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1.
We are presenting an electrochemical sensor for the simultaneous determination of dopamine (DA) and uric acid (UA) in the presence of even high concentrations of ascorbic acid (AA). It based on a glassy carbon electrode modified with an electroactive film of polymerized dibromofluorescein. The electrochemical behaviors of DA and UA were studied by cyclic voltammetry using the modified electrode. It exhibits excellent electrocatalytic activity towards the oxidation of the two analytes. Most notably, the oxidation potentials differ by 180 and 200?mV between AA-DA and DA-UA, respectively. Thus, excellent selectivity towards the oxidation of DA and UA in the presence of even high concentrations of AA is accomplished. Under the optimum conditions, the anodic peak currents are linearly related to the concentrations of DA and UA in the range from 0.2 to 200?μmol?L-1 and from 1.0 to 250?μmol?L-1, respectively. The detection limits for DA and UA are 0.03?μmol?L-1 and 0.2?μmol?L-1, respectively (at an S/N of 3). The method has good selectivity and sensitivity and was successfully applied to the simultaneous determination of DA and UA in spiked human serum.
Figure
A novel electrochemical sensor based on poly (dibromofluorescein) film modified glassy carbon electrode has been fabricated and used for the simultaneous determination of dopamine and uric acid in the presence of high concentration of ascorbic acid with good selectivity and sensitivity.  相似文献   

2.
A solid bar microextraction (SBME) method containing sorbent materials 2?mg in the lumen of a porous hollow fiber membrane 2.5?cm for the extraction of carbamazepine, diclofenac and ibuprofen from river water samples is described. The desorbed analytes were analyzed using reversed-phase high performance liquid chromatography with ultraviolet detection. In order to achieve optimum performance, several extraction parameters were optimized. Of the sorbents evaluated, LiChrosorb RP-8 was the most promising. Under the optimized conditions, limits of detection from 0.7 to 0.9???g?L?1, precisions from 5.5 to 6.4% and a correlation coefficient of 0.999 were obtained for the target drugs over a concentration range of 1?C200???g?L?1. In comparison with the solid phase extraction, the SBME system offers distinct advantages due to its higher enrichment factors, lower consumption of organic solvents and time saving.
A solid bar microextraction method for the liquid chromatographic determination of trace diclofenac, ibuprofen and carbamazepine in river water  相似文献   

3.
We have developed a solid phase extraction method for the determination of cadmium ions in aqueous samples. It is based on the adsorption of Cd(II) on alumina nanoparticles coated with sodium dodecyl sulfate and modified with a newly synthesized Schiff base. Analytical parameters such as pH value, amount of adsorbent, type and concentration of eluent, flow rates of the sample and eluent, sample volume and matrix effects were optimized. Desorption is accomplished with 2?mol?L?1 nitric acid. Cd(II) was then determined by flame atomic absorption spectrometry. The maximum enrichment factor is 75. Under the optimum experimental conditions, the detection limit is 0.14???g?L?1 in original solution. The adsorption capacity of the modified sorbent is 4.90?mg?g?1 for cadmium ions. The method was applied to the determination of trace quantities of Cd(II) in water, wastewater, and biological and food samples with satisfactory results.
Figure
Schematic representation of the loading L on the alumina nanoparticles  相似文献   

4.
Multiwalled carbon nanotubes were impregnated with 4-(2-thiazolylazo)resorcinol and used for the separation and preconcentration of Cd(II), Pb(II), Zn(II) and Ni(II) ions from food samples. The analytes were quantitatively recovered at pH 7.0 and eluted with 3?mol?L?1 acetic acid. The effects of pH value, flow rate, eluent type and sample volume on the recoveries, and the effects of alkali, earth alkali and transition metals on the retention of the analytes were studied. The method was validated using the standard certified reference materials SRM 1570A (spinach leaves) and IAEA 336 (lichen), and the results were found to be compatible with the certified values of reference materials. The new enrichment procedure was applied to the determination of these ions in various food samples.
Figure
Multiwalled carbon nanotubes were impregnated with 4-(2-thiazolylazo)resorcinol and used for the separation and preconcentration of Cd(II), Pb(II), Zn(II) and Ni(II) ions from food samples. The analytes were quantitatively recovered at pH 7.0 and eluted with 3 mol L-1 acetic acid. The method was validated using the standard certified reference materials SRM 1570A (spinach leaves) and IAEA 336 (lichen), and the results were found to be compatible with the certified values of reference materials. The new enrichment procedure was applied to the determination of these ions in various food samples.  相似文献   

5.
We have evaluated an in-situ ionic liquid-dispersive liquid-liquid microextraction procedure for the determination of six endocrine disrupting phenols in seawaters and industrial effluents using HPLC. The optimized method requires 38???L of the water-soluble ionic liquid 1-butyl-3-methylimidazolium chloride, and 5?mL of seawater or industrial effluent. After appropriate work-up, a drop (~10???L) of an ionic liquid is formed that contains the analytes of interest. It is diluted with acetonitrile and injected into the HPLC system. This procedure is accomplished without heating or cooling the solutions. The method is characterized by (a) average relative recoveries of 90.2%, (b) enrichment factors ranging from 140 to 989, and (c) precisions (expressed as relative standard deviations) of less than 11% when using a spiking level of 10?ng?mL?1. The limits of detection range from 0.8?ng?mL?1 for 4-cumylphenol to 4.8?ng?mL?1 for bisphenol-A.
Figure
Scheme of the in situ IL-DLIME procedure to determine endocrine disrupting phenols in environmental waters.  相似文献   

6.
A novel kind of carbon paste electrode (CPE) was prepared by mixing graphite powder, liquid paraffin and the ionic liquid 1-ethyl-3-methylimidazolium ethylsulfate. The resulting electrode was used for the simultaneous determination of guanosine and adenosine by differential pulse voltammetry. Compared to a conventional CPE, the oxidation peak currents are largely increased, and the oxidation peak potentials are negatively shifted. The electrochemical responses to guanosine and adenosine were investigated. Under optimized conditions, the calibration curves are linear in the concentration range from 1.0?×?10-6?mol?L-1 to 1.6?×?10-4?mol?L-1 for guanosine, and from 1.0?×?10-6?mol?L-1 to 2.7?×?10-4?mol?L-1 for adenosine at pH 3.5. Substances potentially interfering in the biological matrix do no interfere. The method was successfully applied to detect adenosine and guanosine in human urine without sample treatments.
Figure
Cyclic voltammograms on CPE (a) and CILE (b) for 1.0?×?10-4?mol?L-1 adenosine and 1.0?×?10-4?mol?L-1guanosine in a pH 3.5 B-R buffer solution at the scan rate of 100?mV?s-1. Inset was the typical differential pulse voltammograms of 1.0?×?10-4?mol?L-1 adenosine and 1.0?×?10-4?mol?L-1?L guanosine on CILE  相似文献   

7.
A new solid-phase extraction sorbent was used for the preconcentration of Pb(II) and Cr(III) ions prior to their determination by flame atomic absorption spectrometry. It was prepared by immobilization of 2,4-dinitrophenylhydrazine on nano-alumina coated with sodium dodecyl sulfate. The sorbent was characterized by scanning electron microscopy, N2 adsorption and Fourier transform infrared spectrometry, and used for preconcentration and separation of Pb(II) and Cr(III) from aqueous solutions. The ions on the sorbent were eluted with a mixture of nitric acid and methanol. The effects of sample pH, flow rates of samples and eluent, type of eluent, breakthrough volume and potentially interfering ions were studied. Linearity is maintained between 1.2 and 350???g?L-1 of Pb(II), and between 2.4 and 520???g?L-1 of Cr(III) for an 800-mL sample. The detection limit (3?s, N?=?10) for Pb(II) and Cr(III) ions is 0.43 and 0.55???g?L-1, respectively, and the maximum preconcentration factor is 267. The method was successfully applied to the evaluation of these trace and toxic metals in various water, food, industrial effluent and urine samples.
Figure
Recovery percentage of Pb(II) and Cr(III) ions at different solution volumes.  相似文献   

8.
We have developed a simple microchip-based method for the separation and enrichment of acetylated proteins and peptides using a microchip technique. Poly (dimethylsiloxane) (PDMS) microfluidic channels were modified by passing an acidic solution of hydrogen peroxide through them. This resulted in hydrophilic silanol-covered surfaces onto which poly (diallyldimethylammonium chloride) (PDDA) can be coated. Protein A/G beads were then captured by the PDDA layer and antibodies can then be immobilized via the protein A/G. This technique enables efficient capture of antigens due to the optimal spacing and orientation of surface molecules. Two solutions, one containing 72.5 fmol?μL?1 of acetylated bovine serum albumin (BSA-Ac), the other 72.5 fmol?μL?1 of tryptic BSA-Ac digest were then enriched. High selectivities were obtained, and a 82.4 % recovery of the acetylated proteins was attained. This on-chip platform was then coupled to MALDI-MS to provide information on the acetylation sites of proteins and peptides. Additional peaks were observed in the mass spectra after enrichment and were assigned to acetylated peptides. This is significant with respect to understanding the mechanism and function of acetylation. In our opinion, this microchip-based technique has a large potential for detecting acetylated proteins and peptides in complex biological mixtures, and in acetylomics in general.
Figure
Figure A simple and novel strategy of microchip-based antibodies immobilization technique combined with advanced matrix-assisted laser desorption ionization mass spectrometry (MALDI-MS) has been developed for sensitive identification of acetylated proteins and acetylated sites.  相似文献   

9.
We report on a small (20?×?10 mm) micromachined device for the detection of gases in micro-gas chromatography (GC). It incorporates a micro-discharge across a 20-μm gap, and a remote electrode in the micro cavity that generates an electrical signal corresponding to the photo-ionization of gaseous analytes in a stream of carrier gas. Multi-component mixtures were detected and the results compared to those obtained with a flame ionization detector. The minimum detectable limit is 350 pg.μL?1 of n-octane in air when applying a 1.4 mW discharge. The combination of wet etching of glass (as used for microfluidic channels) with a lift-off process for detector electrodes by a robust batch process results in a universal, non-destructive, and sensitive microdetector for micro-GC.
Figure
?  相似文献   

10.
We have developed two methods for the quantitation of gabapentin in human plasma. They are based on capillary electrophoresis with laser-induced fluorescence detection (CE-LIF) with and without solid-phase extraction (SPE) and the derivatizing reagent 5-(4,6-dichlorotriazinyl)amino fluoresencin. The conditions for derivatization, separation and extraction were investigated in detail, and the optimal labeling conditions include a temperature of 40?°C, a reaction time of 30?min, and the use of a borate buffer of pH 9.0 as the reaction medium. A borate buffer of pH 9.2 served as a background electrolyte for CE separations. The CE-LIF and SPE-CE-LIF methods have linear ranges of 5–200?nmol?L?1 and 0.2–10?nmol?L?1, respectively, and the limits of detection are 0.5 and 0.02?nmol?L?1, respectively. The SPE-CE-LIF method was successfully applied to the determination of gabapentin in blood plasma samples.
Figure
Two methods have been developed for the quantization of gabapentin (GBP) in human plasma. They are based on capillary electrophoresis-laser induced fluorescence detection (CE-LIF) with and without solid-phase extraction (SPE) and the derivatizing reagent 5-(4,6-dichlorotriazinyl)aminofluorescein.  相似文献   

11.
A new simple and sensitive method has been developed for the determination of trace levels of inorganic species in environmental water samples. It is based on the use of supramolecular?Cbased dispersive liquid?Cliquid microextraction (SM?CDLLME) prior to microsample introduction into FAAS. The ions are micro?Cextracted with coacervates composed of reverse micelles made from decanoic acid and dispersed in tetrahydrofuran?Cwater mixtures. Cobalt ion was used as a model ion, and 1?C (2?Cpyridylazo)?C2?Cnaphthol as the complexing agent. SM?CDLLME results from a combination of DLLME with coacervation?Cbased microextraction. It combines the advantages of DLLME with those of preconcentration based on coacervation and reverse micelles. Factors affecting the extraction efficiency of Co and its subsequent determination by FAAS were optimized. Under the optimized conditions and using 5.00?mL sample only, the enhancement factor is 58, the limit of detection is 4.2???g L?C1, and the relative standard deviations for 100???g L?C1 and 30???g L?C1 of Co are 2.1% and 3.8%, respectively (n?=?6). The accuracy of the method was confirmed by parallel analyses using the ASTM reference method.
Schematic representation SM?CDLLME enrichment method (Supramolecular assemblies were hired as extraction media in dispersive liquid?Cliquid microextraction. This method is based on microextraction of analytes with coacervates made up of decanoic acid reverse micelles dispersed in tetrahydrofuran (THF)?Cwater. Hazardous organic solvents as the microextraction solvent were avoided)  相似文献   

12.
We present a study on the application of magnetic nanoparticles (MNPs) prepared from Fe3O4 and functionalized with pyridine as an adsorbent for the solid-phase extraction of trace quantities of Pd(II) ion. The pyridine group was immobilized on the surface of the MNPs by covalent bonding of isonicotinamide. The modified MNPs can be readily separated from an aqueous solution by applying an external magnetic field. Effects of pH, the amount of functionalized MNPs, extraction time, type and quantity of eluent, desorption time, break-through volume and interfering ions on the extraction efficiency were optimized. The amount of Pd(II) was then determined using FAAS. Under the optimized conditions, the detection limit and preconcentration factor are 0.15?μg?L-1 and 196, respectively, and the relative standard deviation (at 20?μgL?1; for n?=?10) is 3.7?%. The method had a linear analytical range from 1 to 80?μg?L-1 and was applied to determine Pd(II) in spiked tape water and soil.
Figure
?  相似文献   

13.
We report on a simple amperometric detector for use in microchip capillary electrophoresis. A disposable syringe serves as the electrode holder that is fixed at the outlet of the separation channel. A carbon paste electrode is used to detect dopamine (DA) and catechol (CA) after electrophoretic separation. The two model analytes were well separated within 60 s. The response is linear in the concentration range from 4 to 500???M, and the detection limit is 1.2???M for DA (S/N = 3:1). The relative standard deviations of the inter-run and inter-electrode peak currents, respectively, are 2.8% and 5.7% for DA, and 3.9% and 6.5% for CA. Favorable column efficiency (expressed by the theoretical plate number which is 5.3 × 104 m-1 for DA) is achieved. The method was successfully applied to the separation and detection of 3-aminophenol (3-AP) in an injection powder containing sodium 4-aminosalicylate. The detection limit of 3-AP is as low as 1.7???M, which meets the demand of the impurity test. The facile assembly allows convenient replacement of working electrodes and improves the longevity of the microanalytical system.
Figure
Voltammetric behaviors of 3-AP and 4-AS at carbon paste electrode (CPE), and microchip electrophoresis-amperometry with CPE for the two analytes.  相似文献   

14.
We have developed a method, termed solidification of floating organic drop microextraction (SFOME), for the extraction of polybrominated diphenyl ethers (PBDEs) in water and urine samples, this followed by quantification via HPLC. This method requires very small quantities of organic solvent consumption. It is based on exposing a floating solidified drop of an organic solvent on the surface of aqueous solution in a sealed vial. The organic drop is easily collected with a spatula, molten (at ambient temperature), and then submitted to HPLC. Experimental parameters including extraction solvent and its volume, disperser solvent and its volume, extraction time, ionic strength, stirring speed and extraction temperature were optimized. The enrichment factors of analytes are in the range from 921 to 1,462, and acceptable extraction recoveries (92%–118%) are obtained. The dynamic linear range for five PBDE congeners is in the range of 0.5–75?μg.L?1 and from 5 to 500?μg.L?1 for BDE 209. The correlation coefficients range from 0.9960 to 0.9999. The limits of detection (at S/N?=?3) for PBDE congeners vary between 0.01 and 0.04?μg.L?1. This method has been successfully applied to detecting PBDEs in two environmental waters and in human urine.
Figure
Under optimized conditions, the enrichment factors of PBDEs by solidification of floating organic drop microextraction were from 921 to 1,462, and extraction recoveries (92%–118%) were obtained. The correlation coefficients ranged from 0.9960 to 0.9999. The limits of detection (at S/N?=?3) for PBDE congeners varied between 0.01 and 0.04?μg.L?1.  相似文献   

15.
We report on a new kind of non-covalent multi-label electrochemical immunoassay that was applied to simultaneously quantify the tumor markers CA15-3 and CA19-9. The method employs a nanohybrid composed of an ionomer and conductive titanium dioxide nanoparticles that act as a matrix support for the antibodies. The two antibodies (anti-CA153 and anti-CA199) were labeled (a) with a cobaltous dipyridine complex, and (b) with methylene blue. Labeling is based on cation-exchange interaction rather than on covalent conjugation. The redox potentials of the two labels are separated by an interval of 0.3 V. The resulting sandwich-type immunosensor was read out by differential pulse voltammetry. The potential sites and currents of the two redox probes reflect the concentration of the two analytes. The two analytes were determined with a detection limit of 1.6 U?mL?1 for CA19-9, and of 0.3 U?mL?1 for CA15-3.
Figure
A new non-covalent multi-label electrochemical immunoassay was applied to simultaneously quantify dual tumor markers. DPV performed the identification and quantification of dual analytes on same electrode surface.  相似文献   

16.
A method using on-line solid-phase microextraction (SPME) on a carbowax-templated fiber followed by liquid chromatography (LC) with ultraviolet (UV) detection was developed for the determination of triclosan in environmental water samples. Along with triclosan, other selected phenolic compounds, bisphenol A, and acidic pharmaceuticals were studied. Previous SPME/LC or stir-bar sorptive extraction/LC-UV for polar analytes showed lack of sensitivity. In this study, the calculated octanol–water distribution coefficient (log D) values of the target analytes at different pH values were used to estimate polarity of the analytes. The lack of sensitivity observed in earlier studies is identified as a lack of desorption by strong polar–polar interactions between analyte and solid-phase. Calculated log D values were useful to understand or predict the interaction between analyte and solid phase. Under the optimized conditions, the method detection limit of selected analytes by using on-line SPME-LC-UV method ranged from 5 to 33 ng?L?1, except for very polar 3-chlorophenol and 2,4-dichlorophenol which was obscured in wastewater samples by an interfering substance. This level of detection represented a remarkable improvement over the conventional existing methods. The on-line SPME-LC-UV method, which did not require derivatization of analytes, was applied to the determination of TCS including phenolic compounds and acidic pharmaceuticals in tap water and river water and municipal wastewater samples.
Figure
Schematic diagram of the On-line solid-phase microextraction  相似文献   

17.
The interaction between papain and two typical ionic liquids (ILs), 1-octyl-3-methylimidazolium chloride ([C8mim]Cl) and 1-butyl-3-methylimidazolium chloride ([C4mim]Cl), was investigated by using fluorescence spectroscopy technique at a pH value of 7.4. The results suggested that ILs could quench the intrinsic fluorescence of papain probably via a static quenching mechanism. The binding constants were determined by employing the fluorescence quenching method. They were very small compared with that of volatile organic solvents, indicating that only very weak interaction between ILs and papain existed. The Gibbs free energy change (?G), enthalpy change (?H), and entropy change (?S) during the interaction of papain and ILs were estimated. Negative values of these parameters indicated that the interaction between ILs and papain was a spontaneous process, also implying that hydrogen bonding and van der Waals forces played important roles in the interaction processes.
Figure
Three-dimensional fluorescence spectrum of papain (0.2?g?L-1)  相似文献   

18.
We have developed a simple method for the microextraction of the carbamate pesticides carbofuran, pirimicarb, and carbaryl. It is termed ionic liquid magnetic bar microextraction (ILMB-ME) and based on an ionic liquid deposited on a magnetic stirrer bar placed in a sealed short PCR tube into which microholes where pinned. When placed in a vial containing the aqueous sample solution, the ILMB tumbles freely in the aqueous solution and the carbamates are extracted into the ionic liquid phase which then was determined by HPLC. The enrichment factors for carbofuran, pirimicarb, and carbaryl are 107, 94, 95, respectively. The limits of detection, calculated as three times the signal-to-noise ratio (S/N), are 1.4?μg?L?1 for carbofuran, 3.4?μg?L?1 for pirimicarb, and 1.7?μg?L?1 for carbaryl. The repeatability, carried out by extracting water samples spiked with carbamate levels of 200?μg?L?1, yielded relative standard deviations between 2.9 and 6.0?%, (for n?=?5). The recoveries of all the three fungicides from tap, lake and rain water samples at spiking levels of 5 and 50?μg?L?1 are in the range from 86 to 98?%, and from 80 to 96?%, respectively. We conclude that this is a simple, practical and efficient method for the determination of fungicide residues in real water samples.
Figure
?  相似文献   

19.
We report on a new method for sample pretreatment. It is based on solid-phase extraction combined with dispersive liquid-liquid microextraction (SPE-DLLME) and was applied to the determination of carbamates in apple and cucumber. The carbamates carbofuran, carbaryl, and pirimicarb were first extracted from samples by SPE. The analytes were then eluted from the sorbent with acetonitrile, and the DLLME technique was then applied to the resulting eluate. Finally, the analytes in the extraction solvent were determined by HPLC. Several parameters affecting the SPE-DLLME process were optimized. The new method provides enrichment factors that range from 5,400 to 7,650. Calibration plots are linear in the range from 0.25 to 100?μg?kg?1 for carbofuran and carbaryl, and from 0.10 to 100?μg?kg?1 for pirimicarb, with correlation coefficient (r2) ranging from 0.9980 to 0.9997. The limits of detection range from 5 to 60?pg?kg?1 (at S/N?=?3). The method was successfully applied to the extraction and sensitive determination of carbamates in apple and cucumber samples.
Graphical abstract
Chromatograms of non-spiked apple sample with the treatment of SPE-DLLME (1), apple sample spiked with carbamates at the concentration of 10.0 μg kg-1 without (2) / with (3) the treatment of SPE-DLLME.  相似文献   

20.
We describe a method for the determination of inorganic selenium in water samples via gas-phase chemiluminescence (GPCL). Se(IV) was first derivatized with 4-nitro-o-phenylenediamine to form 5-nitropiazselenol. The latter was decomposed by persulfate through photocatalytic oxidation to give Se(VI), which was reduced to Se(IV). Selenium hydride was generated from Se(IV) through reduction with sodium borohydride and then preconcentrated using cryotrapping. The cryotrapped hydride was evaporated and carried to a reaction chamber by a stream of helium, where it produced GPCL as a result of ozonation. The method exhibits a wide linear calibration range (from 0.5?μg?L?1 to 1.0?mg?L?1) with a detection limit of 0.12?μg?L?1 (for n?=?11), and a relative standard deviation of 3.90?% (at n?=?11) at 5.0?μg?L?1 level of selenium. The method was applied to the determination of inorganic selenium in water samples and gave satisfactory results.
Figure
A GPCL detection system is developed for the determination of inorganic selenium in water samples. By using analytical technique in this figure, such as derivatization, UV/ S2O 8 2- decomposition, stopped-flow injection and cryotrapping, the system can separate and preconcentrate the analyte from the matrix, then produce GPCL as a result of ozonation. The method was simple, sensitive with low-cost instrumentation.  相似文献   

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