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171.
掺氧空气-乙炔火焰原子吸收光谱法测定地质样品中痕量镱 总被引:1,自引:0,他引:1
提出掺氧空气-乙炔火焰原子吸收光谱法测定地质样品中痕量镱的新方法。使用磺基水杨酸作保护剂消除铝对镱的挥发原子化干扰,KC1作消电离剂消除镱的电离干扰。方法的检出限为0.0042mg·L-1。应用于测定地质标准样品中痕量镱,结果与标准值相符,对GBW07302试样测定8次,RSD为5.41%。 相似文献
172.
Removal of humic matter interference in the determination of Cr(VI) in soil extracts by the diphenylcarbazide method 总被引:1,自引:0,他引:1
Alkaline digestion of soil samples, which is recommended for minimizing Cr(III)–Cr(VI) interconversions during the extraction of Cr(VI), may also solubilize humic matter (HM). The latter is responsible for both positive and negative interference in the analysis of Cr(VI) in the extract by the diphenylcarbazide (DPC) method. Humic compounds indeed absorb light at 540 nm as the Cr-DPC product and are also able to rapidly reduce Cr(VI) under the pH conditions of the standard DPC method. To prevent any risk of interference and make the DPC method applicable to soil extracts, a new protocol is proposed. This consists of three successive steps: (1) extraction of Cr(VI) by the U.S.EPA method 3060A in the presence of Mg2+; (2) batch removal of solubilised HM by the XAD-7 sorbent at pH 3.0 ± 0.1 with 3–5 min contact time; (3) analysis of Cr(VI) with the DPC method at pH 3.0 ± 0.1. The application of this new protocol to the soil product SQC-012 Lot 4 certified by R.T. Corporation (RTC, USA) gave significantly lower Cr(VI) concentrations and smaller variability compared to certified values (46.5 ± 2.3 instead of 153 ± 32.6 mg/kg). The new protocol was validated by Cr(VI) and Cr(III) spikes either to the soil/extractant suspension or to the exctract. Cr(VI) results in the wide range of acceptance limits (104–202 mg/kg) reported by RTC were only obtained when the U.S.EPA method 3060A without the addition of Mg2+ and DPC analysis at pH 1.0 were applied. The latter procedure appears questionable since it leads to largely variable results which reflect the complex role played by humic matter in the determination of Cr(VI) and the instability of Cr(III) during the extraction. 相似文献
173.
土壤重金属生物有效性的评价方法 总被引:10,自引:0,他引:10
土壤重金属污染已成为人们广泛关注的全球性的环境问题之一。重金属生物有效性已成为污染生态学研究的前沿。对国内外土壤重金属生物有效性评价方法的研究进展作了简要综述,并对今后的研究作了展望。 相似文献
174.
马景治 《中国无机分析化学》2018,8(6):42-45
采用粉末压片制样,利用岛津1800型X 射线荧光光谱分析仪,对石灰石、白云石等灰岩类标准物质拟合校准曲线,建立了 X 射线荧光光谱法(XRF)同时测定石灰石、白云石样品中主次量组分(SiO2、Al2O3、TFe2O3、MgO、CaO、K2O、Na2O、MnO、P)的快速分析方法。通过试验确定了样品粒度要达到74μm以下,30t压力下制片。通过灼烧减量对SiO2、Al2O3、TFe2O3、MgO、CaO 含量进行校正,根据其含量与强度的对应关系绘制校准曲线,采用经验系数法可减小元素间的增强-吸收效应。对灰岩类试样进行精密度考察,各组分含量的相对标准偏差 RSD<2%;对石灰石和白云石标准样品和实际样品进行准确度考察,测定值与标准推荐值或传统方法的测定值一致。 相似文献
175.
建立了一种采用超声辅助提取(UAE)、强阴离子交换固相萃取(SAX-SPE)净化、高效液相色谱(HPLC)测定土壤中残留头孢菌素C(CPC)简单、快速方法。 样品以超纯水为提取剂,超声辅助提取,SPE柱子以3 mL甲醇和3 mL水活化,采用5 mL的10%甲醇水溶液作为淋洗液,2 mL的5%甲酸水溶液/甲醇溶液(体积比50:50)进行洗脱,高效液相色谱紫外检测器(HPLC-PDA)测定,检测波长λ=254 nm,柱温30 ℃ ,流动相为0.1%甲酸水溶液/甲醇溶液(体积比95:5)对土壤中不同加标浓度的CPC进行检测,方法的回收率在77.9%~98.9%,标准偏差范围为5.0%~6.3%(n=5),方法检出限(LOD)为340.4 μg/kg,定量限(LOQ)为1126.8 μg/kg。 同时采用此方法检测分析新疆某药厂附近阳性土壤样品,不同批次土壤样品结果分别为:检出(低于定量限)、1532.1 μg/kg。 相似文献
176.
177.
Microextraction-based sample preparation techniques have exhibited remarkable importance in analytical chemistry since they were first developed in the 1980s. The application of these techniques involves efficient and, at the same time, environmentally-friendly analytical methodologies. They are also generally faster when compared with classical sample preparation techniques, requiring low solvent and sample volumes, and also allowing for automated or semi-automated procedures. This paper provides an overview of the basic principles of sample preparation techniques and the important applications and developments that have taken place in this area over the past five years. These procedures include solid-phase microextraction (SPME), stir bar sorptive extraction (SBSE), bar adsorptive microextraction (BAμE), rotating disk sorptive extraction (RDSE), micro solid-phase extraction (μ-SPE) and liquid-phase microextraction (LPME). The main variations are discussed with a focus on recent applications in the analysis of environmental water samples. Lastly, some of the trends and perspectives associated with these outstanding microextraction sample preparation approaches are highlighted. 相似文献
178.
The advent of multiple collector–inductively coupled plasma–mass spectrometry (MC-ICP-MS) has made the high-precision determination of Ge isotopes possible, which leads to the widespread application of Ge isotopes in earth, ocean, and cosmochemistry fields. This paper reviews the history of Ge isotope analysis, chemical dissolution and purification, and mass spectrometry measurements. Concentrated HNO3 is sufficient to dissolve nearly all types of samples and HF is also involved for Si-rich samples. Low-temperature ashing prior to dissolution is an alternative way to preconcentrate Ge in organic-rich samples. For different matrices, Ge isotopes can be determined by MC-ICP-MS coupled with a traditional nebulizer system or hydride generation system after two-step separation, one step cation/anion-exchange separation, or Mg/Fe co-precipitation protocols. Ion-exchange column methods are suitable for samples with elevated matrix and Ge content such as sulfides, iron oxides, silicate rocks, and coals, whereas Mg or Fe coprecipitation methods are particularly suitable for all kinds of water. Hydride generation systems are improved over traditional nebulizer system due to the smaller sample quantity and fewer matrix-related interferences. Sample-standard bracketing, double spike, and external Ga isotope normalization are used to mass bias correction and yield consistent results. Analytical methods involving Ge-poor samples and Ge isotope analyses based on different Ge species or specific Ge compound in natural environment will be important prospects in the further study. For further applications of Ge isotopes in mineral deposits such as sulfide and iron oxide deposits, sulfides, and iron oxides reference materials should be developed in the future. 相似文献
179.
《Electroanalysis》2018,30(8):1734-1739
The present study describes a novel electrochemical aptasensor for detection of carcinoembryonic antigen (CEA), a key cancer biomarker. The sensing strategy relied on the CEA‐induced bridge assembly, as a physical barrier, on the surface of gold electrode, resulting in a significant increase of the sensor sensitivity. Under optimal conditions, the aptasensing platform showed a wide linear range (3 pg/mL to 40 ng/mL) and a low detection limit (0.9 pg/mL). Some possible interfering materials were also assessed and the results indicated that the designed aptasensor had good specificity toward CEA. The quantitation of CEA in the spiked human serum samples confirmed the reliability and applicability of the electrochemical aptasensor. So, the developed sensing method has a potential application in the clinical diagnosis. 相似文献
180.
《Electroanalysis》2018,30(8):1870-1879
A portable electroanalytical system applied for rapid and simultaneous determination of uric acid (UA) and nitrite (NIT) in human biological fluids (urine, saliva and blood) is reported. The system is based on batch‐injection analysis with multiple‐pulse amperometric (BIA‐MPA) detection using screen‐printed electrodes (SPEs) modified with multi‐walled carbon nanotubes. Sample dilution in optimized electrolyte (0.1 mol L−1 Britton‐Robinson buffer pH 2) followed by injection of 100 μL on the electrode surface using an electronic micropipette is performed. UA is detected at +0.45 V and both UA+NIT at +0.70 V. Linear calibration plots for UA and NIT were obtained over the range of 1–500 μmol L−1 with detection limits of 0.05 and 0.06 μmol L−1, respectively. For comparison, a differential‐pulse voltammetric (DPV) method was optimized, and linear calibration plots for UA and NIT were obtained over range of 1–30 μmol L−1 and 1–40 μmol L−1 with detection limits of 0.1 and 0.3 μmol L−1, respectively. BIA‐MPA is highly precise (RSD<1.3 %), fast (160 h−1) and free from sample‐matrix interferences as recovery values ranged from 77 to 121 % for spiked samples (short contact time of sample aliquot with SPE). Contrarily, recovery tests conducted using DPV did not provide adequate recovery values (>150 %), probably due to the longer contact time of the SPE with the biological samples during analysis leading to a severe interference of sample matrices. 相似文献