The application of strongly reducing agents in flow injection analysis: Part 4. Uranium(III)

The application of uranium(III) in acidic medium as a powerful reducing reagent in flow injection analysis in detail. Results of the determination of a number of organic and inorganic substances are presented. With spectrophotometric detection based on the absorption by uranium(III) at 350 nm, limits of determination were of the order of 10^?5 mol 1^?1. For nitrate and nitrite, similar limits of determination were achieve with amperometric detection. This limit of determination is lower than in the case of chromium(II) and vanadium(II).     

The application of strongly reducing agents in flow injection analysis : Part 3. Vanadium(II)

The application of vanadium(II) as a powerful reducing reagent in flow injection analysis is described. Results are presented for the determination of various organic and inorganic substances. With spectrophotometric detection, based on the absorption by vanadium(II)-EDTA at 350 nm, limits of determination were about 5 X 10^?5 mol 1^?1. Nitrate, nitrite and hydroxylamine were measured with amperometric detection. The limit of determination was about the same as with spectrophotometric detection. In a slightly acidic medium, hydrazine could be determined with the amperometric detector, with a limit of determination of about 10^?4 mol l^?1. By coupling an ammonia detection device to the reduction system, the percentage conversions of nitrate, nitrite and hydroxylamine to ammonia were shown to be 26%, 54% and 47%, respectively.     

The application of strongly oxidizing agents in flow injection analysis : Part 3. Cobalt(III)

The application of cobalt(III) as a powerful oxidizing agent in flow injection analysis is described. Cobalt(III) is electrochemically generated in the flowing system at a working electrode consisting of a packed bed of gold powder. Depending on the analyte, spectrophotometric detection is at 605 nm or 320 nm. For the oxidizable organic and inorganic substances tested, linear responses are usually obtained in ranges around 10^?3 mol l^?1.     

The application of strongly oxidizing agents in flow injection analysis : Part 2. Manganese(III)

The application of manganese(III) as a powerful oxidizing agent in flow injction analysis is described. Manganese(III) is generated electrochemically in the flowing system at a working electrode consisting of a packed bed of gold powder. Spectrophotometric detection is used at 490 nm, where manganese(III) in sulphuric acid solution absorbs strongly. Undr the experimental conditions, the generation of manganese(III) can be accompanied by generation of manganese(IV) and permanganate; manganese(III) alone can be generated by a proper selection of the generating current and the flow rate. Results are presented for the determinatin of various organic and inorganic substances by means of manganese(III), usually at concentrations in the 10^?4—10^? mol l^?1 range. Unlike permanganate and manganese(IV), manganese(III) does not react with chloride, so that oxidizable compounds can be determined in the presence of large amounts of this species.     

The application of strongly reducing agents in flow injection analysis: Part 1. Chromium(II) and vanadium(II)

Many reagenst cannot easily be applied in quantitative analysis, because of their instability under atmospheric conditions. When such reagents are prepared in a flowing stream, their applicability is very promising; for example, in flow injection analysis, a reagent need be stable only for 20–30 s. The application of chromium(II) and vanadium(II) in flow injection analysis is described. Nitrate and nitrile can be determined in the concentration range 5 × 10^?5?5 × 10^?3. Calibration graphs show good linearity.     

The application of strongly oxidizing agents in flow injection analysis : Part 4. Manganese(VI) and Copper(III)

The application of manganese(VI) and copper(III) in strongly alkaline solutions as strong oxidizing reagents in flow injection analysis is described. Both reagents were prepared under batch conditions and fed to the flow from a stock solution. The reactions of most analytes tested with manganese(VI) required the use of a heated (65° C) reaction coil. The main application appears to be for the determination of monosaccharides in the 10^?4–10^?5 mol l^?1 range.     

The application of strongly reducing agents in flow injection analysis : Part 5. Chromium(II) and vanadium(II) in acidic medium

Chromium(II) and vanadium(II) in acidic medium are applied as powerful reducing agents in flow injection analysis. Detection is done amperometrically. For the determination of nitrite with chromium(II), the limit of determination is 5 × 10^?6 mol l^?1 with a linear range up to 7.5 × 10^?5 mol l^?1, similar to the case of uranium(III). Vanadium(II) is less suitable for the determination of nitrite. Nitrate, hydroxylamine and hydrazine could not be determined with these reagents.     

The Application of strongly oxidizing agents in flow injection analysis : Part 1. Silver(II)

The application of silver(II) as a powerful oxidizing reagent in flow injection analysis is described in detail. Under the experimental conditions, the half-life of the very unstable silver(II) was about 120 s. Nevertheless, various organic and inorganic substances could be determined. Spectrophotometric detection was at 390 nm where silver(II) in nitric acid solutions absorbs strongly. As neither iron(III) nor copper(II) reacts with silver(II), oxidizable compounds can be determined in the presence of large amounts of these species. Special attention is given to manganese(II), which can be determined selectivity by this method in the range 10^?5–10^?4 mol l^?1.     

Differential kinetic analysis and flow injection analysis: Part 2. The (2.2.1) Cryptates of Magnesium and Calcium

Simultaneous differential kinetic analysis for magnesium and calcium ions in solution has been adapted to the flow injection system. The two-point kinetic assay is based on dissociation of the cryptand (2.2.1) complexes of magnesium and calcium ions with sodium ion as scavenger. The ions could be determined reproducibly with phthalein complexone as indicator, at a sampling rate of 80 samples per h with 200-μl sample injections and low reagent consumption. Rules derived from f.i.a. theory were confirmed experimentally.     

Catalytic-fluorimetric determination of EDTA and iron(III) by flow injection analysis

Summary In this paper the authors report on several methods for the direct determination of EDTA and indirect determination of iron(III), based on the inhibition effect of EDTA on the catalytic action of copper (II) on the oxidation of 2,2-dipyridyl ketone hydrazone by hydrogen peroxide and on the decrease of this inhibition effect in the presence of Fe(III), respectively. These methods allow the determination of EDTA in the ranges of 0.4–2.0 g · ml^–1 and 0.2–1.0 g · ml^–1 for the normal and reversed FIA modes, respectively, and of 40–240 ng · ml^–1 for Fe(III) by reversed FIA.

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Katalytisch-fluorimetrische Bestimmung von EDTA und Eisen(III) durch FließinjektionsanalyseInhibitionsmethoden

Zusammenfassung Verfahren zur direkten Bestimmung von EDTA sowie zur indirekten Bestimmung von Eisen(III) werden beschrieben. Sie beruhen auf der Inhibitorwirkung von EDTA auf den katalytischen Effekt von Kupfer(II) bei der Oxidation von 2,2-Dipyridylketonhydrazon mit Wasserstoffperoxid bzw. auf der Schwächung dieser Inhibitorwirkung in Gegenwart von Eisen(III). Es ist mit diesen Methoden möglich, EDTA im Bereich von 0,4–2,0 g/ml (normale FIA) bzw. 0,2–1,0 g/ml (umgekehrte FIA) und Eisen im Bereich von 40–240 ng/ml (umgekehrte FIA) zu bestimmen.

     

On-line solid-phase extraction and multisyringe flow injection analysis of Al(III) and Fe(III) in drinking water

A new analytical method was developed for on-line monitoring of residual coagulants (aluminium and iron salts) in potable water. The determination was based on a sequential procedure coupling an extraction/enrichment step of the analytes onto a modified resin and a spectrophotometric measurement of a surfactant-sensitized binary complex formed between eluted analytes and Chrome Azurol S. The optimization of the solid phase extraction was performed using factorial design and a Doehlert matrix considering six variables: sample percolation rate, sample metal concentration, flow-through sample volume (all three directly linked to the extraction step), elution flow rate, concentration and volume of eluent (all three directly linked to the elution step). A specific reagent was elaborated for sensitive and specific spectrophotometric determination of Al(III) and Fe(III), by optimizing surfactant and ligand concentrations and buffer composition. The whole procedure was automated by a multisyringe flow injection analysis (MSFIA) system. Detection limits of 4.9 and 5.6 μg L⁻¹ were obtained for Al(III) and Fe(III) determination , respectively, and the linear calibration graph up to 300 μg L⁻¹ (both for Al(III) and Fe(III)) was well adapted to the monitoring of drinking water quality. The system was successfully applied to the on-site determination of Al(III) and Fe(III) at the outlet of two water treatment units during two periods of the year (winter and summer conditions).     

The fluoride ion-selective electrode in flow injection analysis : Part 3. Applications

Flow-injection potentiometry with a combination fluoride-selective electrode is used to determine fluoride in tap water, beverages and urine. Excellent sensitivity (down to 1 μg l^?1) and long-term stability are obtained, with a sample throughput of 30–40 h^?1, based on triplicate injections at 120 h^?1. The commonly used buffer TISAB-III is unsuitable for the analysis of undiluted tea and urine samples. The application of a modified citrate-containing TISAB overcomes interferences caused by high natural ionic strength and avoids complexation of fluoride. Recoveries after spiking tap water, tea and urine with fluoride concentration ranging from 0.01 to 1 mg l^?1 are in the range 91–106%. The equipment used provides a flexible system allowing fast changes between different buffers and carrier streams depending on the samples presented.     

Simultaneous spectrofluorimetric determination of cerium(III) and cerium(IV) by flow injection analysis

Cerium(III) (1–100 μg l^?1) is determined by injection into a carrier stream of hydrochloric, perchloric or sulphuric acid, and monitoring its native fluorescence. Cerium(IV) can be determined similarly by incorporating a zinc reductor minicolumn into the system. Splitting the injection sample so that only part passes through the reductor, and the remainder by-passes it, allows total cerium and cerium(III) to be detected from the two sequential fluorescence peaks obtained.     

Differential kinetic analysis and flow injection analysis: Part 3. The (2.2.2) Cryptates of Magnesium,Calcium and Strontium

Simultaneous determinations of strontium and magnesium or calcium ions in solution can be done by differential kinetic analysis in continuous flow systems. Two different approaches are described; both are based on the differences between the dissociation rates of the cryptand (2.2.2) complexes of the metal ions, in the presence of potassium ions as scavenger and phthalein complexone as the chromogenic reagent for the released metal ions. Analyses were carried out at 40 h^-1, injected sample volumes were 25–150 μl.     

The fluoride ion-selective electrode in flow injection analysis: Part 1. General Methodology

A simple flow-injection system for determination of traces of fluoride by means of the fluoride-selective electrode is presented. A comparison of several flow-cell arrangements confirmed the advantages of a well-jet design. Systematic investigations of the parameters affecting response times (i.e., polishing procedure, flow rate, carrier composition) established the optimal experimental conditions for measurements down to 1 μg l^?1 fluoride. Calibration plots in the lower μg l^?1 range were neither Nernstein nor linear, but good precision (0.5–5%) was obtained even when the potential differences for concentration steps of one decade were as small as 3 mV.     

Recent progress on coumarin scaffold-based anti-microbial agents (Part III)

The biological, therapeutic, and medicinal properties of coumarins (chromen-2-ones), and its analogs have triggered enormous studies aimed toward growing synthetic routes to these heterocyclic compounds. This review presents a systematic and comprehensive survey of the method of preparation, the chemical reactivity, and the anti-microbial properties associated with this system.     

Activation of reducing agents. Sodium hydride containing complex reducing agents 29. Epimerization of alcohols by nickel-containing complex reducing agents (NiCRA)

Epimerization of selected alcohols has been easily achieved by nickel-containing Complex Reducing Agents (termed NiCRA) prepared from 2,5-dimethyl-2,5-hexanediol. It is shown that these reactions are under thermodynamic control.     

Metal benzoylpivaloylmethanates. Part III. Manganese(III) and iron(III) chelates

Summary The synthesis and principle properties of several novel tris[1-(4-X-phenyl)-4,4-dimethylpenta-1, 3-dionato]-iron(III) and manganese(III) complexes, where X=MeO, Me, H, F, Cl and NO₂, are described. Magnetic susceptibility measurements in the 4.2–295 K range show a near Curie behaviour and a constant magnetic moment for manganese(III) complexes and for iron complexes, with X=F, Cl or NO₂. Iron complexes with ligands having substituents: X=MeO, Me and H, show weak antiferromagnetic interaction (J=ca.–8 cm^–1 for the two former compounds) and a decrease in magnetic moment with decreasing temperature. In both manganese(III) and iron(III) complexes the diketonate ligand can be easily replaced by chlorine. Equilibrium constants could be evaluated only for substitution of the third diketonate ligand by chloride in the iron complexes on the basis of spectrophotometric measurements. For manganese chelates, the replacement of the second diketonate by chloride is accompanied by reduction of manganese(III) manganese(II) and free organic radical formation is observed.     

Reverse flow injection spectrophotometric for determination of aluminium(III)

A reverse flow injection analysis (rFIA) spectrophotometric method has been developed for the determination of aluminium(III). The method was based on the reaction of Al(III), quercetin and cetyltrimethylammonium bromide (CTAB), yielding a yellow colored complex in an acetate buffer medium (pH 5.5) with absorption maximum at 428 nm. The rFIA parameters that influence the FIA peak height have been optimized in order to obtain the best sensitivity and minimum reagent consumption. A linear relationship between the relative peak height and Al(III) concentrations were obtained over the concentration range of 0.02-0.50 mg L⁻¹ with a correlation coefficient of 0.9998. The limit of detection (LOD, defined as 3σ) and limit of quantification (LOQ, defined as 10σ) were 0.007 and 0.024 mg L⁻¹, respectively. The repeatability was 1.10% (n = 11) for 0.2 mg L⁻¹ Al(III). The proposed method was applied to the determination of Al(III) in tap water samples with a sampling rate of 60 h⁻¹. Results obtained were in good agreement with those obtained by the official ICP-MS method at the 95% confidence level.