17 research outputs found

    Determination of 1-methyl-1H-1,2,4-triazole in soils contaminated by rocket fuel using solid-phase microextraction, isotope dilution and gas chromatography–mass spectrometry

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    Environmental monitoring of Central Kazakhstan territories where heavy space booster rockets land requires fast, efficient, and inexpensive analytical methods. The goal of this study was to develop a method for quantitation of the most stable transformation product of rocket fuel, i.e., highly toxic unsymmetrical dimethylhydrazine – 1-methyl-1H-1,2,4-triazole (MTA) in soils using solid-phase microextraction (SPME) in combination with gas chromatography–mass spectrometry. Quantitation of organic compounds in soil samples by SPME is complicated by a matrix effect. Thus, an isotope dilution method was chosen using deuterated analyte (1-(trideuteromethyl)-1H-1,2,4-triazole; MTA-d3) for matrix effect control. The work included study of the matrix effect, optimization of a sample equilibration stage (time and temperature) after spiking MTA-d3 and validation of the developed method. Soils of different type and water content showed an order of magnitude difference in SPME effectiveness of the analyte. Isotope dilution minimized matrix effects. However, proper equilibration of MTA-d3 in soil was required. Complete MTA-d3 equilibration at temperatures below 40 Β°C was not observed. Increase of temperature to 60 Β°C and 80 Β°C enhanced equilibration reaching theoretical MTA/MTA-d3 response ratios after 13 and 3 h, respectively. Recoveries of MTA depended on concentrations of spiked MTA-d3 during method validation. Lowest spiked MTA-d3 concentration (0.24 mg kgβˆ’1) provided best MTA recoveries (91–121%). Addition of excess water to soil sample prior to SPME increased equilibration rate, but it also decreased method sensitivity. Method detection limit depended on soil type, water content, and was always below 1 mg kgβˆ’1. The newly developed method is fully automated, and requires much lower time, labor and financial resources compared to known methods

    Effects of Moisture Content and Solvent Additive on Headspace Solid-Phase Microextraction of Total Petroleum Hydrocarbons from Soil

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    Present paper describes optimization of the method of quantitative determination of total petroleum hydrocarbons in soil samples using headspace solid - phase microextraction (SPME) in combination with gas chromatography - mass spectrometry (GC-MS). Effects of moisture content and solvent additives were studied. It was established that an increase of the moisture content in soil leads to an increase of the response of petroleum hydrocarbons reaching its maximum at 15-20% depending on the soil type and concentration of total petroleum hydrocarbons followed by its gradual decrease. For the same concentration of petroleum hydrocarbons, an increase of moisture content in soil from 0 to 20% may lead to a 15x increase of total petroleum hydrocarbons response by solid - phase microextraction. Determination of total petroleum hydrocarbons in soils by SPME -GC-MS without moisture control of samples may lead to large errors, especially at low concentrations. It was established that addition of the solvent to a soil-water mixture allows dissolution of an oil film on the water surface and provides better extraction of hydrocarbons from soil to water phase. To avoid effect of moisture content on the extraction efficiency and more precise analysis of the real samples, addition of the excess distilled water must be done. Addition of the polar organic solvent to a soil-water mixture (10% isopropanol) allows dissolution of an oil film on the water surface and provides linear dependence of extraction efficiency vs total petroleum hydrocarbons content in soil. Testing of the optimized method on model soil samples provided quantitative data, results being in 30-120% range from the real values

    Mechanism of the thermochemical transformation of wheat grain’s processing waste during heat treatment

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    The thermal destruction of wheat grain’s processing wastes from Almaty and South Kazakhstan regions was studieΠ². The structure of the products obtained depending on the temperature of the carbonization process was formed, and the basic physico chemical characteristics of the obtained carbon material based on the WGPW were studied using thermogravimetric analysis, differential scanning calorimetry, IR spectroscopy and EPR spectroscopy. The analysis of the elemental composition of the obtained samples of the sorption material showed that the carbon content in the composition of the obtained carbon material is 75.08 - 76.12%, which in turn can cause a sufficiently high degree of sorption capacity of this material, as well as its mechanical strength. The obtained carbon materials based on OIP were modified with ammonium nitrate (NH4NO3) to improve its physico-chemical characteristics, such as specific surface area, porosity and adsorption capacity by iodine. It is shown that structural transformations of the processing waste of wheat grain (bran) in the process of heat treatment irrespective of temperature (in the studied interval) proceed through the stage of formation of free radicals. The concentration of free radicals formed in this process, as well as the composition of the graphite-like component of the products obtained, are determined by the temperature indices of the process

    GC–MS and GC–NPD Determination of Formaldehyde Dimethylhydrazone in Water Using SPME

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    Formaldehyde dimethylhydrazone (FADMH) is one of the important transformation products of residual rocket fuel 1,1-dimethylhydrazine (1,1-DMH). Thus, recent studies show that FADMH toxicity is comparable to that of undecomposed 1,1-DMH. In this study, a new method for quantification of FADMH in water based on solid phase microextraction (SPME) in combination with gas chromatography (GC) with mass spectrometric (MS) and nitrogen-phosphorus detection (NPD) is presented. Effects of SPME fiber coating type, extraction and desorption temperatures, extraction time, and pH on analyte recovery were studied. The optimized method used 65 micron polydimethylsiloxane/divinylbenzene fiber coating for 1Β min headspace extractions at 30Β Β°C. Preferred pH and desorption temperature from the SPME fiber are >8.5 and 200Β Β°C, respectively. Detection limits were estimated to be 1.5 and 0.5Β ΞΌgΒ Lβˆ’1 for MS and NPD, respectively. The method was applied to laboratory-scale experiments to quantify FADMH. Results indicate applicability for in situ sampling and analysis and possible first-time detection of free FADMH in water

    Экстракция скандия расплавом Π΄ΠΈ-2-этилгСксилфосфорной кислоты Π² Π»Π΅Π³ΠΊΠΎΠΏΠ»Π°Π²ΠΊΠΈΡ… разбавитСлях

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    Π’ настоящСС врСмя распространСниС экстракционных ΠΌΠ΅Ρ‚ΠΎΠ΄ΠΎΠ² ΠΏΡ€ΠΈ использовании Π»Π΅Π³ΠΊΠΎΠΏΠ»Π°Π²ΠΊΠΈΡ… Ρ€Π΅Π°Π³Π΅Π½Ρ‚ΠΎΠ² ΠΎΠ±ΡŠΡΡΠ½ΡΠ΅Ρ‚ΡΡ рядом свойствСнных ΠΈΠΌ прСимущСств, Ρ‚Π°ΠΊΠΈΡ… ΠΊΠ°ΠΊ высокиС кинСтичСскиС характСристики процСсса, Π»Π΅Π³ΠΊΠΎΡΡ‚ΡŒ раздСлСния Π΄Π²ΡƒΡ… Ρ„Π°Π·, большая ΡΠ΅Π»Π΅ΠΊΡ‚ΠΈΠ²Π½ΠΎΡΡ‚ΡŒ ΠΌΠ½ΠΎΠ³ΠΈΡ… экстрагСнтов, Π²ΠΎΠ·ΠΌΠΎΠΆΠ½ΠΎΡΡ‚ΡŒ ΡΡ€Π°Π²Π½ΠΈΡ‚Π΅Π»ΡŒΠ½ΠΎ ΠΏΠΎΠ»Π½ΠΎΠΉ ΠΈΡ… Ρ€Π΅Π³Π΅Π½Π΅Ρ€Π°Ρ†ΠΈΠΈ. Для экстракции скандия Π² тСхнологичСских цСлях ΠΏΡ€ΠΈΠΌΠ΅Π½ΡΡŽΡ‚ Π½Π΅ΠΉΡ‚Ρ€Π°Π»ΡŒΠ½Ρ‹Π΅ ΠΈ ΠΊΠ°Ρ‚ΠΈΠΎΠ½ΠΎΠΎΠ±ΠΌΠ΅Π½Π½Ρ‹Π΅ экстрагСнты. Ряд экстракционных Ρ€Π΅Π°Π³Π΅Π½Ρ‚ΠΎΠ² Π»Π΅Π³ΠΊΠΎ плавится ΠΏΡ€ΠΈ ΠΏΠΎΠ²Ρ‹ΡˆΠ΅Π½ΠΈΠΈ Ρ‚Π΅ΠΌΠΏΠ΅Ρ€Π°Ρ‚ΡƒΡ€Ρ‹, ΠΈ Ρ‚Π°ΠΊΠΈΠ΅ расплавы ΠΌΠΎΠΆΠ½ΠΎ ΠΈΡΠΏΠΎΠ»ΡŒΠ·ΠΎΠ²Π°Ρ‚ΡŒ для экстракции. Π­Ρ„Ρ„Π΅ΠΊΡ‚ΠΈΠ²Π½ΠΎΡΡ‚ΡŒ экстракционного извлСчСния ΠΌΠ΅Ρ‚Π°Π»Π»ΠΎΠ² ΠΊΠ°Ρ‚ΠΈΠΎΠ½ΠΎΠΎΠ±ΠΌΠ΅Π½Π½Ρ‹ΠΌΠΈ Ρ€Π΅Π°Π³Π΅Π½Ρ‚Π°ΠΌΠΈ зависит ΠΎΡ‚ ΠΌΠ½ΠΎΠ³ΠΈΡ… Ρ„Π°ΠΊΡ‚ΠΎΡ€ΠΎΠ². ИсслСдована экстракция скандия расплавом смСсСй Π΄ΠΈ-2-этилгСксилфосфорной кислоты – Π²Ρ‹ΡΡˆΠΈΠ΅ ΠΊΠ°Ρ€Π±ΠΎΠ½ΠΎΠ²Ρ‹Π΅ кислоты – ΠΏΠ°Ρ€Π°Ρ„ΠΈΠ½ ΠΈΒ  рассмотрСно влияниС кислотности Π²ΠΎΠ΄Π½ΠΎΠΉ Ρ„Π°Π·Ρ‹, ΠΊΠΎΠ½Ρ†Π΅Π½Ρ‚Ρ€Π°Ρ†ΠΈΠΈ скандия Π² Π²ΠΎΠ΄Π½ΠΎΠΉ ΠΈ экстрагСнта Π² органичСской Ρ„Π°Π·Π°Ρ…, ΡΠΎΠΎΡ‚Π½ΠΎΡˆΠ΅Π½ΠΈΡ объСмов органичСской ΠΈ Π²ΠΎΠ΄Π½ΠΎΠΉ Ρ„Π°Π· Π½Π° ΡΠΊΡΡ‚Ρ€Π°ΠΊΡ†ΠΈΡŽ ΠΌΠ΅Ρ‚Π°Π»Π»Π°. УстановлСно, Ρ‡Ρ‚ΠΎ экстракция скандия ΠΏΡ€ΠΎΡ‚Π΅ΠΊΠ°Π΅Ρ‚ ΠΏΠΎ ΠΊΠ°Ρ‚ΠΈΠΎΠ½ΠΎΠΎΠ±ΠΌΠ΅Π½Π½ΠΎΠΌΡƒ ΠΌΠ΅Ρ…Π°Π½ΠΈΠ·ΠΌΡƒ. Π‘ΠΊΠ°Π½Π΄ΠΈΠΉ количСствСнно извлСкаСтся (>99,0%) ΠΈΠ· кислых растворов. ΠžΠΏΡ‚ΠΈΠΌΠ°Π»ΡŒΠ½Π°Ρ концСнтрация Π΄ΠΈ-2-этилгСксилфосфорной кислоты составляСт 0,250 М Π² экстрагСнтС, количСствСнноС ΠΈΠ·Π²Π»Π΅Ρ‡Π΅Π½ΠΈΠ΅ скандия Π½Π°Π±Π»ΡŽΠ΄Π°Π΅Ρ‚ΡΡ Π² ΠΈΠ½Ρ‚Π΅Ρ€Π²Π°Π»Π΅ Π΅Π³ΠΎ ΠΊΠΎΠ½Ρ†Π΅Π½Ρ‚Ρ€Π°Ρ†ΠΈΠΉ 10-3 – 10-6 М ΠΈ ΠΏΡ€ΠΈ ΡΠΎΠΎΡ‚Π½ΠΎΡˆΠ΅Π½ΠΈΠΈ объСмов органичСской ΠΈ Π²ΠΎΠ΄Π½ΠΎΠΉ Ρ„Π°Π· 1:5 – 1:20

    Generation of Hydrogen and Oxygen from Water by Solar Energy Conversion

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    Photosynthesis is considered to be one of the promising areas of cheap and environmentally friendly energy. Photosynthesis involves the process of water oxidation with the formation of molecular oxygen and hydrogen as byproducts. The aim of the present article is to review the energy (light) phase of photosynthesis based on the published X-ray studies of photosystems I and II (PS-I and PS-II). Using modern ideas about semiconductors and biological semiconductor structures, the mechanisms of H+, O2↑, eβˆ’ generation from water are described. At the initial stage, PS II produces hydrogen peroxide from water as a result of the photoenzymatic reaction, which is oxidized in the active center of PS-II on the Mn4CaO5 cluster to form O2↑, H+, eβˆ’. Mn4+ is reduced to Mn2+ and then oxidized to Mn4+ with the transfer of reducing the equivalents of PS-I. The electrons formed are transported to PS-I (P 700), where the electrochemical reaction of water decomposition takes place in a two-electrode electrolysis system with the formation of gaseous oxygen and hydrogen. The proposed functioning mechanisms of PS-I and PS-II can be used in the development of environmentally friendly technologies for the production of molecular hydrogen

    Generation of Hydrogen and Oxygen from Water by Solar Energy Conversion

    No full text
    Photosynthesis is considered to be one of the promising areas of cheap and environmentally friendly energy. Photosynthesis involves the process of water oxidation with the formation of molecular oxygen and hydrogen as byproducts. The aim of the present article is to review the energy (light) phase of photosynthesis based on the published X-ray studies of photosystems I and II (PS-I and PS-II). Using modern ideas about semiconductors and biological semiconductor structures, the mechanisms of H+, O2↑, e− generation from water are described. At the initial stage, PS II produces hydrogen peroxide from water as a result of the photoenzymatic reaction, which is oxidized in the active center of PS-II on the Mn4CaO5 cluster to form O2↑, H+, e−. Mn4+ is reduced to Mn2+ and then oxidized to Mn4+ with the transfer of reducing the equivalents of PS-I. The electrons formed are transported to PS-I (P 700), where the electrochemical reaction of water decomposition takes place in a two-electrode electrolysis system with the formation of gaseous oxygen and hydrogen. The proposed functioning mechanisms of PS-I and PS-II can be used in the development of environmentally friendly technologies for the production of molecular hydrogen

    Effects of Moisture Content and Solvent Additive on Headspace Solid-Phase Microextraction of Total Petroleum Hydrocarbons from Soil

    No full text
    Present paper describes optimization of the method of quantitative determination of total petroleum hydrocarbons in soil samples using headspace solid - phase microextraction (SPME) in combination with gas chromatography - mass spectrometry (GC-MS). Effects of moisture content and solvent additives were studied. It was established that an increase of the moisture content in soil leads to an increase of the response of petroleum hydrocarbons reaching its maximum at 15-20% depending on the soil type and concentration of total petroleum hydrocarbons followed by its gradual decrease. For the same concentration of petroleum hydrocarbons, an increase of moisture content in soil from 0 to 20% may lead to a 15x increase of total petroleum hydrocarbons response by solid - phase microextraction. Determination of total petroleum hydrocarbons in soils by SPME -GC-MS without moisture control of samples may lead to large errors, especially at low concentrations. It was established that addition of the solvent to a soil-water mixture allows dissolution of an oil film on the water surface and provides better extraction of hydrocarbons from soil to water phase. To avoid effect of moisture content on the extraction efficiency and more precise analysis of the real samples, addition of the excess distilled water must be done. Addition of the polar organic solvent to a soil-water mixture (10% isopropanol) allows dissolution of an oil film on the water surface and provides linear dependence of extraction efficiency vs total petroleum hydrocarbons content in soil. Testing of the optimized method on model soil samples provided quantitative data, results being in 30-120% range from the real values.This article is published as Alimzhanova, M. B., B. N. Kenessov, M. K. Nauryzbayev, and J. A. Koziel. "Effects of moisture content and solvent additive on headspace solid-phase microextraction of total petroleum hydrocarbons from soil." Eurasian Chemico-Technological Journal 14, no. 4 (2012): 331-335. Posted with permission.</p

    GC–MS and GC–NPD Determination of Formaldehyde Dimethylhydrazone in Water Using SPME

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    Formaldehyde dimethylhydrazone (FADMH) is one of the important transformation products of residual rocket fuel 1,1-dimethylhydrazine (1,1-DMH). Thus, recent studies show that FADMH toxicity is comparable to that of undecomposed 1,1-DMH. In this study, a new method for quantification of FADMH in water based on solid phase microextraction (SPME) in combination with gas chromatography (GC) with mass spectrometric (MS) and nitrogen-phosphorus detection (NPD) is presented. Effects of SPME fiber coating type, extraction and desorption temperatures, extraction time, and pH on analyte recovery were studied. The optimized method used 65 micron polydimethylsiloxane/divinylbenzene fiber coating for 1 min headspace extractions at 30 Β°C. Preferred pH and desorption temperature from the SPME fiber are >8.5 and 200 Β°C, respectively. Detection limits were estimated to be 1.5 and 0.5 ΞΌg Lβˆ’1 for MS and NPD, respectively. The method was applied to laboratory-scale experiments to quantify FADMH. Results indicate applicability for in situ sampling and analysis and possible first-time detection of free FADMH in water.This article is from Chromatographia 73 (2011): 123–128, doi:10.1007/s10337-010-1820-6. Posted with permission.</p
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