Derivatization of Amphetamine and Methamphetamine With 1,2-Naphthoquinone 4-Sulfonic Acid Into Solid-phase Extraction Cartridges. Determination of Amphetamine in Pharmaceutical and Urine Samples

The Analyst ◽  
1997 ◽  
Vol 122 (7) ◽  
pp. 673-677 ◽  
Author(s):  
Pilar Campíns Falcó ◽  
Carmen Molins Legua ◽  
Adela Sevillano Cabeza ◽  
Rosa Porras Serrano
Keyword(s):  
Solid Phase Extraction ◽  
Sulfonic Acid ◽  
Solid Phase ◽  
Urine Samples ◽  
Phase Extraction

Determination of Diclofenac in Urine Samples by Molecularly-Imprinted Solid-Phase Extraction and Adsorptive Differential Pulse Voltammetry

2007 ◽  
Vol 19 (15) ◽  
pp. 1555-1561 ◽  
Author(s):  
Laura Fernández-Llano ◽  
M. Carmen Blanco-López ◽  
M. Jesús Lobo-Castañón ◽  
Arturo J. Miranda-Ordieres ◽  
Paulino Tuñón-Blanco
Keyword(s):  
Solid Phase Extraction ◽  
Differential Pulse Voltammetry ◽  
Solid Phase ◽  
Differential Pulse ◽  
Urine Samples ◽  
Phase Extraction ◽  
Molecularly Imprinted ◽  
Pulse Voltammetry

Determination of Phenol Sulfone, Phenol Sulfoxide, and Phenol Sulfonic Acid Metabolites of Fenamiphos in Soil by Liquid Chromatography

1995 ◽  
Vol 78 (5) ◽  
pp. 1286-1293
Author(s):  
Gregory C Mattern ◽  
Gilbert D Parker ◽  
Debra L Green ◽  
Gregory L Yeutter
Keyword(s):  
Liquid Chromatography ◽  
Solid Phase Extraction ◽  
Sulfonic Acid ◽  
Solid Phase ◽  
Reversed Phase ◽  
Uv Detection ◽  
Phase Extraction ◽  
Soil Matrix ◽  
Phase Liquid

Abstract An analytical method has been developed to quantitate fenamiphos phenol sulfone, phenol sulfoxide, and phenol sulfonic acid in soil. Both control and analyte-fortified soil samples from Fresno, CA, were extracted with methanol–water (2 + 1) and partitioned with ethyl acetate. Fenamiphos phenol sulfone and phenol sulfoxide were determined by re-versed-phase liquid chromatography (LC) with UV detection at 240 nm after cleanup by silica solid-phase extraction. Fenamiphos phenol sulfonic acid was determined by reversed-phase ion-pairing LC with UV detection at 240 nm after cleanup by amino solid-phase extraction. Recoveries of fenamiphos phenol sulfoxide ranged from 88.2 to 111.0%, with an average of 97.4%. Recoveries of fenamiphos phenol sulfone ranged from 101.6 to 107.0%, with an average of 104.6%. Recoveries of fenamiphos phenol sulfonic acid ranged from 76.0 to 99.9%, with an average of 86.0%. Responses for analysis of analytes in both solvent and soil matrix were linear over the tested range of 10 to 500 ppb. Limits of determination of each analyte in soil were less than 10 ppb.

scholarly journals Dispersive Solid-Phase Extraction using Magnetic Carbon Nanotube Composite for the Determination of Emergent Mycotoxins in Urine Samples

Toxins ◽  
2020 ◽  
Vol 12 (1) ◽  
pp. 51 ◽  
Author(s):  
Arroyo-Manzanares ◽  
Peñalver-Soler ◽  
Campillo ◽  
Viñas
Keyword(s):  
Carbon Nanotube ◽  
Solid Phase Extraction ◽  
High Resolution Mass Spectrometry ◽  
Solid Phase ◽  
Urine Samples ◽  
Sample Treatment ◽  
Phase Extraction ◽  
X Ray ◽  
Relative Standard

Dispersive magnetic solid-phase extraction (DMSPE) has received growing attention for sample treatment preconcentration prior to the separation of analytes due to its many advantages. In the present work, the potential of DMSPE for the determination of emergent mycotoxins (enniatins A, A1, B and B1, and beauvericin) is investigated for the first time. Different magnetic nanoparticles were tested and a magnetic multiwalled carbon nanotube (Fe3O4@MWCNT) composite was selected for the extraction and preconcentration of the five target mycotoxins in human urine samples before their analysis by ultrahigh performance liquid chromatography coupled to high resolution mass spectrometry (UHPLC-HRMS). The nanocomposite was characterized by energy dispersive X-ray spectrometry, scanning electron microscopy, Fourier transform infrared spectrophotometry, and X-ray diffraction. Several parameters affecting the adsorption and desorption of DMSPE steps were optimized and the method was fully validated. Due to a matrix effect, matrix-matched calibration curves were necessary to carry out quantification. In this way, limits of quantification of between 0.04 and 0.1 μg/L, relative standard deviation values lower than 12% and recoveries between 89.3% and 98.9% were obtained. Finally, a study of the reuse of the Fe3O4@MWCNT composite was carried out, confirming that it can be reused at least four times.

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