Since the toxic effects of cadmium and its compounds are well known, the monitoring of this metal in body fluids is of substantial importance. The level of cadmium in urine is an important indicator of human exposure to this metal.Graphite-furnace atomic absorption spectrometry (GFAAS) has been widely used for the direct determination of Cd in urine, owing to its high sensitivity, speed and minimal contamination risks. However, the direct determination of Cd by GFAAS is not easy. Most of the difficulties can be explained by the combination of the matrix urine with a relatively high inorganic salt concentration and analyte, cadmium, that has a relatively high volatility. It can be concluded from recent studies that the most promising technique is to use matrix modifiers for volatilizing Cd at a temperature that leave inorganic salts in the graphite tube. Until now, several matrix modifiers, such as ammonium phosphates, ammonium nitrate and sulfate, magnesium nitrate, nitric acid, sodium hydroxide and palladium salts, have been used in the determination of Cd in various matrices by GFAAS.1-10 Among these modifiers, palladium, which was first reported by Shan and Ni 11 , has experienced increasing interest for the determination of volatile elements by GFAAS. 7-13 Recent studies have indicated that the stability effect of palladium for volatile elements is concerned with its metallic form.9,13-16 Therefore, palladium as a modifier is commonly used under reducing conditions. Palladium has been used with several reducing agents together, such as hydrazine, hydroxyl ammin hydrochloride and ascorbic acid. To the best of our knowledge, hitherto, palladium has not been combined with sodium azide as a reducing agent.The aim of present work was to experimentally evaluate the applicability of palladium combined with sodium azide for the determination of cadmium in urine.
Experimental
ApparatusA Hitachi (Model Z-8000) atomic absorption spectrometer with a Zeeman-effect background corrector equipped with a Hitachi Model graphite furnace atomizer (part No. 180-7400, uncoated tubes) was used through this work. The peak area (integrated absorbance) and peak height were automatically printed out and displayed using a Hitachi data processor. However, the peak-area absorbances were used to evaluate cadmium and the background absorbances. For cadmium, a hollow cathode lamp wavelength was set up 228.8 nm and a slit width to 0.7 nm. Argon served as a sheath gas at a flow rate of 200 ml min -1 . The absorbance of the atomization was measured without argon gas flow.Samples of 10 µl during the study were injected into the furnace using Eppendorf microliter pipettes with disposable polypropylene tips. The mass of the injected cadmium in the linear range of the calibration curve was 40 pg for optimization and comparison studies.
Reagents and solutionAll reagents were from E. Merck and of pro analysis grade. A stock solution of cadmium (200 mg A combination of palladium and sodium azide is proposed as a mixed modifier for cadmium determinat...