痕量硝基酚的反相高效液相色谱电化学检测

本文以甲醇与０．０３ｍｏｌ／Ｌ邻苯二甲酸氢钾缓冲液为淋洗液，采用安培型电化学检测，实现了２－硝基苯酚，３－硝基苯酚，４－硝基苯酚及２，４－二硝基苯酚和２，６－０二硝基苯酚等五种酚类化合物于Ｐｅｒｋｉｎ－Ｅｌｍｅｒ Ｎｕｃｌｅｏｓｉｌ Ｃ８柱上反相高效液相色谱的分离及在Ｅ＝＋１．２Ｖ时于玻碳电极上的同时检测。     

测定牛奶中5种青霉素残留量的高效液相色谱柱前衍生法

样品采用乙腈直接提取,离心分离及固相（Ｃ１８柱）净化方式,经衍生后,用液相色谱紫外检测器测定牛奶中５种青霉素残留,方法最小检测质量 度０．００５ｍｇ／Ｌ,回收率范围在６８．９％－１０１．３％之间,相对标准偏差为３．２１％－６．１８％。     

高效液相色谱法测定复方感冒液多组分含量

报道了采用高效液相色谱法（ＨＰＬＣ）测定复方感冒液中愈创木酚、扑热息痛、甲基麻黄碱、咖啡因、美沙芬及扑尔敏的含量。色谱柱为ＺｏｒｂａｘＯＤＳ柱,前４种药物采用的流动相为甲醇－０．０５ｍｏｌ／Ｌ磷酸二氢钾－磷酸（２５０∶７５０∶０．５）,检测波长２１４ｎｍ;后２种药物采用的流动相为甲醇－水－磷酸－十二烷基硫酸钠（８０∶２０∶０．５∶０．２）,检测波长２６０ｎｍ。在此色谱条件下,６种药物可获得很好的分离,回收率也高。     

高效液相色谱法测定血浆中舒必利浓度

讨论了测定舒必利血药浓度的反相高效液相色谱方法。选用美国Ｂｉｏ－Ｒａｄ７００型高效液相色谱仪,ＲＰ－３１８色谱柱,ＵＶ检测波长２９０ｎｍ,流动相为甲醇－水－冰醋酸（６０３０１）,内标物为胃复安。回收率为９７．９５％～９９．９６％,ＲＳＤ为２．６％～５．１％,最低检出浓度１．０ｍｇ／Ｌ,线性范围５～１００ｍｇ／Ｌ。测定３０例服药病人的血药浓度,得到了满意的结果。     

高效液相色谱法测定地榆中金丝桃甙的含量

采用高效液相色谱法测定了地榆中金丝桃甙的含量。色谱柱为Ｓｈｉｍ－ｐａｃｋＣＬＣ－ＯＤＳ柱,以甲醇－０．０２５ｍｏｌ／Ｌ磷酸（５０５０）为流动相,检测波长３７０ｎｍ,测定组分与其它组分的色谱峰达到基线分离。加样回收率平均值为９８．７％,ＲＳＤ为１．９％。为控制中药地榆的内在质量提供了新的测定指标和可靠的方法。     

反相高效液相色谱法测定人血浆中异丙酚浓度

用柱前衍生化反相高效液相色谱法测定人血浆中异丙酚浓度,为临床药理学研究提供了依据。提取的异丙酚及内标麝香草酚同时以Ｇｉｂｂｓ试剂衍生化,衍生物经色谱柱分离和紫外检测,异丙酚在５０～１５００μｇ／Ｌ浓度范围内呈线性关系（ｒ＝０．９９９１）。方法平均变异系数为６．１％,最低检出浓度为２４．８μｇ／Ｌ,已满意地用于临床药理学研究。     

高效液相色谱法测定伸筋丹中士的宁含量

采用高效液相色谱法（ＨＰＬＣ）测定了中成药伸筋丹中士的宁含量。色谱条件：氰基柱并加同种类预柱；流动相：甲醇－水－乙酸－三乙胺（９８００：１５５：３０：１５）；ｐＨ６．７；流速：１．０ｍＬ／ｍｉｎ；紫外检测，波长２５４ｎｍ；在４～２０ｍｇ／Ｌ浓度范围内，士的宁的峰面积Ａ与浓度Ｃ间的回归方程为：Ａ＝－７．０１×１０~３＋９．０８×１０~５Ｃ（ｒ＝０．９９９９）；外标法定量，方法精密度ＲＳＤ＝１．９１％（ｎ＝６）。     

高效液相色谱法测定伸筋丹中士的宁含量

 采用高效液相色谱法（ＨＰＬＣ）测定了中成药伸筋丹中士的宁含量。色谱条件：氰基柱并加同种类预柱；流动相：甲醇－水－乙酸－三乙胺（９８００：１５５：３０：１５）；ｐＨ６．７；流速：１．０ｍＬ／ｍｉｎ；紫外检测，波长２５４ｎｍ；在４～２０ｍｇ／Ｌ浓度范围内，士的宁的峰面积Ａ与浓度Ｃ间的回归方程为：Ａ＝－７．０１×１０~３＋９．０８×１０~５Ｃ（ｒ＝０．９９９９）；外标法定量，方法精密度ＲＳＤ＝１．９１％（ｎ＝６）。     

相转移催化酯化反相高效液相色谱法测定食品中有机酸

在不预分离水相中有机酸的情况下，用α－溴苯乙酮作酯化试剂，以１８－冠醚－６作相转移催化剂直接酯化有机酸，酯化液直接用高效液相色谱分析，紫外检测器检测，操作简便、干扰小、变异系数ＣＶ％＝１．４－５．６％检测下限５－２０μｇ／Ｌ，实际样品回收率９０．９－１０３．３％。     

肿瘤细胞中长春新碱的高效液相色谱法测定

长春新碱（ＶＣＲ）为重要和常用抗肿瘤药物之一。肿瘤细胞耐药性是导致化疗失败的主要原因。为了筛选耐药细胞的逆转剂,建立了测定肿瘤细胞内ＶＣＲ浓度的高效液相色谱法,色谱条件为：Ｚｏｒｂａｘ－ＯＤＳ反相柱２５ｃｍ×４．６ｍｍｉ．ｄ．,流动相：０．０２ｍｏｌ／ＬＫ２ＨＰＯ４（ｐＨ６．６）∶ＣＨ３ＯＨ（２０∶８０,Ｖ／Ｖ）,流速：１．０ｍＬ／ｍｉｎ,检测波长：２６７ｎｍ。方法简单、快速、选择性好,在１０～２００ｍｇ／Ｌ范围内ＶＣＲ浓度－峰高呈良好的线性关系（ｒ＝０．９９９８）,仪器灵敏度为４ｎｇ。     

Degradation of atrazine and several organophosphorus pesticides in oranges

The degradation of atrazine and four organophosphorus pesticides (chlorpyriphos, fenamiphos, methidathion and methyl-parathion) in oranges was studied. Oranges were immersed in a Milli-Q water solution spiked with 10 mg litre-1 of each pesticide for one day, allowing their adsorption on the orange peel. Then, the oranges were rinsed with Milli-Q water and left outdoors to expose them to natural ambient conditions for two weeks. In parallel, an aqueous solution containing 1 mg litre-1 of each pesticide was placed in a Pyrex flask, which was tightly closed, and exposed to the same ambient conditions. Both samples (orange peel and Milli-Q water) were analyzed periodically by gas chromatography coupled to a nitrogen-phosphorus detector. The pesticide degradation in both samples could be described using a first-order degradation curve. Half-lives varied from 14.5 to more than 30 days in aqueous solution and from 2.3 to 4.1 days in oranges for organophosphorus pesticides, while those for atrazine were 3.1 days and 14.2 days, respectively. The presence of some organophosphorus degradation products in water samples after storage under the above conditions was confirmed by gas chromatography-mass spectrometry.     

Removal of endocrine‐disrupting compounds from water using macroporous molecularly imprinted cryogels in a moving‐bed reactor

Highly efficient removal of endocrine‐disrupting compounds (EDCs) such as 17β‐estradiol (E2), 4‐nonylphenol (NP) and atrazine from water was achieved using a novel macroporous adsorption medium. The medium consisted of a macroporous poly(vinyl alcohol) (PVA) cryogel with molecularly imprinted polymer (MIP) particles embedded in it. The MIP was prepared using E2, NP and atrazine as templates. The macroporous composite molecularly imprinted cryogels were formed inside the open‐ended protective shells, known as Kaldnes carriers. These adsorbents (defined as Macroporous Gel Particles, MGPs) were evaluated on the removal of E2, NP and atrazine from water using different column configurations, namely column filled with the MGPs (packed‐bed column) and in moving‐bed reactors (defined here as moving‐bed MGPs reactor). Complete binding (> 99%) of E2 from a spiked aqueous solution (1 mg/L) was achieved using E2‐MIP/MGPs in a moving‐bed MGPs reactor at the retention time in the reactor of 4 min, while only 77% was bound to the nonimprinted medium (NIP/MGPs). Similar results were also obtained for the adsorption medium imprinted with atrazine. All contaminants studied (E2, atrazine and NP) were effectively removed from water at low (environmentally relevant) concentrations by the respective adsorption medium.     

Determination of herbicide residues in soil in the presence of persistent organochlorine insecticides

Summary A rapid and reproducible gas-chromatographic method has been developed for determination of residues in soil of some widely used herbicides such as trifluralin, metribuzin, alachlor, acetochlor, metolachlor, pendimethalin, simazine, atrazine, prometryne, in the presence of persistent organochlorine insecticides (p,p-DDT, o,p-DDT, p,p-DDE, alpha-HCH, gamma-HCH, heptachlor). Determination of some herbicides by GC/ECD is difficult since their relative retention times on packed columns usually used for pesticide analysis are equal or close to those of some persistent organochlorine insecticides which can still be found almost everywhere, especially in cultivated soils. A 1.8 m column of 3% OV-225 + 5% SE-52 in a ratio of 1.4:0.9 gave good separation of all herbicides and insecticides mentioned. The influence of 6 solvents and solvent systems applied most frequently for soil extraction of pesticide residues on recovery of the compounds under study was examined. Acetonitrile was the most suitable extractant as it rendered highest residue recoveries and minimal amount of co-extractives. Residues of simazine, atrazine, and prometryne were determined in the same extracts by the use of NP-detector and a column of 5% Carbowax 20M. Recoveries of the compounds under study were in the interval of 86–103% without cleanup and 78–94% when cleanup was carriet out. The method can be used in pesticide monitoring of soil as it offers an opportunity for rapid determination of soil applied herbicides and persistent organochlorine insecticides which are some of the most common pollutants in cultivated soils.     

Adsorption of atrazine from aqueous electrolyte solutions on humic acid and silica

The adsorption of, the still widely used, herbicide atrazine on model soil components, such as humic acid and humic acid-silica gel mixtures, was investigated in a series of batch experiments, under different experimental conditions (ionic strength, temperature, and pH). The investigation aimed at obtaining an estimate of the contribution of each of the soil components on the adsorption of atrazine from aqueous solutions. The kinetics of atrazine adsorption on humic acid showed two steps: a fast step, of a few hours duration, and a second slow step, which continued for weeks. The kinetics of adsorption data gave a satisfactory fit to the Elovich equation. Τhe adsorption of atrazine on the test substrates was found to be reversible in all cases. The atrazine uptake data on the test substrates were fitted best with the Freundlich adsorption isotherm. The ionic strength of the atrazine aqueous solutions did affect the amount of the atrazine adsorbed on the test substrates, suggesting that electrostatic forces between atrazine molecules and soil play a significant role in the adsorption process. An increase of temperature resulted in a decrease of atrazine adsorption on humic acid at low atrazine equilibrium concentrations. However, for higher levels of equilibrium concentrations (≥3 mg/L) the amount of atrazine adsorbed onto the test substrate increased as temperature increased. The calculated isosteric enthalpies of adsorption ranged between slightly exothermic at low atrazine uptake and slightly endothermic at high atrazine uptake, all values being in the range of physisorption.     

Adsorption of atrazine on soils: model study

The adsorption of the widely used herbicide atrazine onto three model inorganic soil components (silica gel, gamma-alumina, and calcite (CaCO(3)) was investigated in a series of batch experiments in which the aqueous phase equilibrated with the solid, under different solution conditions. Atrazine did not show discernible adsorption on gamma-alumina (theta=25 degrees C, 3.8相似文献   

在线固相萃取-超高效液相色谱-串联质谱法快速测定地表水中超痕量阿特拉津

建立了在线固相萃取-超高效液相色谱-串联质谱（on line SPE-UPLC-MS/MS）测定地表水中超痕量阿特拉津的方法。样品经滤膜过滤,HLB Direct Connect HP在线固相萃取小柱富集纯化,甲醇溶液洗脱,以Acquity BEH 130为分析柱,串联质谱进行检测,外标法定量。阿特拉津在1.0~5000 ng/L范围内线性关系良好,相关系数（r）为0.9989;该方法检出限为0.2 ng/L,阿特拉津的回收率为83.0%~105.1%,相对标准偏差为1.6%~5.3%（n=7）,满足超痕量分析测试的要求。该法灵敏度高,分析速度快,对于保障水环境安全、及时提供污染信息、有效应对环境应急突发事件具有十分重要的意义。     

Development and application of immunoaffinity column chromatography for atrazine in complex sample media

A rabbit antibody immunoaffinity (IA) column procedure was evaluated as a cleanup method for the determination of atrazine in soil, sediment, and food. Four IA columns were prepared by immobilizing a polyclonal rabbit anti-atrazine antibody solution to HiTrap Sepharose columns. Atrazine was bound to the IA columns when the loading solvents were either 100% water, 2% acetonitrile in water, or 10% methanol in phosphate buffered saline (PBS). Quantitative removal of atrazine from the IA columns was achieved with elution solvents of either 70% ethanol in water, 70% methanol in water, or 100% methanol. One control column was prepared using nonspecific rabbit IgG antibody. This control column did not retain any applied atrazine indicating atrazine did not bind indiscriminately to protein or the Sepharose support. The four IA columns showed reproducible coupling efficiency for the immobilization of the atrazine antibody and consistent binding and releasing of atrazine. The coupling efficiency (4.25 mg of antibody in 1 mL of resin bed) for the four IA columns ranged from 93 to 97% with an average of 96 ± 2% (2.1%). Recoveries of the 500, 50, and 5 ng mL⁻¹ atrazine standard solutions from the four IA columns were 107 ± 7% (6.5%), 122 ± 14% (12%), and 114 ± 9% (8.0%) respectively, based on enzyme-linked immunosorbent assay (ELISA) data. The maximum loading was approximately 700 ng of atrazine for each IA column (∼0.16 μg of atrazine per mg of antibody). The IA columns could withstand 100% methanol as the elution solvent and could be reused more than 50 times with no change in performance. The IA columns were challenged with soil, sediment, and duplicate-diet food samples and effectively removed interferences from these various matrices for subsequent gas chromatography/mass spectrometry (GC/MS) or ELISA analysis. The log-transformed ELISA and GC/MS data were significantly correlated for soil, sediment and food samples although the ELISA values were slightly higher than those obtained by GC/MS. The IA column cleanup procedure coupled with ELISA analysis could be used as an alternative effective analytical method for the determination of atrazine in complex sample media such as soil, sediment, and food samples.     

Preparation, Properties and Mechanism of Inhomogeneous Calcium Alginate Ion Cross-linking Gel Microspheres

Inhomogeneous calcium alginate ion cross-linking gel microspheres,a novel ion absorbent,were prepared by dropping a sodium alginate solution to a calcium chloride solutioin via an electronic droplet generator.Calcium alginate microspheres have uniform particle sizes.a smooth surface and a microporous structure.The electrode probe reveals the inhomogeneous distribution of calcium ions with the highest concentration on the surface,and the lowest concentration in the cores of the spheres.As a novel ion adsorbent,calcium alginate gel microspheres have a lower limiting adsorption mass concentration,a higher enrichment capacity and a higher adsorption capacity for Pb^2 than usual ion exchange resins.The highest percentage of the adsorption is 99.79%.The limiting adsorption mass concentration is 0.0426mg/L.The adsorption capacity for Pb^2 is 644mg/g,Calcium alginate gel microspheres have a much faster ion exchange velocity than D418 chelating resin and D113 polyacrylate resin.The moving boundary model was employed to interpret the ion exchange kinetics process,which indicates that the ion exchange process is controlled by intraparticle diffusion of adsorbable ions.So the formation of inhomogeneous gel microspheres reduces the diffusion distance of adsorbable ions within the spheres and enhances the ion exchange velocity.Alginate has a higher selectivity for pb^2 than for Ca^2 and the selectivity coefficient KCa^Pb is 316. As an ion cross-linking gel,calcium alginate inhomogeneous microspheres can effectively adsorb heavy metal Pb^2 at a higher selectivity and a higher adsorption velocity.It is a novel and good ion adsorbent.     

The role of organic colloids in herbicide transfer to rivers: a quantitative study of triazine and phenylurea interactions with colloids

For moderately hydrophobic compounds such as most pesticides adsorption on colloids (<0.2 microm) may play a key role in pesticide mobility as well as in their degradation by chemical and microbiological processes. However, until now, pesticide-organic colloid interactions are poorly understood. Quantitative data for sorption equilibria on colloids of two series of herbicides including triazines (atrazine, simazine, terbutylazine, prometryne, desethylatrazine, and desisopropylatrazine) and phenylureas (isoproturon, linuron, neburon, and diuron) sampled in the Seine river (urban zone) and the Marne river (agricultural zone) are presented. Partition coefficient of herbicides on colloids (K(com)), were evaluated by solid-phase extraction coupled with high-performance liquid chromatography-UV diode-array detection (SPE-HPLC-UV/DAD). In the case of triazines a satisfactory log-log correlation was found between K(com) and octanol-water coefficient (K(ow)) values. Phenylureas did not obey this correlation, with K(com) values being about two times higher than those of triazines. The existence of two distinct types of adsorption behaviour on colloids partly explains the different occurrence of triazines and phenylureas in surface waters.     

Efficient method for the characterization of the interaction of pesticides with different soil samples

The interaction of atrazine, simazine, terbutryn, prometryn, diuron and sandy as well as brown forest soil samples from different layers was investigated. A suitable, simple model was created, similarly to column chromatography. Polar or apolar character of the pesticides was proven to be the most important factor in the soil-pesticide interaction, increasing polarity resulted in enhanced bond strength between the soil and pesticide.