Abstract:Here was demonstrated for the first time a possible application of abrasive stripping voltammetry in the direct measurement of trace metals in anoxic, sulfidic marine sediments (peloid mud) from a small and shallow (0.2 -1 m) marine lagoon in Central Dalmatia, Croatia. Trace amounts of sample compounds are transferred to the graphite electrode surface and electrochemical reduction or oxidation processes are followed by the cyclic voltammetry in seawater or 0.55 M NaCl as electrolyte. After a preelectrolysis at… Show more
“…Such behavior has been assigned to the complex voltammetry exhibiting characteristics of both adhered and solution phase electrochemistry involving oxidation/dissolution of adhered and reduced species [14]. During negative-going scans that were started from 0 V, a single peak appeared (Fig.…”
Section: Methodsmentioning
confidence: 99%
“…We have encountered the problem of FeS solid phase electrochemistry when we investigated sulfidic natural samples at paraffin-impregnated graphite electrodes (PIGEs). It became evident that it is impossible to understand the behavior of these systems without a detailed study of the redox processes of different Fe, Fe(I), Fe(II) and FeS phases [14]. Recently, it has been shown that different particulate metal-sulfide species are electroactive on the HMDE by producing cathodic peaks situated at around À 1.0 V (vs. Ag/AgCl) i.e., situated similarly to ones reported for FeS aq species [15 -17].…”
Electrochemical quartz crystal microbalance (EQCM) measurements were employed for studying of the redox processes of FeS microparticles immobilized on Au electrode surface in contact with aqueous solutions of NaCl, NaClNaHCO 3 , and NaCl-Na 2 S. The objective was to shed light on the complexity of the iron sulfide electrochemistry. For the sake of comparison electrochemical behavior of FeS suspension was also investigated on the paraffin-impregnated graphite (PIGE) and hanging mercury drop (HMDE) electrodes. In order to understand the complex nature of the redox transformations of FeS, Mohr-salt was dissolved in NaCl and NaCl-NaHCO 3 solutions, respectively, and the deposition-dissolution processes occurring in the course of the reduction of Fe(II) and reoxidation of Fe (0) were also monitored.
“…Such behavior has been assigned to the complex voltammetry exhibiting characteristics of both adhered and solution phase electrochemistry involving oxidation/dissolution of adhered and reduced species [14]. During negative-going scans that were started from 0 V, a single peak appeared (Fig.…”
Section: Methodsmentioning
confidence: 99%
“…We have encountered the problem of FeS solid phase electrochemistry when we investigated sulfidic natural samples at paraffin-impregnated graphite electrodes (PIGEs). It became evident that it is impossible to understand the behavior of these systems without a detailed study of the redox processes of different Fe, Fe(I), Fe(II) and FeS phases [14]. Recently, it has been shown that different particulate metal-sulfide species are electroactive on the HMDE by producing cathodic peaks situated at around À 1.0 V (vs. Ag/AgCl) i.e., situated similarly to ones reported for FeS aq species [15 -17].…”
Electrochemical quartz crystal microbalance (EQCM) measurements were employed for studying of the redox processes of FeS microparticles immobilized on Au electrode surface in contact with aqueous solutions of NaCl, NaClNaHCO 3 , and NaCl-Na 2 S. The objective was to shed light on the complexity of the iron sulfide electrochemistry. For the sake of comparison electrochemical behavior of FeS suspension was also investigated on the paraffin-impregnated graphite (PIGE) and hanging mercury drop (HMDE) electrodes. In order to understand the complex nature of the redox transformations of FeS, Mohr-salt was dissolved in NaCl and NaCl-NaHCO 3 solutions, respectively, and the deposition-dissolution processes occurring in the course of the reduction of Fe(II) and reoxidation of Fe (0) were also monitored.
“…Recently, during investigation of mercury electrode/sulfide anion/second metal ion system, it has been shown that different metal sulfide particles are electroactive on the Hg and paraffin impregnated graphite electrodes (PIGE) [20][21][22][23][24][25]. The results show the possibility of Hg electrode use for detection of calcogenide nanoparticles in natural samples by adsorptive cathodic stripping voltammetry [20][21][22][23][24][25].…”
A long-standing problem associated with voltammetric determination of iron and sulfide in reduced natural waters has been the nature of the presumed analyte responsible for a reduction peak at À1.1 V vs. Ag/AgCl. Cyclic voltammetry at the Hg electrode is used here to study solutions with different Fe(II) to sulfide ratios in chloride and acetate electrolytes (pH 6-7). The results indicate that the À1.1 V peak can be assigned to reduction of Fe 2 + or its labile complexes on FeS layers that partially cover the Hg electrode. Hg electrodes covered with FeS act like FeS solid electrodes over a very wide potential range (À0.35 to À1.9 V). Two mechanisms for forming FeS layers on Hg are described. Over the broadest deposition potential range, the dominant mechanism involves attachment at the Hg surface of FeS nanoparticles, which are generated quickly in initially supersaturated mixtures of Fe(II) and S(-II). In a narrow deposition potential range, roughly À0.56 to À0.70, FeS layers are produced additionally by replacement of preformed HgS. Because Fe 2 + is reduced at À1.1 V on FeS layers and at À1.4 V on bare Hg, it may be underdetermined when only the À1.4 V peak is measured.
“…It is important to mention that released Mn(II) after some short time is expected to oxidize and form nonelectrolabile colloidal manganese (IV) hydrous oxides, which normally constitutes the main fraction of manganese in oxic waters. To have a more complete knowledge about the speciation of manganese in such a system reaching equilibrium, a combination of the presented technique with, e.g., voltammetric analyses of the solid phase as reported in [50,51] could be interesting.…”
Detection of Mn(II) using differential pulse anodic stripping voltammetry (DPASV) on solid silver amalgam electrode is introduced. A well-defined peak for the oxidation of Mn(0) to Mn(II) was observed around À 1.45 V in NH 4 Cl (0.05 M) solution. Concentrations down to 1 mg/L were measured in NH 4 Cl (0.05 M) with 900 s deposition time at À 1.70 V, and good linearity was observed (r 2 avg ¼ 0.993) for standard additions in different concentration ranges (1 -3 mg/L, 10 mg/L -60 mg/L, and 50 mg/L -250 mg/L). For all measurements relative standard deviation was within 5% (n ¼ 9). Interactions between Mn and Cd, Ni, Cu, Pb and Zn were examined, and it was found that lead and nickel significantly interfere, while zinc, cadmium, copper, and mercury did not interfere within reasonable concentration ranges. The method was demonstrated for online detection of manganese in a contaminated river where the Mn(II) concentration varied between 3 and 15 mg/L. The relation between the Mn(II) concentration in the river water and the vessel traffic was observed due to the presence of high concentrations of Mn(II) in anoxic pore waters.
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