Solid phase extraction of halogenated, organophosphorus and nitrogen-containing pesticides from river water samples. Analytical quality parameters.

Citation
Me. Baez et al., Solid phase extraction of halogenated, organophosphorus and nitrogen-containing pesticides from river water samples. Analytical quality parameters., BOL SOC CH, 44(2), 1999, pp. 217-226
Citations number
26
Categorie Soggetti
Chemistry
Journal title
BOLETIN DE LA SOCIEDAD CHILENA DE QUIMICA
ISSN journal
03661644 → ACNP
Volume
44
Issue
2
Year of publication
1999
Pages
217 - 226
Database
ISI
SICI code
0366-1644(199906)44:2<217:SPEOHO>2.0.ZU;2-O
Abstract
A study of matrix effects arising from river water samples using C18 SPE co lumns in the determination of 38 pesticides having different chemical prope rties is presented. Recoveries from river water samples of different origin and the influence of prefiltration step, pH and ionic strength were tested . A calibration equation for the extraction method was calculated by using the statistical method of linear regression, the independent variable being the amount of analyte added and the dependent variable, the amount of reco vered analyte. Extractions were carried out in waters spiked with 65 to 160 0 ng L-1 of organophosphorus and nitrogen-containing pesticides, and with 1 2.5 to 320 ng L-1 of halogenated pesticides. Only trifluralin, captan, aldr in, tri-allate, alpha-BHC, gamma-BHC, and azinphos-methyl behavior could no t be described through a linear relationship due to low precision and, poss ibly, to interferences caused by the matrix sample. Linearity, analytical s ensitivity, precision and limit of detection were established for 31 compou nds. Slope values in the regression equation ranged from 0.68 to 0.98, the exception being amitraz (0.43), dieldrin (0.51), and 4,4' DDT (0.58), which accounted for losses produced in the extraction process. Systematic errors were detected for most of the compounds and they could be corrected by usi ng the calibration data obtained for the whole analytical process. The dete ction limits established through the model in most of the cases were lower than the maximum allowed limit for waters by the European Union (100 ng L-1 ), ranging from 7 to 21 ng L-1 for pesticides determined by GC-ECD, and fro m 20 to 102 ng L-1 (except triadimefon, 220), for those determined by GC-NP D.