原子吸收光谱法测定丹参及其近缘种中痕量元素

丹参及其近缘种样品用硝酸-高氯酸混合酸(体积比4比1)浸泡过夜,加热消解.在优化的仪器工作条件下,用火焰原子吸收光谱法测定所制得样品溶液中钙、镁、铁、锰、铜和锌的含量,并用石墨炉原子吸收光谱法(GFAAS)测定其中的钼、铅、铬及镉的含量.测定铅及镉时,用磷酸二氢铵作基体改进剂,而测定铬时,用抗坏血酸作基体改进剂.10种元素的检出限(3S/N)均小于0.26μg·g-1,测定钙、镁、铁、锰、铜和锌时,测得其回收率在99.0%～103.6%之间,其相对标准偏差(n=5)在0.54%～1.77%之间;测定钼、铅、铬和镉时,其回收率在100.O%～108.0%之间,相对标准偏差(n=5)在0.02%～1.9%之间.     

电感耦合等离子体原子发射光谱法测定枸杞中11种元素含量

采用电感耦合等离子体原子发射光谱法测定了枸杞中锌、铅、锰、铁、铬、镁、钙、铜、钠、钾和镉11种元素含量。选择硝酸(2+98)溶液作为介质,选择波长为213.86,220.35,257.61,259.94,267.72,279.08,324.75,317.93,589.59,766.49,226.50 nm 11条谱线依次作为测定锌、铅、锰、铁、铬、镁、钙、铜、钠、钾和镉的分析线,测得11种元素的检出限(3δ)均低于0.07 mg·L~(-1),相对标准偏差(n=11)在0.72%～2.40%之间。比较了常规湿法消化法、高压消化罐法和微波消解法处理样品对测定结果的影响。研究表明,高压消化罐法和微波消解处理样品精密度好。     

高压密闭消解-原子吸收光度法同时测定土壤中的铜、锌、铅、镉、镍、铬

采用高压密闭消解-原子吸收光度法同时测定土壤中铜、锌、铅、镉、镍、铬6种重金属元素。通过剖析不同消解体系,选择了最佳消解条件和测定条件。测定土壤中各元素的回收率均在86%～110%之间,相对标准偏差均小于8.0%(n=6)。     

电感耦合等离子体质谱法测定原油中微量元素

原油样品用硝酸和过氧化氢经高压密闭消解罐消解处理,采用电感耦合等离子体质谱法测定其中镁、铝、钒、铬、镍、铜、锌、钼、镉和铅等10种微量元素的含量。10种元素的检出限(3s)在0.012～0.300μg·g~(-1)之间。方法用于S-21油标准样品分析,测定值与认定值相吻合,相对标准偏差(n=5)在0.5%～5.0%之间。10种元素的回收率在93.3%～116.0%之间。     

电感耦合等离子体原子发射光谱(ICP-AES)法和电感耦合等离子体质谱(ICP-MS)法测定大气降尘中的铅、镉、铬、锌、锰、镍、铜、铊

大气中Pb、Cd、Cr、Mn、Ni、Tl等重金属污染物是目前国内外城市大气污染的主要因子之一,研究大气降尘中重金属元素含量具有重大意义。本文采用盐酸-硝酸混合酸为消解体系,在105℃条件下用电热板消解回流大气降尘样品2小时后定容测定,通过电感耦合等离子发射光谱法仪(ICP-AES)和电感耦合等离子体质谱仪(ICP-MS)测定大气降尘中铅、镉、铬、锌、锰、镍、铜和铊等8种重金属元素。测定结果表明： ICP-AES(铅、镉、铬、锌、锰、镍、铜)和ICP-MS(铊)两种方法的曲线线性好,准确度高,测定范围宽,检出限在0.024mg/kg-0.548mg/kg之间,精密度在0.15%-2.38%之间,能准确测定大气降尘中的重金属元素含量。     

火焰原子吸收光谱法测定土壤中金属元素

土壤样品用硝酸-氢氟酸-高氯酸(5+5+3)混合酸消解后,采用火焰原子吸收光谱法分别测定了试样溶液中铁、锰、铜、锌、铅、镉和镍的含量。因消解过程中加入了氢氟酸,大部分硅生成四氟化硅气体除去,可在此溶液中直接测定其中铁、锰、铜、锌及镍的量。考虑到SiO_3~(2-)、Ti(Ⅳ)及Al~(3+)对锰测定有负干扰,加入一定量的氯化钙溶液作为释放剂消除其干扰。如试样含铁量较高,须加入硝酸镧溶液作释放剂以克服其对锌测定的干扰。测定铅及镉时须加入碘化钾溶液使之生成碘化物络阴离子后,用4-甲基-2-戊酮作溶剂进行萃取分离,随后在有机相中测定铅与镉的含量。用7种元素的标准溶液制作了各自的标准曲线,所得线性回归方程的相关系数在0.999 2～0.9996之间。以土壤样品为基体,加入一定量7种元素的标准溶液做回收试验,得到回收率在96.8%～99.9%之间,相对标准偏差(n=6)在0.9%～2.0%之间。     

微波消解-ICP-MS测定电镀污泥中的重金属

采用微波消解系统对某电镀污泥进行消解,利用ICP-MS对污泥中的重金属进行测定。称取制备后样品,置于消解罐中充分反应后,赶酸、定容后利用电感耦合等离子体质谱法进行测定。电镀污泥中的铬为18845.2mg/kg、镉为10.3mg/kg、镍为5200.0mg/kg、铅为189.7mg/kg、铜为3271.7mg/kg、锌为49632.6mg/kg。测定结果表明所检测项目工作曲线线性关系好,相关系数r均大于0.999。铬加标回收率在91.6～97.7%之间、镉加标回收率在92.0～97.0%之间、镍加标回收率在95.1～98.0%之间、铅加标回收率在94.3～95.2%之间、铜加标回收率在97.1～102%之间、锌加标回收率在96.3～98.7%之间,均满足相关测定要求。计算的潜在生态危害系数、潜在生态危害指数结果表明,电镀污泥中的铬、镉、铅、铜、锌为轻微生态危害,镍为强生态危害;潜在生态危害指数RI计算值为216.69,属于中等生态危害。     

电感耦合等离子体原子发射光谱法测定龋齿牙釉质和牙本质中微量元素

牙齿样品经硝酸-高氯酸体系消解,应用电感耦合等离子体原子发射光谱法(ICP-AES)测定龋齿和健康齿的牙釉质与牙本质中锌、铁、铜、锶、镁、铬、铝和铅等微量元素的含量。在优化的试验条件下,各元素的测定下限(10S/N)均为0.03 mg.L-1,回收率在96.3%～114.0%之间。探讨龋病的牙釉质和牙本质与这些微量元素的关系,试验结果表明:锌、铁、铜和锶在健康齿组牙釉质和牙本质中的含量均高于龋齿组中的含量,而镁、铬、铝和铅的含量则均明显低于龋齿组中含量,说明牙齿中的微量元素是指示龋病的一种因子。     

原子吸收法测定污泥蚯蚓中的镉、铜、铬、锌、铅

研究用原子吸收法测定蚯蚓中的镉、铜、铬、锌、铅.将制备成粉状的蚯蚓用硝酸-高氯酸消解,在仪器工作条件下,金属离子含量与吸光度呈良好的线性关系.测定结果的相时标准偏差为1.3%～3.5%(n=7),加标回收率为93%～107%.测定镉、铜、铬、锌、铅离子的线性范围、线性相关系数、检出限依次为0～0.9 mg/L,r=0.9984,0.0r7 mg/L;0～10 mg/L,r=0.9989,0.05 mg/L;0～5 mg/L,r=0.999 1,0.13mg/L;0～0.7 mg/L,r=0.9997,0.02 mg/L;0～7.5 mg/L,r=0.9994,0.3 mg/L.     

毛细管电泳单脉冲伏安测定重金属铜铅锌镉

以毛细管为分离通道 ,在KNO3 缓冲溶液中 ,用表面镀汞膜的金微电极作为工作电极 ,采用单脉冲伏安法同时测定铜、锌、铅、镉含量 ,考察并优化了影响分离和检测的相关因素 :缓冲溶液pH、分离高压、脉冲上限和下限、脉冲宽度等。该法的最佳实验条件 :5mmol/LKNO3(pH6.0) ,分离高压20kV ,脉冲上限 -0.2V ,脉冲下限 -1.15V(vs.SCE) ,脉冲宽度500ms。结果表明 ,各峰面积与其离子浓度成线性关系 ,线性范围(μg/mL)分别为 :铜5.0×10-2～10.0;锌1.0×10-2～10.0 ;铅5.0×10-2～5.0 ;镉2.0×10-2～10.0。加标回收率在95%～110%之间。用该法较好地测定了水样中的重金属铜锌铅镉     

石墨炉原子吸收光谱法测定土壤中铅、镉含量

土壤样品经硝酸、氢氟酸和过氧化氢加热消解,采用石墨炉原子吸收光谱法测定其中铅和镉的含量。以磷酸铵作为基体改进剂,铅和镉的灰化温度分别为400℃,250℃,原子化温度分别为2 100℃,1 800℃。铅和镉的质量浓度分别在0.50～50.0,0.10～2.5μg.L-1范围内与其吸光度呈线性关系,检出限依次为6.5,0.4pg。应用此法分析了4个土壤标准样品,测定值与标准值相符,相对标准偏差(n=6)分别在1.5%～6.3%和2.3%～5.1%之间。铅、镉的加标回收率分别在85.4%～103.2%,91.5%～102.3%之间。     

反相高效液相色谱法同时测定镉、铅、铜和锌

 研究了meso-四（对羟基苯基）卟啉为柱前衍生化试剂与Cd2+,Pb2+,Cu2+和Zn2+离子的配合反应条件及配合物在C18色谱柱上的分离条件,建立了反相高效液相色谱快速分离光度检测Cd2+,Pb2+,Cu2+和Zn2+的新方法。配合物和试剂在15 min内出峰完毕。4种离子的检出限为: Cd2+0.02 ng,Pb2+0.02 ng, Cu2+0.02 ng,Zn2+0.12 ng;线性范围为:Cd2+0.8 μg/L～150 μg/L,Pb2+0.8 μg/L～300 μg/L,Cu2+0.8 μg/L～500 μg/L,Zn2+5.0 μg/L～1 000 μg/L;方法的日内相对标准偏差为:2.8%～4.8%,测定低、中、高3个浓度的日间相对标准偏差为3.7%～9.7%。     

Studies on transport phenomena in electrothermal vaporization sample introduction applied to inductively coupled plasma for optical emission and mass spectrometry

In the present work electrothermal vaporization (ETV) was used in both inductively coupled plasma mass spectrometry (ICP-MS) and optical emission spectrometry (OES) for sample introduction of solution samples. The effect of (Pd + Mg)-nitrate modifier and CaCl₂ matrix/modifier of variable amounts were studied on ETV-ICP-MS signals of Cr, Cu, Fe, Mn and Pb and on ETV-ICP-OES signals of Ag, Cd, Co, Cu, Fe, Ga, Mn and Zn. With the use of matrix-free standard solutions the analytical curves were bent to the signal axes (as expected from earlier studies), which was observed in the 20–800 pg mass range by ICP-MS and in the 1–50 ng mass range by ICP-OES detection. The degree of curvature was, however, different with the use of single element and multi-element standards. When applying the noted chemical modifiers (aerosol carriers) in microgram amounts, linear analytical curves were found in the nearly two orders of magnitude mass ranges. Changes of the CaCl₂ matrix concentration (loaded amount of 2–10 μg Ca) resulted in less than 5% changes in MS signals of 5 elements (each below 1 ng) and OES signals of 22 analytes (each below 15 ng). Exceptions were Pb (ICP-MS) and Cd (ICP-OES), where the sensitivity increase by Pd + Mg modifier was much larger compared to other elements studied. The general conclusions suggest that quantitative analysis with the use of ETV sample introduction requires matrix matching or matrix replacement by appropriate chemical modifier to the specific concentration ranges of analytes. This is a similar requirement to that claimed also by the most commonly used pneumatic nebulization of solutions, if samples with high matrix concentration are concerned.     

Principal component analysis: a chemometric aid for classification of polluted and unpolluted mussels

Ten trace elements (Al, Cr, Mn, Fe, Co, Ni, Cu, Zn, Cd and Pb) were determined in the dissolved ash of the edible part of wild mussels (28 samples) from a polluted site by electrothermal atomic absorption spectrometry. The distribution of the concentration of each element in the mussels was first investigated by means of a test of normality. The correlation matrix around the mean was used as a starting matrix for principal component analysis (PCA). Ten variables were reduced to two principal components, accounting for 77% of the total variance; Al, Cr, Mn, Fe, Zn, Cd and Pb are all positively associated with the first principal component and form a cluster of variables, indicating a common terrigenous origin. Comparison with 43 samples of unpolluted mussels from a nearby hatchery, on the basis of eight common variables (concentration of Mn, Fe, Co, Ni, Cu, Zn, Cd and Pb; 71 samples) by using a two-dimensional plot of PC scores, allows the mussels from the two sites to be differentiated.     

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.     

Trace metal accumulation in tissues of sole (Solea senegalensis) and the relationships with the abiotic environment

The distribution patterns and the organ-specific accumulation trends of 10 trace metals (iron, manganese, zinc, copper, chromium, nickel, cobalt, lead, cadmium and silver) and 4 major elements (sodium, potassium, calcium and magnesium) in 10 different tissues (heart, muscle, kidney, stomach, intestine, liver, gill, gonads, white skin and dark skin) of a benthic fish species (Solea senegalensis) from a densely populated coastal area affected by anthropogenic activities, the Bay of Cadiz (SW Spain), have been investigated. High variability of metal concentrations among tissues were found for Ca, Fe, Zn, Cu, Pb and Ag. Factor analysis was applied to study this variability. Five principal components were found explaining the 92.95% of the total variance and similarities in behavioural patterns of bioaccumulation were described. They associated Mg, Cr, Ni and Mn to intestine and stomach tissues (PC1), Ag, Cu and Cd to liver (PC2), Zn, K and Co to gonads (PC3), Na, Fe and Pb to gill, heart and kidney tissues (PC4) and Ca, Pb and Mn to gill and dark skin (PC5). The metallic concentration in the sediment and water was also studied. The pollution in this area was found moderate with outstanding values of Zn, Cu and Pb (average values of 139, 50.4 and 75.6?mg?kg^?1, respectively) in sediment and dissolved Cu (average value of 2.5?µg?L^?1). Metal bioconcentration trends followed the order Zn?>?Cu?>?Cd?>?Pb for dissolved metals in seawater, Cu?>?Zn?>?Cd?>?Pb?≈?Mn?>?Fe?≈?Ni?≈?Co for metals associated to particulate matter and Zn?≈?Cu?>?Cd?>?Mn?>?Co?≈?Fe?>?Ni?≈?Pb?>?Cr for metals in the sediment. Higher values were found for copper in liver, zinc in gonads and lead in gill, showing the relationship between biotic and abiotic environment. In addition, Cd bioconcentration factors were found high in liver and gill showing the sensitivity of sole to this metal even at low concentrations.     

原子吸收光谱法测定水生生物体内铜、锌、镍、铬、铅、镉

用硝酸-高氯酸体系消解螺蛳和水葫芦样品,采用火焰原子吸收光谱法测定铜、锌、镍、铬,用石墨炉原子吸收光谱法测定铅、镉。铜、锌、镍、铬、铅、镉的检出限分别为0.328、0.126、0.271、0.416、0.006 64、0.001 15 mg/kg,线性相关系数不小于0.999 0,测定结果的相对标准偏差为1.1%~3.7%,加标回收率为86.0%~94.2%。     

Inductively Coupled Plasma Mass Spectrometry for Sequential Determination of Trace Metals in Rain and River Waters Using Electrothermal Vaporization

Abstract

The sequential determination of 14 trace metals, Al, V, Cr, Mn, Fe, Ni, Cu, Zn, As, Se, Mo, Cd, Sb and Pb, in rain and river water samples has been investigated using an inductively coupled plasma mass spectrometry (ICP-MS) with a graphite rod electrothermal vaporizer (ETV) in the presence of the mixed modifier of palladium nitrate and magnesium nitrate. The sensitivity enhancements due to the presence of the modifier were observed for all analyte elements. Detection limits as high as 0.52, 0.13, 0.89, 0.35, 1.76, 0.5, 0.9, 0.5, 0.04, 1.03, 0.28, 0.07, 0.1 and 3.78 pg, respectively, for Al, V, Cr, Mn, Fe, Ni, Cu, Zn, As, Se, Mo, Cd, Sb and Pb have been achieved. For the determination of trace metals in both rain and river water samples by this method, the repeatibility of sample solution were very good, i.e. from 1% to 7% (as a coefficient variation) and the recoveries of elements were good enough, i.e. from 81% to 106%, by using a standard addition method. There was no difference between the results obtained by nebulizer ICP-MS and those obtained by this method, except for zinc and arsenic.     

凤仙花植株不同部位微量元素含量的比较分析

The samples of pueraria lobata ohwi were digested by HNO3 + HClO4 .contents of the next trace elements Fe,Zn,Cu,Mn,Ca,Mg,Co,Cr,Ni,Cd,Pb and Al in the bloom,base,stem,and leaf of Impatiens balsamina have been determined by Flame Atomic Absorption method.The result show that the recovery is about 97.5%-103.2%,and the RSD<2.7%,with good accuracy and precision.The order of the content of the trace elements of high to low is as follows:leaf>stem>bloom>base.The importance of essential trace elements Zn,Fe,Mn,Cu for human each has a higher content.In addition,toxic trace elements such as lead,arsenic and cadmium are also found.     

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.