共查询到15条相似文献,搜索用时 78 毫秒
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HPLC-ICP-MS法分析太湖沉积物中砷的形态及分布特征 总被引:3,自引:0,他引:3
以0.3 mol/L磷酸和0.1 mol/L抗坏血酸为提取试剂,对沉积物样品进行微波萃取。以2.0 mmol/L NaH2PO4/0.2 mmol/L EDTA(pH 6.0)为流动相,采用高效液相色谱-电感耦合等离子体质谱(HPLC-ICP-MS)联用技术测定萃取液中As(Ⅲ)、As(Ⅴ)、MMA和DMA的含量。4种形态砷的色谱峰在10 min内可以得到完全分离,标准曲线线性良好,样品的加标回收率范围为94.2%~110%,样品中砷形态的提取效率为80.4%~98.7%。研究表明,太湖表层沉积物中的砷主要为无机形态,未检出有机砷形态,As(Ⅴ)形态的含量高于As(Ⅲ),说明太湖表层沉积物基本上处于氧化性沉积环境中。近20年来,太湖湖底沉积物中砷的含量有了显著增加。检测的沉积剖面沉积物中砷的形态亦为无机形态,各沉积剖面沉积物中砷形态的相对比例没有显著差异。 相似文献
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王水(1+1)体系——双道原子荧光光度计同方法、同步测定土壤中的砷、汞 总被引:1,自引:0,他引:1
通过对王水(1+1)消解土壤方法的优化,利用双道原子荧光光度计的双道检测优势,优化仪器条件,同方法、同步测定土壤中的砷和汞。结果表明:王水(1+1)消解方法的优化可实现土壤中砷、汞的同步测定,这个方法是简便、快速、准确和精确的,提高了土壤中砷和汞的检测速度。 相似文献
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总砷超标食用菌样品中砷形态分布研究 总被引:1,自引:0,他引:1
目的:研究总砷超标食用菌样品中砷的形态分布,对食用菌中总砷含量与食用安全性的关系及其限量规定进行探讨。方法:从2010年深圳口岸进出口食用菌批量监测的各种食用菌样品中选择总砷超标的几类样品,采用液相色谱-氢化物发生-原子荧光光谱联用技术(LC-HGAFS)分析了不同种类食用菌样品中的砷形态,准确测定了总无机砷与总砷含量。结果:形态分析方法能够准确定性定量食用菌中的总无机砷含量,而食用菌中总砷含量和总无机砷含量并不存在对应关系。干香菇中总砷和总无机砷含量均较高,食用安全风险较高;而蘑菇中总砷含量高,但总无机砷含量却很低,主要以一甲基砷等无毒砷形态存在,可以放心食用。结论:食用菌中砷形态分布测定能更科学地体现砷超标和食用安全性的关系。我国现行食用菌卫生标准仅规定了总砷限量指标,建议对该标准进行修订。 相似文献
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通过与无机砷的2种国标提取方法的实验对比,建立高效、快速的微波辅助提取稻米中无机砷的方法,以0.3mol/L盐酸为提取剂,在60℃、固液比1:20的条件下微波加热提取15min,并用1%的L-半胱氨酸完成对As(V)的预还原。方法回收率为As(Ⅲ):94%~108%、As(V):92%~101%,精密度为2.94%,检出限为0.086μg/L,可准确用于稻米中有毒无机砷的定量检测和风险评估。 相似文献
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目的:建立使用L-半胱氨酸作为还原剂,氢化物-原子荧光光谱法测定肉及肉制品中无机砷的方法。方法:样品以6mol/L盐酸提取无机砷,样液用L-半胱氨酸作为还原剂,应用氢化物发生-原子荧光分析技术测定肉及肉制品中总无机砷。结果:方法的线性范围在0~30μg/L,相关系数r=0.9999(n=6),回归方程Y=51.7977X-7.7185,检出限为0.11μg/L,样品的相对标准偏差(RSD)为1.4%~3.5%,加标回收率为91.2%~93.7%。 相似文献
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采用几种常见浸提方法对砷污染土壤和蜈蚣草样品进行处理,并使用LC-AFS测定砷形态,重点考察不同浸提方法对样品砷浸提效果的差异,以及其形态分布特征。结果表明:土壤和蜈蚣草中砷主要以As(Ⅲ)和As(Ⅴ)的无机形态存在。土壤、蜈蚣草根和蜈蚣草叶中As(Ⅲ)所占比例分别为11.6%,24.2%和73.8%。磷酸150℃高温浸提对土壤的浸提效率最高,可达41.0%;甲醇/水(1:9)超声浸提对蜈蚣草根和叶有最高的浸提效率,分别为60.2%和82.5%。样品加标回收率和相对标准偏差分别在92.7%~108.4%和2.05%~10.49%范围内。 相似文献
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Heavy metals are largely responsible for soil and water pollution. Recently, phytoremediation is receiving a large attention as a plant-based technology for removing metals from contaminated soil and water in an environment-friendly and cost-effective way. In such context, some species of ferns such as Pteris cretica were found to be a hyper-accumulator of arsenic (As). In this study, we first explored the validity of measuring the water-refilling process in xylem vessels of Pteris cretica using the synchrotron X-ray microimaging technique. Then we investigated the effects of arsenic concentration on the water-refilling speed inside the xylem vessel. The methodology to measure the water-refilling speed was consistent within five repetitions and 3 hours after the stem sample was cut from the plant. The water-refilling speed in the xylem vessels of the Pteris grown in arsenic solution was faster than that in normal water. Arsenic concentration of 0-1,000 μM was tested and the maximum speed was obtained at 500 μM. Conclusively, the experimental methodology developed in this study allowed to obtain some interesting results for understanding how arsenic affect the xylem sap flow transport and the mechanism by which growth is enhanced in the presence of heavy metal. 相似文献
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R. D. Preston 《Journal of microscopy》1971,93(1):7-13
Reason is given for the belief that an overlapping of images ensures a gross underestimate of cellulose microfibril width in plant cell walls observed both in section and negatively stained. Both theory and optical simulation of the electron-microscope situation suggest that the error involves a factor of at least two or three times. These, and other considerations render doubtful the existence of elementary microfibrils as components of the broad (c. 20 nm) microfibrils of some seaweeds. 相似文献
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BaoweiChen WilliamCullen MeilingLu XiufenLu AnthonyMcKnight-Whitford ShengwenShen ZhongwenWang MichaelWeinfeld HuimingYan ChungangYuan X.ChrisLe 《质谱学报》2010,31(Z1):22-22
Arsenic is one of the most important environmental agents in causing chronic human disease. Elevated levels of arsenic in drinking water may affect >100 million people around the world. A wide variety of adverse health effects, most seriously, cancers of bladder, lung, urinary tract, and skin, have been attributed to chronic exposure to arsenic. However, the biochemical mechanisms responsible for these effects caused by arsenic remain unclear, but may be mediated by the binding of trivalent arsenicals to thiol groups in proteins, thereby changing the conformation of these proteins and inhibiting their functions. If some of the affected proteins are responsible for cellular repair of DNA damage, for example, the inhibition of these proteins could lead to carcinogenesis. To study interaction of arsenic with proteins, we have developed an affinity selection technique, coupled with mass spectrometry, to select and identify specific arsenic-binding proteins from a large pool of cellular proteins. Controlled experiments using proteins either containing free cysteine(s) or inactive cysteine showed that the arsenic affinity column specifically captured the proteins containing free cysteine(s) available to bind to arsenic. The technique was able to capture and identify trace amounts of bovine biliverdin reductase B present as a minor impurity in the commercial preparation of carbonic anhydrase II, demonstrating the ability to identify arsenic-binding proteins in the presence of a large excess of non-specific proteins. Application of the technique to the analysis of subcellular fractions of A549 human lung carcinoma cells identified 50 proteins in the nuclear fraction, and 24 proteins in the membrane/organelle fraction that could bind to arsenic. This added substantially to the current list of only a few known arsenic-binding proteins. A number of arsenic-binding proteins identified using the affinity chromatography tandem mass spectrometry approach were of particular interest because of their important biological functions. For example, DNA-dependent protein kinase, ATP-dependent helicase II (Ku70), and topoisomerase 2 alpha, are involved in DNA repair and maintaining genome stability. Several other proteins modulate the redox status of cells, e.g. peroxiredoxin-1 and thioredoxin, and apoptosis, e.g., lamin A and heat shock cognate protein. This work shows that arsenic can bind to these proteins in cell extracts. How arsenic affects the function of these proteins in biological systems will have to be confirmed by studying arsenic interaction with proteins in living cells. 相似文献