Abstract

Permanent modifiers (V, Ir, Ru, V–Ir, V–Ru, and W–V) thermally coated on to platforms of pyrolytic graphite tubes were employed for the determination of Cd, Pb, and Zn in botanic and biological slurries by electrothermal atomic absorption spectrometry (ETAAS). Conventional Pd + Mg(NO 3) 2 modifier mixture was also used for the determination of analytes in slurries and digested samples. Optimum masses and mass ratios of permanent modifiers for Cd, Pb, and Zn in slurry sample solutions were investigated. The 280 μg of V, 280 μg of V + 200 μg of Ir, 280 μg of V + 200 μg of Ru or 240 μg of W + 280 μg of V in 0.2% (v/v) Triton X-100 plus 0.5% (v/v) HNO 3 mixture was found as efficient as 5 μg of Pd + 3 μg of Mg(NO 3) 2 modifier mixture for obtaining thermal stabilization, and for obtaining best recoveries. Optimization conditions of analytes, such as pyrolysis and atomization temperature, characteristic masses and detection limits, and atomization and background peak profiles were studied with permanent and 5 μg of Pd + 3 μg of Mg(NO 3) 2 conventional modifiers and compared with each other. The permanent V–Ir, V–Ru, and W–V modifiers remained stable for approximately 250–300 firings when 20 μl of slurries and digested samples were delivered into the atomizer. In addition, the mixed permanent modifiers increase the tube lifetime by 50–95% when compared with untreated platforms. The characteristic masses and detection limits of analytes (dilution factor of 125 ml g −1) obtained with V–Ir based on integrated absorbance as example for 0.8% (m/v) slurries were 1.0 pg and 3 ng g −1 for Cd, 18 pg and 17 ng g −1 for Pb, and 0.7 pg and 4 ng g −1 for Zn, respectively. The results of analytes obtained by employing V–Ir, V–Ru, and W–V permanent modifier mixtures in botanic and biological certified and standard reference materials were in agreement with the certified values of reference materials.

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