• 상하수도학회지
• /
• 제9권2호
• /
• pp.127-135
• /
• 1995

The purpose of this study was to more fully evaluate the potential for chlorophenol degradation in anaerobic sludge. The pH effects on the ring cleavage of phenol and dechlorination of monochlorophenol isomers and dichlorophenl isomers. This study results are as follows ; Each of the monochlorophenol isomers were degraded in anaerobic sludge. The relatives rates were 2-Chlorophenol > 3-Chlorophenol > 4-Chlorophenol. Biodegradation results for the dichlorophenol isomers in anaerobic sludge are such as 2,3-dichlorophenol and 2,5-dichlorophenol was reductively dechlorinated to 3-chlorophenol, 2,4-dichlorophenol to 4-chlorophenol, 2,6-dichlorophenol to 2-chlorophenol. The two dichlorophenol isomers which did not contain an ortho Cl substituent 3,4-dichlorophenol and 3,5-dichlorophenol were persistent during the 6-week incubation. The rate of dechlorination was enhanced by the presence of a Cl group ortho, rather than para, to the site of dechlorination.

• 상하수도학회지
• /
• 제26권6호
• /
• pp.779-786
• /
• 2012

The degradation of 2-chlorophenol(2-CP) by various AOPs(Advanced Oxidation Processes) including the photo-Fenton process has been examined. In sole $Fe^{2+}$, UV or $H_2O_2$ process without combination, low removal efficiencies have been achieved. But the photo-Fenton process showed higher removal efficiency for degradation of 2-chlorophenol than those of other AOPs including the Fenton process and the UV processes. In the photo-Fenton process, the optimal experimental conditions of 2-chlorophenol degradation were obtained at pH 3 and the $Fe^{2+}/H_2O_2$molar ratio of 1. Also the 2-chlorophenol removal efficiency increased with decreasing of the initial 2-chlorophenol concentration. 3-chlorocatechol and chlorohydroquinone were identified as photo-Fenton reaction intermediates, and a degradation pathway of 2-chlorophenol in the aqueous phase during the photo-Fenton reaction was proposed.

• Membrane and Water Treatment
• /
• 제2권3호
• /
• pp.137-145
• /
• 2011

Membrane processes are major breakthrough for the removal of organic pollutants in water remediation. The separations of solutes depend on nature of the membranes and solutes. The separation performance depends on the nature of the solutes (i.e., molecular volume, polarity, and hydrophobicity) for the same membrane. As 4-chlorophenol is of more dipolemoment compared to 2-chlorophenol, the orientation of the molecule enables it pass through the pores of the membrane, which is of negatively charged and thus separation order follows: 2-chlorophenol > 4-chlorophenol. Hydrophobicity factor also supports the order. Addition of sodium dodecyl sulfate (SDS) to chlorophenol solution shows remarkable increase in separation performance of the membrane. The improvement in separation is 1.8 and 1.5 times for 4- and 2- chlorophenol consecutively in case of 0.0082 M SDS (1cmc = 0.0082 M) in the solution. 4-chlorophenol has better attachment tendency with SDS because of its relatively more hydrophobic nature and thus reflects in performance i.e. the separation performance of 4-chlorophenol with SDS through the membrane is better compared to 2-chlorophenol.

• 한국환경농학회지
• /
• 제21권4호
• /
• pp.261-268
• /
• 2002

Monochlorophenol인 2-, 3- 및 4-chlorophenol에 대해서 D. concentrica, T. versicolor, P. ostreatus 3균주를 이용하여 저항성, 분해능, 분해산물 등을 비교 분석하였다. T. versicolor는 monochlorophenol의 종류 및 농도의 증가에 따라 전혀 영향을 받지 않고 균사 생장이 이뤄지며, D. concentrica는 3-, 4-chlorophenol에서 100 mg/L 이상으로 농도가 증가하면 균사 생장이 느려져 제한을 받고 있는 것으로 나타났다. P. ostreatus는 두 균주와 달리 대조구 자체의 생장이 14일 정도로 상당히 느렸으나 2-, 3-chlorophenol을 첨가했을 때 오히려 1$\sim$2일 정도씩 생장이 촉진되는 결과를 나타냈다. 2-Chloro- phenol 이나 3-chlorophenol에서는 P. ostreatus가 제일 우수한 분해능을 보였으며 4-chlorophenol의 경우는 T. versicolor가 2균주에 비하여 월등하게 우수하게 나타나 균주에 따른 mono- chlorophenol의 분해능에 있어서 차이가 있고, 염소의 치환 위치에 따라 ortho나 meta 보다는 para 위치에 염소가 치환된 4-chlorophenol이 D. concentrica나 P. ostreatus의 경우 분해가 느린 것으로 나타났다. 그러나 T. versicolor는 2-, 3- 및 4-chlorophenol의 저항성 시험에서 균사 생장이 제한을 받지 않고 우수한 생장력을 갖고 있는 것처럼 분해능 시험에 있어서도 우수하였다. 균주별로 pH와 균사량은 P. ostreatus > T. versicolor > D. concentrica 순으로 높았으며, 균주내에서 배양일수별로 pH의 변이는 유동적이었고 균사량은 조금씩 증가하였으나 뚜렷한 차이는 없었다. 즉, 2-, 3- 또는 4-chlorophenol의 목질분해균을 이용한 분해에 있어서 pH 및 균사량은 monochlorophenol의 분해능과는 상관관계가 낮은 것으로 나타났다. T. versicolor와 P. ostreatus의 경우는 높은 laccase의 유도 효과를 나타내면서 monochlorophenol의 분해에 영향을 주는 것으로 생각된다. Monochlorophenol의 분해산물로는 1,3,5-trihydroxyl benzene, 1-ethyl-1-hydroxyl poltane, 2-pro-penoicacid, methylmalonic acid, 2-methyl-4-keto-pentan-2-ol 등과 지방산의 일종인 tetradecanoic acid, hexadecane, hept-adecanoic acid, octadecanoic acid 등이 확인되었다.

• Bulletin of the Korean Chemical Society
• /
• 제25권8호
• /
• pp.1195-1201
• /
• 2004

Tyrosinase was covalently immobilized on platinum electrode according to the method we developed for laccase (Bull. Korean Chem. Soc. 2002, 23(7), 385) and p-chlorophenol, p-cresol, and phenol could be detected with sensitivities of 334, 139 and 122 nA/ ${\mu}M$ and the detection limits of 1.0, 2.0, and 2.5 ${\mu}M$, respectively. The response time ($t_{90\%}$) is 3 seconds for p-chlorophenol, and 5 seconds for p-cresol and phenol. The optimal pHs of the sensor are in the range of 5.0- 6.0. This sensor can tolerate at least 500 times repeated injections of p-chlorophenol with retaining 80% of initial activity. In case of tyrosinase and laccase co immobilized platinum electrode, the sensitivities are 560 nA/ ${\mu}M$ for p-phenylenediamine (PPD) and 195 nA/ ${\mu}M$ for p-chlorophenol, respectively. The sensitivity of the bi-enzyme sensor for PPD increases 70% compared to that of only laccase immobilized one, but the sensitivity for p-chlorophenol decreases 40% compared to that of only tyrosinase immobilized one. The sensitivity increase for the bi-enzyme sensor for PPD can be ascribed to the additional catalytic function of the co-immobilized tyrosinase. The sensitivity decrease for p-chlorophenol can be explained by the “blocking effect” of the co-immobilized laccase, which hinders the mass transport through the immobilized layer. If PPD was detected with the electrode that had been used for p-chlorophenol, the sensitivity decreased 20% compared to that of the electrode that had been used only for PPD. Similarly, if p-chlorophenol was detected with PPD detected electrode, the sensitivity also decreased 20%. The substrate-induced conformation changes of the enzymes in a confined layer may be responsible for the phenomena.

• 한국환경과학회지
• /
• 제22권9호
• /
• pp.1089-1095
• /
• 2013

The degradation of 3-chlorophenol(3-CP) by various AOPs(Advanced Oxidation Processes) including the ultraviolet / hydrogen peroxide, the Fenton and the ultraviolet(UV)-Fenton process has been conducted. The highest removal efficiency for 3-CP in the aqueous phase was obtained by the UV-Fenton process among the AOPs. In the UV-Fenton process, The removal efficiency of 3-CP decreased with increasing pH in the range of 3 to 6, and it decreased with increasing initial concentration. As the intermediates of 3-CP by UV-Fenton reaction, 3-chlorocatechol, 4-chlorocatechol, and chlorohydroquinone were detected thus the degradation pathways were proposed.

• 상하수도학회지
• /
• 제27권1호
• /
• pp.31-38
• /
• 2013

The degradation of 4-chlorophenol(4-CP) by various AOPs(Advanced Oxidation Processes) with continuous feeding of $H_2O_2$, including the ultraviolet/hydrogen peroxide, the Fenton and the photo-Fenton process has been investigated. The photo-Fenton process showed the highest removal efficiency for degradation of 4-chlorophenol than those of other AOPs including the Fenton process and the combined UV process with continuous feeding of $H_2O_2$. In the photo-Fenton process, the optimal experimental condition for 4-CP degradation was obtained at pH 3. Also the 4-CP removal efficiency increased with decreasing of the initial 4-CP concentration. 4-chlorocatechol and 4-chlororesorcinol were identified as photo-Fenton reaction intermediates, and the degradation pathways of 4-CP in the aqueous phase during the photo-Fenton reaction were proposed.

• 한국지하수토양환경학회지:지하수토양환경
• /
• 제19권3호
• /
• pp.47-55
• /
• 2014

Arthrobacter chlorophenolicus A6 possesses several monooxygenases (CphC-I, CphC-II, and CphB) that can catalyze the transformation of 4-chlorophenol (4-CP) to hydroxylated intermediates in the initial steps of substrate metabolism. The corresponding genes of the monooxygenases were cloned, and the competent cells were transformed with these recombinant plasmids. Although CphC-II and CphB were expressed as insoluble forms, CphC-I was successfully expressed as a soluble form and isolated by purification. The specific activity of the purified CphC-I was analyzed by using 4-CP, 4-chlorocatechol (4-CC), and catechol (CAT) as substrates. The specific activities for 4-CP, 4-CC, and CAT were determined to be 0.312 U/mg, 0.462 U/mg, 0.246 U/mg, respectively. The results of this study indicated that CphC-I is able to catalyze the degradation of 4-CC and CAT in addition to 4-CP, which is a primary substrate. This research is expected to provide the fundamental information for the development of an eco-friendly biochemical degradation of aromatic hydrocarbons.

• 환경위생공학
• /
• 제15권4호
• /
• pp.35-43
• /
• 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.

• 한국세라믹학회지
• /
• 제41권6호
• /
• pp.485-492
• /
• 2004

비정질알루미나와 기공형성제를 물과 혼합하여 원통형으로 성형하고 수화, 건조 및 소성하여 직경 5mm의 ${\gamma}$알루미나 펠릿을 제조하였다. 이를 Fe$(NO_{3})_{3}$.$9H{2}O$ 용액과 $CH{3}COOH$ 혼합용액에 침척시키고 $200^{\circ}C$ 온도로 3시간 수열처리 하여 펠릿을 담지시킨 후 건조와 소성공정을 통하여 촉매를 제조하였다. 이와 같이 수열법에 의해 제조딘 산화철 담지${\gamma}$알루미나 촉매를 환경촉매로 적용하기 위해 4-chlorophenol과 같은 난분해성물질을 촉매를 사용하지 않는 오존단독공정과 촉매를 사용하는 촉매오존(catalytic ozonation)공정으로 구분하여 OH 라티칼 전환반응 개시제로서의 기능과 그 분해특성을 비교하였다.