• YAKHAK HOEJI
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• v.37 no.4
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• pp.317-324
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• 1993

The metabolic profile of carbinoxamine, 2-[(4-chlorophenyl)-2-pyridinyi-methoxy] N, N-dimethylethanamine, was determined in rat urine. Urinary extracts obtained with or without enzyme hydrolysis were derivatized with MSTFA/TMSCI (N-methyl-N-trimethylsilyl trifluoroacetamide/Trimethylchlorosilane) and analyzed by GC/MSD. In rat urine, which obtained after oral treatment with carbinoxamine maleate, chlorobenzolyl pyridine, (4-chlorophenyl)-2-pyridinyl methanol : carbinol, 2-[(4-chlorophenyl)-2-pyridinylmethoxy]-N-methylethanamine : norcarbinoxamine, 2-[(4-chlorophenyl)2-pyridinylmethoxy]ethanamine : bis-norcarbinoxamine and parent carbinoxamine were detected in free form. Norcarbinoxamine and bisnorcarbinoxamine were also detected in conjugated form(acetylation). These data suggest that in the rat, hydroxylation of either the benzyl or pyridinyl ring can occur during carbinoxamine elimination. O-demethylation and subsequent conjugation represents the primary pathway of carbinoxamine elimination in the rat.

• Korean Journal of Weed Science
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• v.14 no.2
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• pp.156-162
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• 1994

To better understand the exact nature of the major toxic compound responsible for phytotoxicity of sorghum stem, the most toxic compound from the stem extract was isolated by rapid chromatography and subsequently purified by thin-layer chromatography(TLC) and high pressure liquid chromatography(HPLC). Of the eight fractions isolated by rapid chromatography, the fraction with solvent combinations of butanol (8) : acetic acid (1) : water (1) had the highest toxicity. Further separation of the fraction by TLC in a solvent mixture of butanol (24) : acetic acid (16.4) : water (7) : propanol (1) showed that the spot with an $R_f$ 0.71 had one major peak with retention time of 20.40 minutes. Upon subjecting gas chromatography and the HPLC fraction to the mass spectrometry, the toxic compound is probably one of the four compounds ; 1-methyl-1-(2-propynyl)-hydrazine, 1-aziridineethanol, 5-chloro-2-pentanone, and 2-(methylseleno)-ethanamine.

• Environmental Analysis Health and Toxicology
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• v.20 no.2 s.49
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• pp.123-131
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• 2005

본 연구는 GC/MS를 이용하여 수질, 토양 및 저질 시료 중의 4-Nitrotoluene(4-NT)을 분석하는 방법을 확립하고자 하였다. 4-NT은 수질 시료(100mL)에서 n-hexane으로 추출하였으며, 토양 및 저질 시료(10g)에서는 먼저 메탄올로 추출한 후 hexane으로 다시 추출하여 농축시켜 분석하였다. 수질 시료 중의 4-NT의 회수율은 $99.1\%$ 이상이였으며 토양에서의 회수율(recovery)은 약 $110\%$를 보였고 재현성 (relative standard deviation)은 $11.99\%$ 이하였다. 검정곡선은 상관계수$(R^2)$값이 수질과 토양 모두에서 0.994이상의 좋은 직선성을 보여주었다. 본 연구에서 채취한 수질 43개 지역, 토양 35개 지역 및 저질 11개 지역의 모든 시료에서 4-NT은 검출한계 이하로 나타났다. 이 분석방법은 환경 중에 미량으로 존재하는 4-NT의 분석과 모니터링에 유용하게 사용할 수 있는 적합한 방법이라 사료된다.

• Microbiology and Biotechnology Letters
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• v.27 no.3
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• pp.179-183
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• 1999

The volatile components (essential oil) showing antimicrobial activity were extracted from the fruit peel of Zanthoxylum piperitum DC by distillation and separated by thin layer chromatography (TLC). The crude volatile components exhibited antimicrobial activity only at very high concentration. The active fraction obtained by TLC inhibited noticeably the growth of bacteria. The minimum inhibitory concentration (MIC) of the fraction were 150ppm, 300ppm, and 300ppm against Escherichia coli, Staphylococcus aureus, and Salmonella enteritidis, respectively. The components in the active fraction were identified by gas chromatography/mass spectrometry to be geranlyl acetate (60.23%), citronellal(36.01%), citronellol(3.77%), geraniol(0.46%), and cumin ldehyde(0.43%).

• Analytical Science and Technology
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• v.7 no.1
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• pp.65-78
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• 1994

The herbicide mixture of 7 triazines and 9 phenoxyalkanoic acid esters was simultaneously separated and determinated with the selected ion monitoring by using gas chromatography/mass spectrometry. The extraction recoveries of those herbicides from the reagent water were studied for the organic solvent extraction(LLE) with methylene chloride. The calibration curves of them showed good linearity over the concentration range of 0.2~0.5ng/ml and the detection limits were 0.2~0.5ng/ml for 100ml of water. This analytical method could be applied to the drinking water and biological sample.

• Analytical Science and Technology
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• v.23 no.5
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• pp.477-484
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• 2010

Personal care products are a diverse group of synthetic organic chemicals such as antimicrobial compounds, UV filters and organo-phosphate flame retardants and derived from individual usages of soaps, toothpaste and cosmetics. It has been detected in municipal sewage effluent and various environmental samples such as surface water, marine, soil, sediment and aquatic biota in many countries. The occurrence of personal care products in environmental samples could negatively impact the health of the ecosystem and humans, due to persistent, long-term chronic exposure of aquatic organisms. In this study, fifteen personal care products in aquatic environmental samples were determined by gas chromatography-mass spectrometry (GC-MS) with liquidliquid extraction (LLE). Method detection limits were in the range of $0.004\sim0.273\;{\mu}g/L$. Two compounds (TCEP, TCPP) were detected in surface waters and seven compounds (triclosan, 4-MBC, EHMC, BP-3, TCEP, TPP, TBEP) were detected in sewage treatment plants (STP) influents or effluents.

• Analytical Science and Technology
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• v.13 no.6
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• pp.736-742
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• 2000

The purpose of this study was to determine the homocysteine (Hey), methionine (Met) and cysteine (Cys) using solid phase micro-extraction (SPME)/gas chromatography (GC)-mass spectrometry (MS) in human plasma and to correlate between the plasma concentration of homocysteine with coronary artery disease. The homocysteine, methionine and cysteine in blood can be used as biomarkers for the risk assessment of vascular disease. The plasma homocysteine level for the coronary artery disease patients was higher than general patients. The concentration ranges of the Hcy, Met and Cys for coronary artery disease patients were $18.47-33.38{\mu}mol/L$, $30.16-55.72{\mu}mol/L$ and $183.16-387.32{\mu}mol/L$, respectively. This method showed good sensitivity and convenience.

• Korean Journal of Environment and Ecology
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• v.29 no.4
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• pp.564-569
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• 2015

In order to discover materials that can be used for OLED, extractions of marine microalgae was screened for photoluminescence(PL) properties and analyzed using gas chromatography-mass spectrometry(GC-MS). The extractions of Nitzschia denticula, Navicula cancellata and Nannochloropsis salina showed PL spectroscopy among fourteen marine microalgae species. The selected three fractions from three microalgae were analyzed by GC-MS. According to the results, it was found that the identified organic light-emitting materials can be subdivided into three functional groups based on imidazole, purine and quinoline. These chemicals are considered to have a strong relationship with PL spectroscopy for OLED materials.

• Korean Journal of Food Science and Technology
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• v.40 no.5
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• pp.497-502
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• 2008

The volatile components in Gamdongchotmoo kimchi, unfermented and fermented for 3 or 25 days, were extracted via solvent-assisted flavor evaporation (SAFE), and then analyzed via gas chromatography/mass spectrometry (GCMS). A total of 57 components, including 14 S-containing compounds, 22 terpene hydrocarbons, 13 aliphatic hydrocarbons, 4 alcohols, and 4 miscellaneous components, were detected in Gamdongchotmoo kimchi. Among them, the S-compounds were quantitatively dominant. The aroma-active compounds were also determined via gas chromatography-olfactometry (GC-O), using aroma extract dilution analysis (AEDA). A total of 16 aroma-active compounds were detected via GC-O. The most intense aroma-active compounds in Gamdongchotmoo kimchi included 4-isothiocyanato-1-butene ($Log_3$ FD factor 7, rancid), an unknown($Log_3$ FD factor 7, spicy) and another unknown ($Log_3$ FD factor 7, seasoning-like). In addition, other aroma-active compounds, including dimethyldisulfide ($Log_3$ FD factor 6, rotten onion-like/sulfury), 2-vinyl-[4H]-1,3-dithiin ($Log_3$ FD factor 5, spicy/garlic-like), and an unknown ($Log_3$ FD factor 5, rancid/cheese-like) might be crucial to the flavor characteristics of Gamdongchotmoo kimchi.

• Journal of Environmental Health Sciences
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• v.28 no.1
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• pp.21-29
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• 2002

To identify and evaluate the dichlorobenzidine(DCB)-DNA adducts in liver cell and bladder epithelial cells by $^{32}$ P-postlabeling and GC/MS-SIM, we orally exposed the dichlorobenzidine(20mg/kh body wt./day) to male Sprague-Dawley rats(l85$\pm$10g) for 14 days. Two kinds of DCB-DNA adduct(A1 and A2) were found at the same site of thin layer chromatogram of $^{32}$ P-postlabeling method in liver cells and bladder epithelial cells. In liver cells, relative adduct labeling(RAL) $\times$ 10$^{12}$ of DCB-DNA adduct A1 were 34.1$\pm$3.71 and 69.9$\pm$5.02, that of adduct A2 were 74.1$\pm$10.1 and 105.1$\pm$10.1 on 10 and 14 days after treatment, respectively. And in bladder epithelia cells, RAL $\times$ 10$^{12}$ of DCB-DNA adduct A1 were 5.92$\pm$1.60 and 15.9$\pm$1.31, that of adduct A2 were 9.81$\pm$2.81 and 22.8$\pm$1.79 on 10 and 14 days after treatment, respectively. DCB metabolites formed DNA adducts were monoacetyl-dichlorobenzidine(acDCB) and diacetyl-dichlorobenzidine(di-acDCB), which was identify by gas chromatography/mass spectrometry-scan ionization mode(GC/MS-SIM), after hydrolysis of DCB-DNA adducts isolated from live cells and bladder epithelial cells. The base peak of acDCB were 252 and 294 m/z, and that of di-acDCB were 252, 294 and 336 m/z. In conclusion, the exposed DCB formed two kinds of DCB-DNA adduct, the proximate materials of that were acDCB and di-acDCB in liver and bladder epithelial cells. And the above GC/MS-SIM method was found the DCB-DNA adducts could be monitoring by gas chromatography.