Quantification of phenylurea herbicides and their free and humic acid-associated metabolites in natural waters

Citation
A. Di Corcia et al., Quantification of phenylurea herbicides and their free and humic acid-associated metabolites in natural waters, J CHROMAT A, 852(2), 1999, pp. 465-474
Citations number
17
Categorie Soggetti
Chemistry & Analysis","Spectroscopy /Instrumentation/Analytical Sciences
Journal title
Volume
852
Issue
2
Year of publication
1999
Pages
465 - 474
Database
ISI
SICI code
Abstract
There is increasing interest in and demand for simultaneously monitoring pe sticides as well as related degradation products (DPs) in natural waters, a s the latter compounds can be even more toxic than the former ones. A metho d for determining parts per trillion levels of phenylurea herbicides and th eir DPs, that is their dealkylated forms and aromatic amines, is described. This method is based on solid-phase extraction with a Carbograph 4 cartrid ge followed by liquid chromatography (LC) with electrospray (ES) mass spect rometric detection. A study aimed at optimizing the response of the ES-MS d etector for very weakly basic chloroanilines was conducted. Results showed that ion signal intensities of the above species were dependent on the comp osition of the LC mobile phase to an astonishing degree. At concentration l evels of a few hundred ng/l, laboratory experiments showed that the aromati c amines considered here were mostly associated to dissolved humic acids (H As) by both reversible and irreversible bindings. The addition of a reducin g agent, i.e., NaBH4, succeeded in liberating that fraction of aromatic ami nes, which being reversibly bound to quinoidal structures of HAs are bioava ilable. Analyte recoveries were better than 85% on extraction from 4 l of d rinking water (spike level, 25 ng/l), 21 of ground water (spike level, 50 n g/l) and 0.5 l of river water (spike level, 200 ng/l). Relative standard de viations ranged between 4.6 and 20% for drinking water, 4.3 and 15% for gro und water, 5.9 and 13% for river water. Method detection limits calculated for drinking water, groundwater and surface water were between 3 and 11, 6 and 21, 36 and 75 ng/l, respectively. (C) 1999 Elsevier Science B.V. All ri ghts reserved.