The determination of trace amounts of lead in environmental samples is currently of great importance due to their high toxicity, accumulative and persistent character in the environment and living organisms. Thus, there is great interest concerning the implementation of a reliable preconcentration system for lead(II) for analytical determinations. At the moment, one of the most used matrix removal preconcentration methods is the on-line retention of the analyte on an adequate solid support by using microcolumns in a flow system, based on mass transfer between a liquid phase and a solid one. 1 These preconcentration systems can be on-line coupled to several atomic detection techniques.Flame atomic absorption spectrometry (FAAS) is a simple and very available technique for the determination of heavy metals in water samples. However, the main problem is a low sensitivity for trace metal at the ng/ml level. This limitation can be overcome by using a preconcentration procedure.Solid-phase extraction (SPE) techniques have found increasing applications for the preconcentration of trace metal ions and the elimination of matrix interference prior to an AAS analysis. Activated carbon is one of the sorbent materials that have been used as collectors for trace elements.2-4 Solid-phase extraction procedures based on the sorption of metal complexes on activated carbon have been widely applied. [2][3][4][5][6] In most of the previous studies, metal complexes were collected on activated carbon as a filter. Then, the preconcentrated trace metals on the filter were recovered by treating with suitable solvents, such as nitric acid. Thus, the prepared activated carbon filter was used only for one analysis. Several complexing agents have been used in the adsorption process on activated carbon, including dithiozone, 7 dithiocarbamate derivatives, 8,9 1-(2-pyridylazo)2-naphthol, 10,11 resorcinol derivatives, 12 1-nitrous-2-naphtol, 13 o,o-diethyldithiophosphate 14,15 and pyrocatechol violet. 16 In all of these methods, a ligand solution was needed for each experiment, because, the chelating agent was used to wash metal ions from the surface of sorbent.In this paper, a new on-line column separationpreconcentration method is described for the determination of Pb(II) by using active carbon loaded with Pyrogallol Red (PGR) and FAAS. Active carbon tightly adsorbed Pyrogallol Red and thus the adsorbed Pyrogallol Red did not wash away with the washing solution that was used to remove lead(II) ions from the column. Automation of the procedure can possibly reduce the risk of operational errors, increase the precision of the method and accelerate the sample throughput. 17
Experimental
Reagents and chemicalsAll solutions were prepared with doubly distilled water, unless otherwise stated. A Pyrogallol Red (PGR) solution was prepared by dissolving a suitable amount of PGR (Merck) in a water/ethanol (50:50 v/v) mixture. A buffer solution (0.1 M) was prepared by adding an appropriate amount of NaOH to a potassium hydrogen phthalate solution for pH 3...