浊点萃取-石墨炉原子吸收光谱法测定膨化食品中铅

以8-羟基喹啉(8-HQ)为螯合剂,在pH 9缓冲溶液中,痕量铅(Ⅱ)与8-HQ生成螯合物,加入表面活性剂Triton X-100用浊点萃取分离富集样品中痕量铅。分取部分表面活性剂相用0.1mol·L-1硝酸溶液定容至2mL,所得溶液直接用石墨炉原子吸收光谱法进行测定。对影响浊点萃取的因素和共存离子的干扰等进行了试验并予以优化。方法的检出限(3σ)为0.85pg。应用所提出的方法测定了膨化食品样品中铅的含量,在5种样品中用标准加入法进行方法的回收试验,测得回收率在91.7%～101.7%之间。     

浊点萃取-石墨炉原子吸收光谱法测定环境样品中的痕量镉

研究了浊点萃取-石墨炉原子吸收光谱法(GFAAS)测定痕量镉的新方法,利用表面活性剂Triton X-100和络合剂1-(2-吡啶偶氮)-2-萘酚(PAN)对镉进行浊点萃取。详细探讨了影响浊点萃取及测定灵敏度的因素。优化条件为:0.25 mL 30%NaC l,pH 8.5,0.50 mL、4.0×10-4mol/L PAN,0.2 mL 1.0%TritonX-100。在最佳条件下,镉的富集倍率为50倍,检出限为5.9 ng/L,RSD为2.1%。该方法用于环境样中痕量镉的富集和测定,结果令人满意。     

浊点萃取-石墨炉原子吸收光谱法测定食品包装材料中锑

以吡咯烷二硫代氨基甲酸铵(APDC)为络合剂,在pH5.0乙酸-乙酸钠缓冲溶液中,痕量锑(Ⅲ)与APDC生成络合物,加入表面活性剂TritonX-114用浊点萃取分离富集样品中痕量锑。分取部分表面活性剂相用0.1mol·L-1硝酸甲醇溶液溶解,所得溶液直接用石墨炉原子吸收光谱法进行测定。对影响浊点萃取的因素和共存离子的干扰等进行了试验并予以优化。方法的检出限(3σ/k)为0.37μg.L-1。应用所提出的方法测定了食品包装材料陶瓷样品中锑的含量,并用标准加入法进行方法的回收试验,测得回收率为99.3%。     

浊点萃取-石墨炉原子吸收光谱法测定环境样品中的镉

建立了浊点萃取分离富集石墨炉原子吸收光谱法测定环境样品中痕量镉的方法.浊点萃取选择8-羟基喹啉为螯合剂,Triton X-100为表面活性剂.在pH 8～9、0.01%8-羟基喹啉和0.2%-Triton X-100、80 ℃水浴20 min的优化条件下,所建立方法的检出限为2.5 ng/L; 加标回收率为94.6%～106.2%; 对样品溶液进行富集的富集因子为17.利用该方法分别测定了2个实际水样和2个国家标准参考物质中的总镉含量,结果令人满意.     

浊点萃取-石墨炉原子吸收光谱法测定痕量钯

建立了浊点萃取-石墨炉原子吸收光谱法(GFAAS)测定痕量金属钯的新方法,利用表面活性剂Triton X-114和络合剂2-(5-溴-2-吡啶偶氮)-5-二甲氨基苯胺(5-Br-PADMA)对钯进行浊点萃取。研究了溶液pH、试剂浓度、平衡温度和加热时间等因素对浊点萃取及测定灵敏度的影响。优化条件为:pH 5.50 HAc-NaAc缓冲,0.08 mL 5×10-4 mol/L 5-Br-PADMA,0.70 mL10g/L Triton X-114。在最佳条件下,方法的线性范围为0.1～10 ng/mL,钯的检出限为0.068 ng/mL,富集倍率为45倍。该方法可用于环境样品中痕量钯的富集和测定,结果令人满意。     

正交设计优化浊点萃取-石墨炉原子吸收光谱法测定环境水样中痕量Cd(Ⅱ)

建立了浊点萃取-石墨炉原子吸收光谱法测定环境水样中痕量Cd(Ⅱ)的方法。Cd(Ⅱ)可与8-羟基喹啉生成螯合物,通过水浴加热,螯合物被萃取到Triton X-45表面活性剂相,经离心与水相分离。在单因素基础上,采用L27(313)正交试验方法优化浊点萃取条件,详细探讨了溶液pH、试剂加入量、水浴温度和时间等实验条件对浊点萃取的影响。在最优条件下,Cd(Ⅱ)在0.05~0.50μg/L范围与吸光度有良好的线性关系,方法检出限为1.7ng/L,相对标准偏差为0.54%(n=6),加标回收率为96.2%~101.5%,对于10mL样品溶液其富集倍数为18.4。建立的方法可用于环境水样中痕量Cd(Ⅱ)的测定。     

浊点萃取-石墨炉原子吸收光谱法同时测定生物样品中痕量铅和镉

提出了石墨炉原子吸收光谱法同时测定小鼠肝中痕量Pb和Cd的方法。以8-羟基喹啉为络合剂,在pH 9.0时,用Triton X-100浊点萃取富集样品中的Pb和Cd。用NH4H2PO4作为基体改进剂测定Pb和Cd,Pb和Cd的检出限(3s/k)分别为0.103μg/L和0.0136μg/L,相对标准差(n=6)分别为1.4%,0.73%。对于10 mL样品溶液的富集倍数分别为7.1,9.3。利用该法分别测定了小鼠肝中的Pb和Cd的含量,加标回收率分别为96.4%～97.1%和101.3%～103.2%。     

浊点萃取富集-石墨炉原子吸收光谱法同时测定环境水样和中药中超痕量铅和镉

提出了石墨炉原子吸收光谱法同时测定环境水样和中药中超痕量铅与镉的方法.以双硫腙为络合剂,在pH 7.0时,用Triton X-114非离子表面活性剂浊点萃取富集样品溶液中痕量铅和镉.用硝酸镁和磷酸二氢铵的混合液作为基体改进剂测定铅和镉,铅和镉的检出限(3s/k)分别为0.138,0.007μg·L-1,相对标准偏差(n=7)分别为1.90%,2.08%.对于10 mL样品溶液的富集倍数分别为18.3,17.7.应用所提出的方法测定了杨树叶(GBW 07604)和小麦粉(GBW08503)国家标准样品,测定结果与标准值相符.铅和镉的加标回收率分别为97.8%,94.0%(水样);98.0%,94.0%(中药样).     

浊点萃取-火焰原子吸收光谱法测定痕量铜

2-磺酸基-4-甲氧基苯基重氮氨基偶氮苯(MOSDAA)和Cu(II)反应生成疏水性络合物后,被萃取到Triton X-114非离子表面活性剂胶束相中,火焰原子吸收光谱法测定其中的铜,建立了浊点萃取预富集-火焰原子吸收光谱法测定铜的方法。反应体系的pH、MOSDAA和Triton X-114的浓度、平衡温度及时间等实验条件被优化。在选择的实验条件下,方法的检出限为1.1 ng/mL(3σ),对浓度为0.1μg/mL的Cu(II)溶液平行测定6次,相对标准偏差为1.9%。方法已用于小米和水样中痕量铜的测定。     

浊点萃取-火焰原子吸收光谱法测定水样中痕量铜的研究

提出了浊点萃取火焰原子吸收光谱法测定痕量铜的新方法。详细探讨了溶液pH，试剂浓度等实验条件对浊点萃取及测定灵敏度的影响，在最佳下，富集50mL样品溶液，用火焰原子吸收光谱法测定，铜的检测限为0.35μg/L，铜的富集倍率为71倍。方法用于自来水、河水及海水中痕量铜的测定。     

浊点萃取电热原子吸收光谱法测定水中痕量铊

采用吡咯烷基二硫代氨基甲酸铵(APDC)为螯合剂,Triton X-114作为表面活性剂,建立了浊点萃取预富集电热原子吸收光谱法测定水中痕量铊的方法。在优化的实验条件下,方法的检出限可达0.07μg/L,相对标准偏差为3.6%(4μg/L,n=7),加标回收率为93%~106%,富集倍率为31。该方法成功应用于自来水和河水中痕量铊的测定。     

Determination of trace vanadium in sea cucumbers by ultrasound-assisted cloud point extraction and graphite furnace atomic absorption spectrometry

An ultrasound-assisted cloud point extraction (CPE) procedure was used for preconcentration and determination of vanadium by graphite furnace atomic absorption spectrometry. The vanadyl(IV) complex with ascorbic acid form a hydrophobic complex with 4-(2-pyridylazo) resorcinol (PAR) in a micelle medium, which is stable under our working conditions, and followed by its extraction into Triton X-100 surfactant-rich phase. The main factors affecting CPE efficiency, such as pH, concentrations of PAR, ascorbic acid and Triton X-100, incubation temperature, frequency and equilibration time of ultrasonic bath were investigated in detail. Under the optimum conditions, preconcentration of 10 mL sample gave a preconcentration factor of 36.4 and a detection limit of 4.0 µg kg^?1. The proposed method was successfully applied to determination of vanadium in sea cucumbers with satisfactory results.     

Determination of lead in water samples by graphite furnace atomic absorption spectrometry after cloud point extraction

Cloud point extraction (CPE) has been used for the pre-concentration of lead, after the formation of a complex with 2-(5-bromo-2-pyridylazo)-5-(diethylamino)-phenol (5-Br-PADAP), and later analysis by graphite furnace atomic absorption spectrometry (GFAAS) using octylphenoxypolyethoxyethanol (TritonX-114) as surfactant. The chemical variables affecting the separation phase were optimized. Separation of the two phases was accomplished by centrifugation for 15 min at 4000 rpm. Under the optimum conditions i.e., pH 8.0, cloud point temperature 40 °C, [5-Br-PADAP] = 2.5 × 10⁻⁵ mol l⁻¹, [Triton X-114] = 0.05%, added methanol volume = 0.15 ml, pre-concentration of only 10 ml sample permitted an enhancement factor of 50-fold. The lower limit of detection (LOD) obtained under the optimal conditions was 0.08 μg l⁻¹. The precision for 10 replicate determinations at 5 μg l⁻¹ Pb was 2.8% relative standard deviation (R.S.D.). The calibration graph using the pre-concentration system for lead was linear with a correlation coefficient of 0.9984 at levels near the detection limits up to at least 30 μg l⁻¹. The method was successfully applied to the determination of lead in water samples.     

Determination of ultra trace arsenic species in water samples by hydride generation atomic absorption spectrometry after cloud point extraction

Cloud point extraction (CPE) methodology has successfully been employed for the preconcentration of ultra-trace arsenic species in aqueous samples prior to hydride generation atomic absorption spectrometry (HGAAS). As(III) has formed an ion-pairing complex with Pyronine B in presence of sodium dodecyl sulfate (SDS) at pH 10.0 and extracted into the non-ionic surfactant, polyethylene glycol tert-octylphenyl ether (Triton X-114). After phase separation, the surfactant-rich phase was diluted with 2 mL of 1 M HCl and 0.5 mL of 3.0% (w/v) Antifoam A. Under the optimized conditions, a preconcentration factor of 60 and a detection limit of 0.008 μg L⁻¹ with a correlation coefficient of 0.9918 was obtained with a calibration curve in the range of 0.03–4.00 μg L⁻¹. The proposed preconcentration procedure was successfully applied to the determination of As(III) ions in certified standard water samples (TMDA-53.3 and NIST 1643e, a low level fortified standard for trace elements) and some real samples including natural drinking water and tap water samples.     

石墨炉原子吸收法测定石脑油中微量砷

试样用四氢呋喃（THF）有机溶剂稀释,以硝酸镍为基体改进剂,研究采用石墨炉原子吸收法直接进样测定石脑油中的砷量。研究表明,砷量在0～50μg／L范围内线性关系良好,回收率93％～104％。     

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

Cloud point extraction (CPE) has been used for the simultaneous pre-concentration of cadmium, copper, lead and zinc after the formation of a complex with 1-(2-thiazolylazo)-2-naphthol (TAN), and later analysis by flame atomic absorption spectrometry (FAAS) using octylphenoxypolyethoxyethanol (Triton X-114) as surfactant. The chemical variables affecting the separation phase and the viscosity affecting the detection process were optimized. At pH 8.6, pre-concentration of only 50 ml of sample in the presence of 0.05% Triton X-114 and 2×10⁻⁵ mol l⁻¹ TAN permitted the detection of 0.099, 0.27, 1.1 and 0.095 ng ml⁻¹ cadmium, copper, lead and zinc, respectively. The enhancement factors were 57.7, 64.3, 55.6 and 63.7 for cadmium, copper, lead and zinc, respectively. The proposed method has been applied to the determination of cadmium, copper, lead and zinc in water samples and a standard reference material (SRM).     

Determination of ultra trace amounts of bismuth in biological and water samples by electrothermal atomic absorption spectrometry (ET-AAS) after cloud point extraction

A new approach for a cloud point extraction electrothermal atomic absorption spectrometric method was used for determining bismuth. The aqueous analyte was acidified with sulfuric acid (pH 3.0-3.5). Triton X-114 was added as a surfactant and dithizone was used as a complexing agent.After phase separation at 50 °C based on the cloud point separation of the mixture, the surfactant-rich phase was diluted using tetrahydrofuran (THF). Twenty microliters of the enriched solution and 10 μl of 0.1% (w/v) Pd(NO₃)₂ as chemical modifier were dispersed into the graphite tube and the analyte determined by electrothermal atomic absorption spectrometry. After optimizing extraction conditions and instrumental parameters, a preconcentration factor of 196 was obtained for a sample of only 10 ml. The detection limit was 0.02 ng ml⁻¹ and the analytical curve was linear for the concentration range of 0.04-0.60 ng ml⁻¹. Relative standard deviations were <5%.The method was successfully applied for the extraction and determination of bismuth in tap water and biological samples (urine and hair).     

石墨炉原子吸收光谱法测定茶叶中的铅

采用石墨炉原子吸收光谱法测定茶叶中铅,以NH4H2PO4作为基体改进剂,提高了测定的灰化温度,消除了基体干扰.方法简便,快速,准确度高.通过对标准物质的多次测定,结果均在其保证值范围内,相对标准偏差为2.8%.对样品进行加标回收试验,回收率为96%～105%,方法检出限为0.12μg/L.     

石墨炉原子吸收法测定3-苯基丙烯酸酯类化合物中微量钯

利用高灵敏的石墨炉原子吸收法,在V(HCl):V(HNO3):V(H2O)＝5:1:94混合酸介质中测定苯基丙烯酸酯类化合物中的钯量.已纯化样品钯量的平均值是6.76 μg/g,标准相对偏差是4.8%,平均回收率为99.3%;未纯化样品钯量的平均值是121.2 μg/g,平均相对偏差是5.4%.还讨论酸介质对测定钯吸光度的影响,通过比较找到了合适的酸介质组成.