• Bulletin of the Korean Chemical Society
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• 제26권2호
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• pp.297-302
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• 2005

The determination of total phenols was accomplished by capillary-high performance liquid chromatography (capillary-HPLC) after nitrosation of the U.S.E.P.A. classified 11 priority pollutant phenols, using the nitrosated parent phenol (POHNO) as a reference for calibration. The optimum mobile phase composition for this analysis was found by examining the effect of changing the percentage of acetonitrile (MeCN) in the mobile phase on retention factors (k values) and peak intensities. As MeCN percentage was increased, k values were reduced and peak intensities were generally increased. From the results obtained, it was found that the optimum mobile phase was 90%(v/v) MeCN solution at pH 8.0, the detection wavelength of 400 nm, and a detection limit (D.L., concentration at signal to noise ratio (S/N) of 3.0) of 4.5 ${\times}$ $10^{-7}$ M. In addition, 10 of the 11 phenols present in mineral or waste water were separated after the nitrosation by capillary-HPLC. The optimum mobile phase for separation was a 40%(v/v) MeCN solution at pH 5.0.

• Bulletin of the Korean Chemical Society
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• 제11권4호
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• pp.297-302
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• 1990

Retention of mono-substituted phenols in reversed-phase liquid chromatography has been studied based on the linear solvation energy relationships using the solvatochromic mobile phase parameters, ${\pi}_m^{\ast}, {\alpha}_m$ and ${\beta}_m$. It has been observed that retention behavior of phenols in RPLC were well represented by regression equations vs. solvatochromic mobile phase parameters even though the equations may be incomplete due to lack of an explicit cavity term. Dependence of retention of monosubstituted phenols on the mobile phase properties were varied depending on the type of the organic cosolvent in the mobile phase, e.g., ${\beta}_m$ and {\alpha}_m$ in methanol-water system, but ${\pi}_m^{\ast} and ${\beta}_m$ in THF-water system. It has been suggested that retention of phenols in methanol-water system is controlled by the solvophobicity of the mobile phase.

• 분석과학
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• 제7권1호
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• pp.33-39
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• 1994

환경오염수에 미량 존재하는 페놀류를 정량하기 위한 분석법의 개발을 위하여 8가지 페놀류를 대상 시료로, 고체상 추출법을 이용한 전처리 방법을 연구하였다. XAD-4와 Dowex $1{\times}8$ 수지를 연결하여 HPLC로 분석하는 온 라인 시스템을 만들어 농축과 분리의 선택성을 높이며 자동화에 중점을 두었다. 시료를 XAD-4 컬럼에 용리시켜 페놀류를 분자흡착으로 농축시킨 후 염기성 아세토니트릴을 용리시켜 탈착시키고 계속해서 Dowex $1{\times}8$ 컬럼에 음이온교환으로 페놀류만을 선택적으로 재흡착시킨다. Dowex $1{\times}8$ 컬럼에 재흡착된 페놀류를 물로 세척한 후 HCl을 포함하는 메탄올 용액으로 재탈착시킨다. 전처리 단계는 switching 밸브에 의해 온 라인으로 연결하였고 탈착된 페놀류를 HPLC에 직접 주입하여 신속하고 신뢰성 있는 정량이 가능하였다. 각 페놀류는 90% 이상의 회수율을 나타내었다. 본 분석법의 활용성을 평가하기 위해 환경오염수에서 페놀류와 공존 가능한 유기 화합물들을 첨가시켜 조제한 실험실적 오염수를 만들어 방해 효과를 조사한 결과, 페놀류만을 선택적으로 농축-분석할 수 있었다.

• 대한화학회지
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• 제38권8호
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• pp.562-569
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• 1994

$ C_{18}$ 및 Phenyl 컬럼에서 메탄올-물 및 아세토니트릴-물 혼합액을 이동상으로 하여 21종의 페놀일치환체들의 머무름을 조사하여 치환기가 머무름에 미치는 영향을 알아보았다. 아미노페놀을 제외한 모든 시료의 머무름은 Phenyl 컬럼보다 $ C_{18}$컬럼에서 더 컸으며, 두 이동상에 대해서는 물의 부피퍼센트가 같을때 메탄올계에서 더 컸다. 일반적으로 일치환 페놀류의 파라 이성질체는 메타 이성질체보다 빨리 용리되었고, 오르토와 메타 이성질체 사이에서는 용리순서가 치환기의 극성에 따라 다르게 나타났다. 페놀 일치환체들의 머무름은 시료와 미반응된 실란올과의 상호작용의 영향을 받는대 이러한 미반응된 실란올의 영향은 치환기의 hydrogen bonding acceptor basicity(${\beta}$)가 클수록 크게 나타났고 Phenyl 컬럼보다 $ C_{18}$ 컬럼에서 이들의 영향이 크게 나타났다. 시료의 van der Waals volume(VWV)과 ${\beta}$값을 함께 고려한 파라미터 (1.01VWV/100-1.84${\beta}$)와 시료의 머무름(log k')과는 좋은 직선관계가 있다. 따라서 $ C_{18}$ 및 Phenyl 컬럼에서 페놀 일치환체들의 머무름은 시료의 (1.01VWV/100-1.84${\beta}$)값으로 쉽게 예측할 수 있음을 알았다.

• 한국지하수토양환경학회:학술대회논문집
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• 한국지하수토양환경학회 2001년도 추계학술발표회
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• pp.19-22
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• 2001

The effects of pH on the sequential sorption/desorption of chlorinated phenols (2-chlorophenol, 2.4-dichlorophenol and 2,4,5-trichlorophenol) in HDTMA-montmorillonite were investigated by maintaining pH 4.85 or 9.15 in the sequential batch sorption and desorption experiments. The chlorinated phenols are hydrophobic ionizable orginic compounds; they can exist as either neutral (pH << pKa) or anionic (pH >> pKa) forms. Among the tested chlorinated phenols, 2,4,5-trichlorophenol showed the highest sorption affinity at pH 4.85 as expected by the $K_{ow}$ . Neutral speciation at pH 4.85 exhibited higher sorption affinity than anionic speciation at pH 9.15. Our results indicates that desorption of chlorinated phenols is strongly dependent on pH of the aqueous phase. Freundlich model was used to analyze the single-solute sorption/desorption results. The ideal adsorbed solution theory(IAST) was employed to predict the hi-solute sorption/desorption equilibria.

• 대한화학회지
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• 제56권6호
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• pp.706-711
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• 2012

Hindered phenols and alcohols were protected as their corresponding ethers using different alkylating agents in presence of KOH/DMSO under microwave irradiation. $$R-OH\;{KOH/DMSO,\;R^{\prime}-X,\;MW \\{\vec{10-15\;Mins,\;80%-90%\;Yield}}}\;R^{{/}^O{\backslash}}R^{\prime}$$.

• 한국환경과학회지
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• 제8권2호
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• pp.233-240
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• 1999

Industrial waste which highly loaded by halogenide phenols was photooxidized by laboratory-scale photooxidation of these organic impurities in the presence of aerotropic and titaniumdioxide as photocatalyst. The disapperance of organic compounds was determined as a function of the irradiation time. Some contaminants such as 2-chlorophenol, 2-bromphenol, 3-bromphenol, 4-bromphenol, 2,4-dibromophenol and 2,6-dibromophenol were photodegraded separately to obtain information on the reaction rates, reactivities, and reaction mechanisms of the photooxidation, and on the stoichiometric correlation between organic reactant and inorganic products concentration in the course of the photocatalytic photoreaction.

• 환경위생공학
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• 제15권4호
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• pp.35-43
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• 2000

Aqueous solutions of chlorobenzene and chlorinated phenols were exposed to 200kHz ultrasound with a power of $6.0W/\textrm{cm}^2$ per unit volume on sonochemical reactor under ambient temperature and pressure conditions. The concentration of chlorobenzene and chlorinated phenols decreased with ultrasound, indicating first-order kinetics. Degradation rate constants are calculated from the slope of plots. The order of the rate constants is as follows : 2-chlorphenol(2-CP)$\leq$ 4-chlorophenol(4-CP)<3-chlorophenol(3-CP)$5.63~9.96({\times}10^{-2})min^{-1}$ under argon. The degradation was suppressed by the addition of t-BuOH and the suppressed yield was agreed with their reactivity for hydroxy radical. The main products of these systems were formic acid, acetic acid, small amount of methane and inorganic carbon forms as carbon dioxide, carbon monoxide in sonolysis of chlorinated phenols, and also these results agreed with change of TOC.

• Bulletin of the Korean Chemical Society
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• 제23권3호
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• pp.427-431
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• 2002

A screen printed graphite electrode has been developed for a simple and sensitive determination of phenolic compounds in an aqueous solution. The electrode developed uses a simple and effective screen printing technique with ${\alpha}-Cyclodextrin({\alpha}-CD)$ modified graphite ink. Phenols were captured on the surface of the ${\alpha}-CD$ modified electrode through complex formation. The phenol/ ${\alpha}-CD$ complex was deposited and quantified electrochemically using cyclic voltammetry (CV), differential pulse voltammetry (DPV) and square wave voltammetry (SWV). The optimization of the experimental parameters was performed in regard to electrode composition, pH, temperature, sample preconcentration time. Interferences from other organic compounds were investigated. The detection limit for phenols was 500 ${\pm}7$ nM for DPV, with the linear range of 0.5 ${\mu}M$ -25.0 ${\mu}M$ and 30 ${\pm}2$ nM for SWV, with the linear range of 30 nM - $50{\mu}M$, respectively.

• Environmental Analysis Health and Toxicology
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• 제21권3호
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• pp.239-244
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• 2006

Caenorhabditis elegans(C. elegans) is a free-living soil nematode that commonly used as a biological model and recently, much work has been done using C. elegans as a toxicity model. To evaluate the acute toxicity of phenols to C. elegans, worms were subsequently exposed to nine different xenobiotics. This study described lethal toxicity, reproductive toxicity and movement inhibition using 2-propylphenol, 4-propylphenol, 2-tert-butylphenol, 3-tert-butylphenol, 4-tert-butylphenol, 2-phenylphenol, 4-phenylphenol, nonylphenol and 4-dodecylphenol to C. elegans for 24 hr or 72 hr. We found that phenols used in this study were very toxic to C. elegans. The order of lethal toxicity, reproductive toxicity and movement inhibition is as follows. 4-propylphenol > 2-phenylphenol > 2-tert-butylphenol > 2-propylphenol > nonylphenol > B-tert-butylphenol > 4-dodefylphenol > 4-tert-butylphenol > 4-phenylphenol.