sorption of Zn(II) and Cd(II) by three chelating resins were studied for various acid conditions in nitrate and chloride media. Both Zn(II) and Cd(II) showed similar behavior. Under higher acid conditions, maximum sorption occurred in 3M HCl solutions. Under low acid conditions, the sorption increased with pH. Chelex 100 gave the highest sorption among the three resins. This revised version was published online in July 2006 with corrections to the Cover Date.     

Ion-chromatographic trace analysis of mercury, cadmium and zinc by post-column derivatisation with a water-soluble porphyrin

Summary A post-column derivatisation system with mesotetra (4-sulfonatophenyl)-porphyrin (TPPS₄) and PAR as accelerating agent in a borate buffer pH 11.5 in the presence of tartrate and NaCl is proposed. The complexes of Cd, Zn and Hg have maximum absorption at 430 nm. The separation system consists of silica-gel chemically bonded cation exchanger as stationary phase and a tartrate-NaCl solution as mobile phase. The separation can be finished within 10 min. The calibration curves of these metal ions with the peak area of the chromatogram were found to be linear in the range of 0.002–0.8, 0.1–8.0 and 0.05–20.0 mg/l for Cd, Hg and Zn. The detection limits for Cd, Hg and Zn are 0.05, 5 and 1 ng. This new method was applied to the analysis of waste water, silicates and corn with satisfying results.

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Ionen-chromatographische Spurenanalyse von Hg, Cd und Zn durch Nachsäulen-Derivatisierung mit einem wasserlöslichen Porphyrin

     

微波消解-GFAAS测定浅水湖泊底泥中重金属元素

探讨了采用微波消解作为底泥样品的前处理方法,运用石墨炉原子吸收法测定浅水湖泊底泥中Cu,Pb,Zn,Cd,Cr含量的实验条件.方法的RSD为2.0％～4.1％,平均回收率为97.4％～101.5％,Cu,Pb,Zn,Cd,Cr的检出限分别为0.4,5,2.8,0.25,2.5ng.该法适合于浅水湖泊底泥中重金属含量的测定.     

Tetrakis(thiadiazole)porphyrazines. 8. Singlet oxygen production, fluorescence response and liposomal incorporation of tetrakis(thiadiazole)porphyrazine macrocycles [TTDPzM] (M = Mg(II)(H2O), Zn(II), Al(III)Cl, Ga(III)Cl, Cd(II), Cu(II), 2H(I))

The photoactivity for the generation of singlet oxygen, (1)O(2), the key cytotoxic agent in the anticancer treatment known as photodynamic therapy (PDT), and the fluorescence response of the highly electron-deficient tetrakis(thiadiazole)porphyrazines of formula [TTDPzM] (M = Mg(II)(H(2)O), Zn(II), Al(III)Cl, Ga(III)Cl, Cd(II), Cu(II), 2H(I)) were examined (c ? 10(-5) M) in dimethylformamide (DMF) and/or in DMF preacidified with HCl (DMF/HCl; [HCl] = 1-4 × 10(-4) M). The singlet oxygen quantum yield (Φ(Δ)) of all the compounds was determined by using a widely employed procedure based on the selective oxidation of the 1,3-diphenylisobenzofuran (DPBF), modified in part as reported. The list of the Φ(Δ) values indicates excellent photosensitizing properties for the series of compounds carrying "closed shell" metal ions, with values measured in DMF/HCl respectful of the "heavy atom effect" for the first four lighter centers, increasing in the order Mg(II) < Al(III) < Zn(II) < Ga(III). Data of Φ(Δ) concerning the unmetalated species [TTDPzH(2)], present in solution in the form of the corresponding anion [TTDPz](2-), and the Cd(II) and Cu(II) complexes are also presented and discussed. Extensive discussion is also developed on the fluorescence quantum yield values Φ(F), with data on the Mg(II) and Al(III) compounds in DMF/HCl (0.44 and 0.53, respectively) indicative of promising perspectives for applications in fluorescence imaging techniques. The Φ(F) data of the studied porphyrazine series, Φ(F)(Pz), correlate linearly with those of the homologous phthalocyaninato complexes, Φ(F)(Pc), suggesting a closely similar behaviour between the two classes of compounds. The incorporation of [TTDPzZn] into liposomes was successfully achieved following the detergent depletion method (DDM) from a mixed micellar solution by means of gel-filtration. Retention of [TTDPzZn] (~40%) in its photoactive monomeric form into liposomes is proved by absorption and fluorescence spectra, this proposing the Zn(II) complex as a promising candidate for use in PDT.