亲水作用色谱-电喷雾串联质谱法检测原料奶及奶制品中的三聚氰胺

建立了亲水作用色谱-电喷雾串联质谱测定原料奶及奶制品中三聚氰胺的方法。样品采用1%三氯乙酸水溶液-乙腈（体积比为1∶1）混合溶液提取,混合型阳离子交换反相固相萃取柱（MCX）富集净化,亲水作用色谱柱分离,电喷雾串联四极杆质谱仪进行检测。结果表明,三聚氰胺的质量浓度在0.05～10.0 mg/L范围内具有良好的线性关系。原料奶及奶制品中的三聚氰胺在0.5,2.5和10 mg/kg 3个添加水平下,平均回收率为76.3%～98.7%,相对标准偏差均小于6.8%;定量限（S/N＞10）为0.05 mg/kg。     

三乙烯四胺修饰β-环糊精交联树脂分离富集/原子吸收法测定大米中的铅、镉

该文制备了一种新型吸附材料三乙烯四胺修饰β-环糊精交联树脂(TETA-β-CDP),并对其进行红外光谱表征,优化了该吸附材料对痕量铅、镉的吸附和解析条件,建立了动态条件下同时分离富集/原子吸收光谱测定大米中铅和镉的新方法。在p H 5.5时,样品溶液以1.0 m L/min流速过柱,试液中的Pb2+和Cd2+可被该树脂定量富集,其动态饱和吸附容量分别为22.8,31.3 mg/g,吸附在TETA-β-CDP上的Pb2+和Cd2+可用0.1 mol/L HCl以0.8 m L/min流速完全洗脱。该方法对铅、镉的检出限(3σ,n=11)分别为0.038 mg/L和0.016 mg/L;线性范围分别为0.2~20 mg/L和0.05~2.5 mg/L;相对标准偏差(RSD)分别为2.8%和1.7%;加标回收率分别为97.5%~101.0%和95.0%~102.5%。该方法用于大米样品中痕量铅、镉的测定,结果满意。     

新型强阳离子交换聚合物整体柱的制备及其在奶制品中三聚氰胺测定中的应用

在内径为530 μm的石英毛细管中原位聚合得到一种新的强阳离子交换聚合物整体柱2-丙烯酰胺-2-甲基-1-丙磺酸-乙二醇二甲基丙烯酸酯聚合物(poly(AMPS-co-EDMA))整体柱,并将其作为聚合物整体柱微萃取(PMME)的萃取介质。优化N,N-二甲基甲酰胺(DMF)和聚乙二醇(PEG)致孔体系的比例,制备得到的poly(AMPS-co-EDMA)整体柱渗透性好、机械强度高且在水溶液中具有良好的稳定性。通过考察样品溶液的pH值、盐浓度和有机溶剂含量对萃取效率的影响,证明该整体柱主要通过强阳离子交换和疏水相互作用对三聚氰胺进行萃取富集。在PMME与高效液相色谱联用技术的基础上,建立了检测奶制品中三聚氰胺含量的分析方法。奶制品中三聚氰胺的检出限和定量限分别为0.09 mg/kg和0.3 mg/kg,在0.5~80 mg/kg的含量范围内具有良好的线性关系,日内、日间测定的相对标准偏差不高于7.5%。结果表明,该方法简便、快速、灵敏度高且成本低,适合于奶制品中微量三聚氰胺的检测。     

流动注射-微柱在线富集/电感耦合等离子发射光谱法测定中成药中痕量铅和镉

采用自制固相萃取材料PTFE-g-GMA-PEI纤维填充微柱预富集和流动注射(FI) 与电感耦合等离子发射光谱仪联用, 测定样品中痕量Pb2+和Cd2+.对Pb2+和Cd2+的富集与洗脱条件进行优化,并给出相应离子的分析特性.结果表明: 本方法Pb2+和Cd2+检出限分别为3.5和0.15 μg/L; 富集倍数分别为30和80; RSD分别为1.5%和0.6%(n=9,单个离子浓度为50 μg/L).本方法应用于几种中成药中的痕量铅和镉的同时测定,样品加标回收率在90%～108% 之间, 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。     

纳米B2O3/TiO2复合材料的制备及其对痕量银的分离富集性能研究与应用

制备了新型纳米B2O3/TiO2吸附材料,并采用扫描电镜(SEM)及红外光谱(IR)对其进行表征,优化了纳米B2O3/TiO2复合材料对试液中痕量银的吸附和解吸条件,建立了纳米B2O3/TiO2分离富集-原子吸收光谱测定痕量银的新方法。当pH 4.3时,在22℃下振荡20 min,Ag+能被该材料快速吸附,其静态饱和吸附容量为11.72 mg/g,吸附在纳米B2O3/TiO2上的Ag+可用0.1 mol/L HNO3-0.05 mol/L硫脲(1∶4)完全洗脱。该方法的检出限为2.01μg/L,线性范围为0.01～4.00 mg/L,相对标准偏差(RSD)为1.8%,加标回收率为95%～105%。方法应用于实际矿渣样品中痕量银的测定,结果满意。     

奶粉中三聚氰胺的加压毛细管电色谱法测定

建立了加压毛细管电色谱法(pCEC)测定奶粉中三聚氰胺含量的方法。采用三氯乙酸和乙腈沉淀样品中的蛋白质,并经强阳离子固相萃取柱富集净化。优化了有机相的比例、流动相的盐浓度和电压,比较了pCEC与毛细管液相色谱(cLC)的三聚氰胺色谱图。经方法学考察,样品在0.8~80 mg/L质量浓度范围内线性关系良好(r0.999 0),检出限为0.4 mg/L,在添加水平为2~100 mg/kg时的回收率为71%~82%,相对标准偏差(RSD)为5.1%~8.5%。     

亲水作用色谱-串联质谱法测定化妆品中三聚氰胺残留量

建立了化妆品中三聚氰胺的亲水作用色谱-质谱联用（HILIC-MS/MS）检测方法。样品经三氯乙酸溶液提取（脂溶性样品再经正己烷萃取)后,用混合型阳离子交换(MCX)反相固相萃取柱富集净化,用5 mmol/L乙酸铵水溶液(含0.1%甲酸)和乙腈作为流动相,以梯度洗脱方式在ZIC-HILIC色谱柱上实现分离,以电喷雾离子源正离子(ESI+)模式进行质谱分析。三聚氰胺在0.02～0.5 mg/L范围内呈良好线性关系,相关系数为0.9985;方法的检出限(LOD,信噪比(S/N)≥3)为5.0 μg/kg,定量限(LOQ,S/N＞10)为20.0 μg/kg;在0.01～0.1 mg/kg添加浓度范围内,三聚氰胺的平均回收率为84.7%～93.4%,相对标准偏差为4.5%～8.4%。该方法能满足化妆品中三聚氰胺残留量的检测。     

铜(Ⅱ)-三聚氰胺体系共振散射法检测痕量三聚氰胺

基于在pH 3.0的B-R缓冲溶液中,三聚氰胺与Cu2+形成2:1的络合物,导致体系共振光散射(RLS)强度明显增大,在405 nm处,三聚氰胺的质量浓度在0.05～9 mg/L范围内与散射强度成正比,据此建立了利用共振光散射测定三聚氰胺的新方法。检出限为0.037 mg/L。方法已用于奶制品中三聚氰胺的测定。同时探讨了反应机理。     

PTFE-g-GMA-PEI纤维填充微柱/ICP-OES在线预富集测定痕量Cr(Ⅵ)和Cr(Ⅲ)研究

采用自制固相萃取材料聚乙烯亚胺胺化的接枝甲基丙烯酸缩水甘油酯的聚四氟乙烯(PTFE-g-GMA-PEI)纤维填充微柱预富集和流动注射(FI)与电感耦合等离子发射光谱仪(ICP-OES)联用测定样品中痕量Cr(Ⅵ)和Cr(Ⅲ)。对Cr(Ⅵ)和Cr(Ⅲ)的富集与洗脱条件进行优化,并给出Cr(Ⅲ)离子的分析特性。结果表明,该法测定的Cr(Ⅲ)离子富集倍数为30,样品通量为72h-1,检出限为2.2μg/L,RSD为1.2%(50μg/L,n=9),其线性范围为2～500μg/L。该法成功用于环境水样中铬的形态分析,其加标回收率为90～104%。     

微孔有机聚合物固相微萃取纤维的制备及在有机氯农药检测中的应用

利用1,3,6,8-四(4-醛基)芘和三聚氰胺为单体合成微孔有机聚合物(MOP),并将其固定在不锈钢丝上,制备成固相微萃取纤维涂层。将其用于顶空固相微萃取(HS-SPME),结合气相色谱-电子捕获检测手段,建立了对大米中有机氯农药的在线检测方法。实验考察了4种实验参数对富集能力的影响,得到了最优的实验条件:萃取温度80℃、萃取时间25 min、NaCl质量浓度200 g/L、解吸时间6 min。在此实验条件下,对有机氯农药的富集倍数达到115~318倍。方法在0.05~50μg/kg范围内具有良好的线性关系,检出限为2.4~11.3 ng/kg。同一纤维及不同纤维富集后测定结果的相对标准偏差范围分别为1.3%~13.1%和2.3%~13.6%。该方法简单、快速,可以实现对实际样品中有机氯农药的痕量分析。     

离子印迹壳聚糖/凹土分离富集-火焰原子吸收光谱测定中药材中痕量Cd(Ⅱ)的研究

建立了离子印迹壳聚糖/凹凸棒石(IICA)分离富集-火焰原子吸收光谱(FAAS)测定中药材中痕量Cd(Ⅱ)的新方法。在动态吸附条件下,系统研究了溶液pH值、流速、洗脱条件和干扰离子对痕量Cd(Ⅱ)分离富集的影响。研究表明,在pH为4.5,上样流速为0.60mL/min条件下,Cd(Ⅱ)能被IICA定量富集;吸附的Cd(Ⅱ)可用1.0mol/L HCl-0.1mol/L甲基异丁酮的乙醇溶液,在流速为0.96mL/min条件下完全洗脱。优化条件下,IICA对Cd(Ⅱ)的动态吸附容量为56.45mg/g。线性范围为0.00097～1.28mg/L,r=0.9994,检出限(3σ,n=11)为0.97μg/L,相对标准偏差为1.32%(n=6,c=0.08mg/L),回收率在96.5%～106.4%之间。该方法操作简便,灵敏度和精密度高,可应用于实际中药材样品中痕量镉的测定。     

纳米二氧化钛分离富集石墨炉原子吸收光谱法测定水样中痕量铅

提出了纳米TiO2分离富集,GFAAS测定水样中痕量铅的新方法。详细考察了纳米TiO2对铅的吸附行为,结果表明：在pH4．0时,Pb^2 可被纳米TiO2定量富集,吸附于纳米TiO2上的Pb^2 可用0．1mol／L的硝酸完全解脱。本法对Pb^2 的检出限为52ng／L,相对标准偏差为4．7％(n=10,C=0．02mg／L)。本法已用于实际水样中铅的测定,结果满意。     

Application of NaClO-treated multiwalled carbon nanotubes as solid phase extraction sorbents for preconcentration of trace 2,4-dichlorophenoxyacetic acid in aqueous samples

Multiwalled carbon nanotubes functionalized by oxidation of original multiwalled carbon nanotubes with NaClO were prepared and their application as solid phase extraction sorbent for 2,4-dichlorophenoxyacetic acid (2,4-D) was investigated systemically, and a new method was developed for the determination of trace 2,4-D in water samples based on extraction and preconcentration of 2,4-D with solid phase extraction columns packed with NaClO-treated multiwalled carbon nanotubes prior to its determination by HPLC. The optimum experimental parameters for preconcentration of 2,4-D, including the column activating conditions, the amount of the sorbent, pH of the sample, elution composition, and elution volume, were investigated. The results indicated 2,4-D could be quantitatively retained by 100 mg NaClO-treated multiwalled carbon nanotubes at pH 5, and then eluted completely with 10 mL 3:1 (v/v) methanol-ammonium acetate solution (0.3 mol/L). The detection limit of this method for 2,4-D was 0.15 μg/L, and the relative standard deviation was 2.3% for fortified tap water samples and 2.5% for fortified riverine water sample at the 10 μg/L level. The method was validated using fortified tap water and riverine water samples with known amount of 2,4-D at the 0.4, 10, and 30 μg/L levels, respectively.     

纳米TiO2微柱分离富集测定环境样品中的微量碲

以处理过的纳米TiO2为微柱吸附材料,采用流动注射技术进行微量碲的分离富集,探讨了溶液的pH值、试样流速、试样体积、洗脱液浓度和用量以及干扰离子等因素的影响。 实验结果表明,pH值在8～9.5范围内,纳米TiO2对Te(Ⅳ)具有良好的吸附性能,吸附率接近99%,动态饱和吸附容量为37.02 mg/g;选用2 mL 0.5 mol/L NaOH溶液可将吸附的Te(Ⅳ)完全洗脱,富集倍数为30。 本法的检出限(3σ)为0.013 mg/L,相对标准偏差为RSD=1.99%。 将本法应用于水样的分析,碲的回收率在98%~103%之间,结果令人满意。     

Capillary-electrophoretic determination of zinc and cadmium ions in aqueous solutions with ion-exchange preconcentration

An approach to choosing analyte preconcentration conditions for the subsequent capillary electrophoresis (CE) analysis of the concentrate was substantiated using the simultaneous determination of zinc(II) and cadmium(II) trace concentrations as an example. A CE procedure was developed for the determination of Zn and Cd with the following characteristics: The time of the analysis, including analyte preconcentration from a 50-mL sample, was 30 min. The analytical ranges were 0.01–0.2 mg/L for cadmium(II) and 0.005–0.1 mg/L for zinc(II).     

Determination of trace cadmium in waters by flame atomic absorption spectrophotometry after preconcentration with 1-nitroso-2-naphthol-3,6-disulfonic acid on Ambersorb 572

A procedure for the determination of trace amount of cadmium after adsorption of its 1-nitroso-2-naphthol-3,6-disulfonic acid chelate on Ambersorb 572 has been proposed. This chelate is adsorbed on the adsorbent in the pH range 3-8 from large volumes of aqueous solution of water samples with a preconcentration factor of 200. After being sorbed, cadmium was eluted by 5 mL of 2.0 mol L(-1) nitric acid solution and determined directly by flame atomic absorption spectrophotometery (FAAS). The detection limit (3sigma) of cadmium was 0.32 microg L(-1). The precision of the proposed procedure, calculated as the relative standard deviation of recovery in sample solution (100 mL) containing 5 microg of cadmium was satisfactory (1.9%). The adsorption of cadmium onto adsorbent can formally be described by a Langmuir equation with a maximum adsorption capacity of 19.6 mg g(-1) and a binding constant of 6.5 x 10(-3) L mg(-1). Various parameters, such as the effect of pH and the interference of a number of metal ions on the determination of cadmium, have been studied in detail to optimize the conditions for the preconcentration and determination of cadmium in water samples. This procedure was applied to the determination of cadmium in tap and river water samples.     

Separation,preconcentration and determination of Pb(Ⅱ) in water samples using microcrystalline triphenylmethane loaded with quinolin-8-olate

This paper described a novel method for the preconcentration of Pb(Ⅱ) using microcrystalline triphenylmethane loaded with quinolin-8-olate prior to the determination by flame atomic absorption spectrometry.Pb(Ⅱ) could be enriched by controlling appropriate condition.The preconcentration factor could reach to 200 and the detection limit of Pb(Ⅱ) was 0.074μg/L.The recovery was in a range of 93.5-103%with relative standard deviation of 1.0-2.2%.The proposed method had been successfully applied to the determ...     

Doehlert matrix for optimisation of procedure for determination of nickel in saline oil-refinery effluents by use of flame atomic absorption spectrometry after preconcentration by cloud-point extraction

This paper proposes a preconcentration procedure for determination of nickel in saline aqueous waste samples by flame atomic absorption spectrometry (FAAS). It is based on cloud-point extraction of nickel(II) ions as 2-(5-bromo-2-pyridylazo)-5-diethilaminophenol (Br-PADAP) complexes using octylphenoxypolyethoxyethanol (Triton X-114) as surfactant. The optimisation step was performed using a four-variable Doehlert design, involving the factors centrifugation time (CT) of system after addition of surfactant, solution pH, methanol volume (MV) added at micellar phase, and buffer concentration (BC). The analytical response used was absorbance, after volume correction. Using the established experimental conditions in the optimisation step the procedure enables nickel determination with a detection limit (3 delta/ S) of 0.2 microg L(-1), quantification limit (10 delta/ S) of 0.7 microg L(-1), and precision, calculated as relative standard deviation ( RSD) of 4.7 ( n=8) and 3.5% ( n=8) for nickel concentration of 1 and 5 microg L(-1), respectively. The preconcentration factor, determined from the ratio of the slopes of the analytical curves with and without preconcentration, is 74. The recovery achieved for nickel determination in the presence of several cations demonstrated that this procedure could be applied for analysis of water samples. The robustness was checked by using saturated fractional factorial designs, centred on the established experimental conditions in the optimisation step. The results of these tests demonstrated that the variables centrifugation time and buffer concentration are robust for modification by 10% and that solution pH and methanol volume are robust for 5%. Accuracy was evaluated by using the certified material reference SLEW-3 estuarine water for trace metals. The procedure was used for determination of nickel in saline effluents from oil refinery samples. Recovery results (95-104%) indicate that the procedure has satisfactory accuracy for nickel determination in these samples.     

On-Line Preconcentration and Simultaneous Determination of Cu and Mn in Water Samples Using a Minicolumn Packed with Sisal Fiber by MIP OES

An on-line preconcentration system for the simultaneous determination of Copper (Cu) and manganese (Mn) in water samples was developed and coupled to a microwave-induced plasma optical emission spectrometer (MIP OES). The flow injection system was designed with a minicolumn packed with sisal fiber (Agave sisalana). A multivariate experimental design was performed to evaluate the influence of pH, preconcentration time, and eluent concentration. Optimal conditions for sample preparation were pH 5.5, preconcentration time was 90 s, and HCl 0.5 mol L⁻¹ was the eluent. The main figures of merit were detection limits 3.7 and 9.0 µg L⁻¹ for Cu and Mn, respectively. Precision was expressed as a relative standard deviation better than 10%. Accuracy was evaluated via spiked recovery assays with recoveries between 75–125%. The enrichment factor was 30 for both analytes. These results were adequate for water samples analysis for monitoring purposes. The preconcentration system was coupled and synchronized with the MIP OES nebulizer to allow simultaneous determination of Cu and Mn as a novel sample introduction strategy. The sampling rate was 20 samples/h. Sisal fiber resulted an economical biosorbent for trace element preconcentration without extra derivatization steps and with an awfully time of use without replacement complying with the principles of green analytical methods.