Sorption–Chromatographic Determination of Aniline, 4-Chloroaniline, and 2,5-Dichloroaniline in Air

Conditions were found for the chemisorption preconcentration of aniline, 4-chloroaniline, and 2,5-dichloroaniline from air using tubes packed with silica gel with immobilized 4-chloro-5,7-dinitrobenzofurazan and for the subsequent HPLC determination with diode-array detection. The maximum analyte recoveries (98, 90, and 75% for aniline, 4-chloroaniline, and 2,5-dichloroaniline, respectively) were achieved at a 2-cm thickness of the adsorbent layer (silica gel with a grain size of 0.1–0.3 mm impregnated with 3 wt % 4-chloro-5,7-dinitrobenzofurazan), an aspiration rate of 0.6–0.8 L/min, and an aspirated air volume of 10 L. Taking into account a tenfold preconcentration of analytes after the desorption, the detection limit for aniline is equal to 0.0007 mg/m³.     

Extraction-chromatographic determination of hydrazine in natural water as a 5,7-Dinitrobenzofurazan derivative using diode-array detection

The conditions for the derivatization of hydrazine withp-dimethylaminobenzaldehyde and 4-chloro-5,7-dinitrobenzofurazan, extraction preconcentration of derivatives from natural water, and HPLC determination of the toxicant with diode-array detection were studied. The 5,7-dinitrobenzofurazan derivative was quantitatively extracted from water with isoamyl alcohol and a mixture of isoamyl alcohol with methylene chloride at pH 3–4. A procedure was developed for the extraction-chromatographic determination of hydrazine in water with c_min = 0.05 Μg/L and the analytical range 0.12-60 Μg/L. The concentration of hydrazine in lake Kaban water was determined.     

Test Method for the Determination of Toxic Irritants in Air

It is shown that 10-chloro-9,10-dihydrophenarsazine and dibenz[b, f][1,4]oxazepine can be determined with the use of indicator tubes containing 4-chloro-5,7-dinitrobenzofurazan and its N-oxide immobilized on silica gel. The conditions for the determination of these substances in air are determined. The following effects are studied: the nature, particle size, and layer thickness of the support; the nature and concentration of the analytical reagent in the chemisorption layer; the rate and time of air aspiration through the indicator tube; and various components of the sample matrix. The limit of visual detection of the toxic substances is 0.05 mg/m³.     

Determination of hydrazine derivatives by flow-injection analysis with spectrophotometric detection

Flow-injection analysis for the determination of hydrazine derivatives based on their nucleophilic substitution reaction with 4-chloro-5,7-dinitrobenzofurazan in aqueous medium, and spectrophotometric detection has been described. The calibration graphs were linear in the range from 0.15 to 4.0 mug ml(-1) of hydrazine derivatives, with sampling rates of up to 28-32 samples h(-1). Interferences from amino compounds, benzoic acids, aliphatic amines and ammonia have been evaluated. The procedure has been applied to the determination of hydrazine derivatives in serum, urine, appressin drugs and artificial mixtures.     

The determination of hydrazine and 1,1-dimethylhydrazine,separately or in mixtures,by high-pressure liquid chromatography

A rapid, sensitive liquid chromatographic method for the determination of hydrazine and 1,1-dimethylhydrazine, separately or in mixtures of varying proportions, is described. The procedure involves salicylaldehyde derivative formation followed by chromatography on a reversed phase (octadecylsilane) column with acetonitrile (52%)—0.14 M potassium dihydrogenphosphate (48%) as a mobile phase and u.v. (254 nm) detection. This system is sensitive to 2 μg ml^-1 of hydrazine and 5 μg ml^-1 of 1,1-dimethylhydrazine and has a relative standard deviation of less than 1%. Monomethylhydrazine forms an unstable salicylaldehyde hydrazone; although it cannot be determined, it can be detected (sensitivity 5 μg ml^-1 ) and does not interfere with quantitative measurement of either hydrazine or 1,1-dimethylhydrazine.     

Flow-injection determination of indole derivatives in pharmaceutical mixtures

The reactions of tryptamine derivatives with 4-chloro-5,7-dinitrobenzofurazan were studied. The composition of the products of analytical reactions was found from the data of elemental analysis, and their structures were confirmed by ¹H NMR spectra. The working conditions were selected for the flow-injection determination of 22 indole derivatives in pharmaceutical mixtures as 5,7-dinitrobenzofurazans with spectrophotometric detection at 490 nm. Optimum results were obtained using acetonitrile-buffer solution (pH 6.8) flows. The analytical range for biologically active substances was between 0.04 and 0.61 μg/mL. The throughput was 25–35 sample/h. The detection limit was 0.01 μg/mL. Serotonin, mexamine, melatonine, sumatryptan, and indolylacetic acid derivatives were determined in pharmaceuticals and in reaction mixtures from the synthesis of biologically active substances.     

Highly sensitive determination of 1,1-dimethylhydrazine by high-performance liquid chromatography–tandem mass spectrometry with precolumn derivatization by phenylglyoxal

A new highly sensitive and rapid approach to the determination of 1,1-dimethylhydrazine in natural water is developed (determination range is 0.03–1 μg/L). It is based on the use of high-performance liquid chromatography–tandem mass spectrometry with precolumn derivatization by phenylglyoxal and does not require any preconcentration. Derivatization, chromatographic separation conditions, and tandem mass spectrometry detection parameters are chosen. Intra-day precision of the results of measurements of 1,1- dimethylhydrazine in natural water is 12–16%, and inter-day precision is 16–22%. The lowest limit of detection and the lowest limit of quantification are 0.010 μg/L and 0.030 μg/L, respectively.     

Gas-chromatographic determination of 1,1-dimethylhydrazine in water

A gas-chromatographic procedure for the determination of 1,1-dimethylhydrazine in water was developed on the basis of its reaction with 4-nitrobenzaldehyde yielding the corresponding hydrazone, the extraction of the latter from water with an organic solvent, its subsequent preconcentration by evaporation, and the determination on a gas chromatograph with a nitrogen-phosphorus detector. The determination limit of 1,1-dimethylhydrazine is 0.03 μg/L. The relative error of the determination is no larger than 22% in the concentration range 0.06–0.60 μg/L and 33% at a level of 0.03 μg/L.     

Simultaneous Determination of Hydrazine,Methylhydrazine, and 1,1-Dimethylhydrazine by High-Performance Liquid Chromatography with Pre- and Post-Column Derivatization by 5-Nitro-2-Furaldehyde

Approaches to the chromatographic determination of 1,1-dimethylhydrazine and two main products of its degradation (hydrazine and methylhydrazine) on their simultaneous presence are proposed using derivatization by 5-nitro-2-furaldehyde and multi-wavelength spectrophotometric detection of the formed derivatives in the visible spectral region. A combination of preliminary derivatization with separation in the reversed-phase HPLC mode and also ion-chromatographic separation with post-column derivatization allowed us to reach the limits of detection for analytes lower than 1 μg/L and to determine 1,1-dimethylhydrazine at the level of the maximum permissible concentration without preconcentration. The developed approaches were tested on an acid extract of a sample of peat bog soil collected at the place of impact of the first stage of a carrier rocket. The identity of the results obtained by different methods and the high level of soil pollution by hydrazines are shown.     

Determination of hydrazine and 1,1-dimethylhydrazine as salicyldehyde derivates by liquid chromatography with electrochemical detection

Summary Determination of hydrazine and 1,1-dimethylhydrazine after derivatization with salicylaldehyde was done using high-performance liquid chromatography with electrochemical detection. The oxidation of the phenolic group of salicylaldazine (S-HY) and salicylaldehyde-1,1-dimethylhydrazone (S-UDMH) was optimized with respect to ionic strength, pH, and applied potential. Less than 5 ng of S-HY and S-UDMH could be detected. The detection limits for hydrazine and 1,1-dimethylhydrazine solutions were estimated to be 0.025 and 0.20 ppm, respectively.     

Effect of support nature on the efficiency of the chemisorption preconcentration of aromatic amines from air

The effect of silica gel-modifying additives on the efficiency of the chemisorption preconcentration of aniline, o-toluidine, and N,N-dimethylaniline as 5,7-dinitrobenzofurazan derivatives from atmospheric air was studied by HPLC. The recovery exhibited a maximum on unmodified silica gel, and the recovery of N,N-dimethylaniline was lower than that of primary aromatic amines. This is likely due to a decrease in the possibility of π-complex formation between an aromatic amine and silica gel after the chemical modification of the adsorbent surface. The formation of a π-complex will increase the rate of reaction between an aromatic amine and an electrophilic reagent.     

Synthesis, structure, and antibacterial activity of aminobenzofuroxan and aminobenzofurazan

The amination of 4,6-dichloro-5,7-dinitrobenzofuroxan and 4,6-dichloro-5,7-dinitrobenzofurazan with dibenzylamine followed the aromatic nucleophilic substitution pattern (S_NAr) and gave products of replacement of both chlorine atoms in the six-membered ring with elimination of hydrogen chloride. Regardless of the reactant ratio, 4,6-dichloro-5,7-dinitrobenzofuroxan was converted into 4,6-bis(dibenzylamino)-5,7-dinitrobenzofuroxan, whereas 4,6-dichloro-5,7-dinitrobenzofurazan under analogous conditions gave rise to unusual bisammonium derivative which lost proton from the amino group on C⁴ and benzyl group from the amino group on C⁶; as a result, the corresponding diamine with secondary and tertiary nitrogen atoms was obtained. The structure of the isolated compounds was determined by IR and NMR spectroscopy, elemental analysis, and X-ray analysis; their thermal stability was studied by simultaneous thermogravimetry and differential scanning calorimetry.     

Rapid Test Determination of Iron(II) in Aqueous Media by Reagent Indicator Paper

A reagent indicator paper with immobilized zirconyl hexacyanoferrate(III) is prepared for the preconcentration and determination of 0.05–500 mg/L of iron(II) in the presence of more than 100-fold amount of iron(III). The paper is stable in the presence of up to 200 mg/L of 1,1-dimethylhydrazine. The test method is successfully verified using a color comparator or a minireflectometer with a red light-emitting diode as applied to samples of natural water from drilling mud flows and aqueous solutions containing 1,1-dimethylhydrazine.     

Salen impregnated silica gel as a new sorbent for on-line preconcentration of cadmium(II)

A new sorbent – salen impregnated silica gel – was prepared and characterised for application as a minicolumn packing for flow-injection on-line preconcentration of cadmium(II). The system was coupled with flame atomic absorption spectrometer (FI-FAAS). The optimal pH for Cd(II) sorption was in the range of 7.4–8.8 and nitric acid (1%, v/v) was efficient as eluent. Sorption was most effective within the sample flow rate up to 7?mL?min^?1. Sorption capacity of the sorbent found in a batch procedure was 26.3?µmol?g^?1 (2.95?mg?g^?1). Enrichment factor (EF) and limit of detection (LOD) obtained for 120-second loading time were 113 and 0.26?µg?L^?1, respectively. The sorbent stability in the working conditions was proved for at least 100 preconcentration cycles. The evaluated method was applied to Cd(II) determination in various water samples.     

Test Films for the Determination of Aromatic Amines and Hydrazines in Aqueous Solutions

Conditions of the test determination of toxic aniline (I), N,N-dimethylaniline (II), N,N-diethylaniline (III), 2,2,4-trimethyl-1,2-dihydroquinoline (IV), 1,1-dimethylhydrazine (V), and phenylhydrazine (VI) as their 4,6-dinitrobenzofuroxan (I) and 5,7-dinitrobenzofurazan (II, III, IV, V, VI) derivatives in aqueous solutions were found. Visual and spectrophotometric measurement of the signal was used. The reagents were immobilized in nitrocellulose films. Optimal results of visual determination of color development in test films were obtained with reagents immobilized in nitrocellulose at their concentration of 5 mass % and pH of the test solution in the range 6.0–7.5. The spectrophotometric measurement of the signal of test films was performed at wavelengths of 500–560 nm for I, V, and VI and 610–620 nm for II, III, and IV. The detection limit for spectrophotometric measurement was 0.01, 0.18, 0.13, 0.15, 0.16, and 0.04 mg/L for I, II, III, IV, V, and VI, respectively. The analytical range of the toxicants was 0.05–6.0 mg/L. Test determination is possible in the presence of alkylamines, ammonia, phenols, carboxylic acids, and inorganic salts.     

Solid Phase Extraction of Neutral Analytes through Silica Gel Coated with Layers of Au Nanoparticles Self‐Assembled with Alkanethiols

In this study, we used Au nanoparticle (NP)‐coated silica gel as a solid phase extraction sorbent for the preconcentration of neutral analytes (steroid drugs). The sorbent was fabricated using two alkanethiol self‐assembly processes: one to deposit the Au NPs onto a 3‐aminopropyltrimethoxysilane‐modified silica gel and the other to functionalize the surfaces of the Au NPs. A large volume of the steroid solution was passed through the silica gel to facilitate adsorption mediated by hydrophobic interactions between the steroids and the hydrophobic moieties on the silica gel surface. Extraction of the steroids was accomplished by flushing the silica gel with a low‐polarity solvent. In this preliminary study, we found that the particle size of the silica gel and the number of layers of Au NPs coated on the silica gel both affected the preconcentration performance for the steroids. When using six layers of Au NPs coated on 5–20‐μm silica gel, the detection limits for steroids were below 80 ng L^?1; the preconcentration efficiency was over 170‐fold higher than that of the original steroid solution. Our findings provide further evidence that nanotechnology has much to benefit analytical science.     

Determination of 1,1-Dimethylhydrazine by Reversed-Phase High-Performance Liquid Chromatography with Spectrophotometric Detection as a Derivative with 4-Nitrobenzaldehyde

A procedure was developed for the determination of 1,1-dimethylhydrazine by reversed-phase high-performance liquid chromatography with spectrophotometric detection and preliminary derivatization by the reaction with 4-nitrobenzaldehyde. Conditions were selected for the chromatographic separation and the detection of the peaks of the reagent and 4-nitrobenzaldehyde dimethylhydrazone. The optimum conditions were found for the derivatization of 1,1-dimethylhydrazine with 4-nitrobenzaldehyde. The determination limit of 1,1-dimethylhydrazine in aqueous solutions was 120 g/L (2 M/L).     

Solid phase extraction using silica gel functionalized with Sulfasalazine for preconcentration of uranium(VI) ions from water samples

Silica gel surface was chemically functionalized by reaction the silanol from the silica surface with 3-chloropropyltrimethoxysilane followed by reaction with Sulfasalazine. This new sorbent has been used for the preconcentration of low levels of U(VI) ions from an aqueous phase. Parameters involved in extraction efficiency such as pH, weight of the sorbent, volume of sample and eluent were optimized in batch and column methods prior to determination by spectrophotometry using arsenazo(III) reagent. The results showed that U(VI) ions can be sorbed at pH range of 5.0–6.0 in a minicolumn and quantitative recovery of U(VI) (>98.0?±?1.6%) was achieved by stripping with 2.5 mL of 0.1 mol L^?1 HCl. The sorption capacity of the functionalized silica gel was 1.15 mmol g^?1 of U(VI). A linear calibration graph was obtained over the concentration range of 0.02–27.0 μg mL^?1 with a limit of detection of 1 μg L^?1 in treatment with 1000 mL of the U(VI) solution in which the preconcentration factor was as high as 400. The method was employed to the preconcentration of U(VI) ions from spiked ground water and synthetic sea water samples.     

Modular stopped-flow/diode-array detection system for simultaneous kinetic analysis

The coupling of a stopped-flow module to a diode-array spectrophotometric detector has been exploited for the simultaneous kinetic resolution of mixtures. The analytical possibilities are shown with the resolution of a mixture of two analytes (hydrazine and phenylhydrazine), yielding products with different spectral features (after reaction with p-dimethylaminobenzaldehyde), so that only the simultaneous measurement of their respective initial rates at their corresponding maximum absorption wavelengths is possible. The method allows 0.02–30 μg ml^?1 hydrazine and 8–2200 μg ml^?1 phenylhydrazine to be determined simultaneously.     

Extraction and preconcentration of formaldehyde in water by polypyrrole‐coated magnetic nanoparticles and determination by high‐performance liquid chromatography

In this study, a simple and rapid extraction method based on the application of polypyrrole‐coated Fe₃O₄ nanoparticles as a magnetic solid‐phase extraction sorbent was successfully developed for the extraction and preconcentration of trace amounts of formaldehyde after derivatization with 2,4‐dinitrophenylhydrazine. The analyses were performed by high‐performance liquid chromatography followed by UV detection. Several variables affecting the extraction efficiency of the formaldehyde, i.e., sample pH, amount of sorbent, salt concentration, extraction time and desorption conditions were investigated and optimized. The best working conditions were as follows: sample pH, 5; amount of sorbent, 40 mg; NaCl concentration, 20% w/v; sample volume, 20 mL; extraction time, 12 min; and 100 μL of methanol for desorption of the formaldehyde within 3 min. Under the optimal conditions, the performance of the proposed method was studied in terms of linear dynamic range (10–500 μg/L), correlation coefficient (R² ≥ 0.998), precision (RSD% ≤ 5.5) and limit of detection (4 μg/L). Finally, the developed method was successfully applied for extraction and determination of formaldehyde in tap, rain and tomato water samples, and satisfactory results were obtained.