Aluminium speciation: Variations caused by the choice of analytical method and by sample storage
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Abstract
We have compared a new FIA method (M1) for aluminium speciation in natural waters and a manual one based on one of Driscoll's proposals (M2). In synthetic solutions, aluminium's fluoro complexes were measured as ‘labile monomeric AP (Al i ) by M2, but not as ‘quickly reacting Al’ (Al qr ) by M1. Aluminium's complexes with Nordic Reference Humic Acid were measured neither as Al i nor as Al qr , and the same result was obtained for Al's citrato complexes. After excluding aluminium's fluoro complexes from Al i , the results of the two methods agreed well for soil leaching samples and fairly well for natural water samples. Detection limits: 10μg L−1 (ca. 0.4 μM) for both methods. Sample throughputs: M1∶66 injections h−1; M2∶5 samples h−1. Repeatabilities (RSD) on natural water samples: M1∶0.6–5.8% and M2 0.7–4.6%.
Sample storage studies on soil solutions (FIA method) indicated that storage effects were ‘sample type specific’. A sample with a low level of Al qr and a high DOC level (P2A) was more sensitive to storage than one with a high [Al] qr and a low [DOC] (P2B*). The decrease in [Al] qr was statistically significant after 10 h (P2A) and 24 h (P2B*), respectively. After 3 days' storage, [Al] qr had decreased by some 40% in P2A, while the decrease in P2B* was less than 10% after 8 days. The results of this part of the study also emphasize the importance of careful method standardization in sample storage studies.
Keywords
Leaching Humic Acid Soil Solution Fluoro Reference HumicPreview
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