• KSBB Journal
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• 제11권5호
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• pp.577-585
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• 1996

본 연구에서는 페놀 분해 능력이 있는 활성슬러지 를 광경화성 수지에 포괄 고정화하여 페놀 분해에 미치는 영향인자에 대하여 조사 검토하였다. 고정화 활성슬러지의 경우 free 활성슬러지 보다 넓은 pH 범위에서 페놀 분해 상대활성도가 높게 나 타났￡며, 고정화비드 직경이 작을수록 페놀분해 시 간이 짧았다. 페놀농도 2000 mg/L까지는 free 활 성슬러지의 분해시간이 짧았으나, 3000 mg/L에서 는 고정화 활성슬러지의 분해능이 높았다. 고정화비 드 주입량에 따른 페놀 분해성은 반융기 내에 주입 된 고정화비드양에 정비례 하지는 않았으나 주입량 이 많을수록 페놀 처리율이 높았다. 고정화 활성슬 러지의 반융에서는 반복샤용 7회 이상일 때의 상대 활성도는 처음의 약 8배 정도 증가하였다. 고정화 활성슬러지를 합성폐수 또는 증류수에서 진탕 또는 정지상태로 20일간 보관한 후에는 700 mg/L의 페놀이 24시간 후면 거의 분해되었으며, 증 류수에 정지된 상태로, 40일간 보관한 후에는 마찬가지로 24시간 후에 96.7 % 이상이 분해되었다. 또 한 고정화 활성슬러지를 합성폐수에서 호기적으로 보존하면 80일간 보존이 가능하였다. 고정화 활성슬러지를 사용한 연속처리에서는 용적 부하 5.59 kg-phenol/m3.d에서 95 % 이상의 페놀 이 제거되었으며, 연속실험에서 페놀제거 효율이 95 % 이상일 때 처리성척을 비교해보면, 고정화 활성 슬러지 빛 free 활성슬러지 용척부하는 각각 7.46, 3 3.72 kg-phenol/m3.day로써 고정화 활성슬러지가 2배 더 높은 부하에서 처리가 가능하였다.

• 한국미생물·생명공학회지
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• 제13권1호
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• pp.33-39
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• 1985

The effects of initial concentration, flow rate, and recycle ratio on the removal efficiency of phenol were studied in a tapered fluidized bed reactor packed with activated carbon which was attached with Candida tropicalis. The optimum conditions of Candida tropicalis were showed that pH was 7.0 and temperature was $30^{\circ}C$, and the specific growth rate of Candida tropicalis was satisfied with the Monod equation up to 500 mg/L of phenol, and beyond it the inhibition of substrate was found. According to the increases of initial concentration and flow rate, the removal efficiency was decreased, as the recycle ratio was increased, the removal efficiency was increased. In the case of flow rate of 10mL/sec and the recycle ratio of 2, the removal efficiency was 90% above for the all of initial concentration. The removal rate of phenol was the first order reaction in this system, and the rate equation of reaction was as follows.

• Environmental Engineering Research
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• 제20권2호
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• pp.181-189
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• 2015

A composite material was tested to eliminate phenol in aqueous solution combining adsorption on activated carbon and photocatalysis with $TiO_2$ in two different ways. A first implementation involved a sequential process with a loop reactor. The aim was to reuse this material as adsorbent several times with in situ photocatalytic regeneration. This process alternated a step of adsorption in the dark and a step of photocatalytic oxidation under UV irradiation with or without $H_2O_2$. Without $H_2O_2$, the composite material was poorly regenerated due to the accumulation of phenol and intermediates in the solution and on $TiO_2$ particles. In presence of $H_2O_2$, the regeneration of the composite material was clearly enhanced. After five consecutive adsorption runs, the amount of eliminated phenol was twice the maximum adsorption capacity. The phenol degradation could be described by a pseudo first-order kinetic model where constants were much higher with $H_2O_2$ (about tenfold) due to additional ${\bullet}OH$ radicals. The second implementation was in a continuous process as with a fixed bed reactor where adsorption and photocatalysis occurred simultaneously. The results were promising as a steady state was reached indicating stabilized behavior for both adsorption and photocatalysis.

• 한국지하수토양환경학회지:지하수토양환경
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• 제13권3호
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• pp.52-58
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• 2008

여러 조건으로 제조한 망간첨착활성탄(Mn-AC)을 유기물과 무기물이 함께 오염되어 있는 합성 폐수처리에 적용하였다. 유기물과 무기물의 대표물질로 각각 페놀과 3가 비소를 선정하였다. Mn-AC의 물리화학적 특성과 안정성을 분석한 후, 회분식 반응조에서 활성탄(AC) 및 Mn-AC에 의한 3가 비소 및 페놀 흡착 특성을 조사하였다. Mn-AC의 안정성 평가를 위해 pH 2에서 4의 산성용액에서 용출되는 망간의 농도로부터 평가하였다. pH 3 이하에서는 Mn-AC로부터 많은 양의 망간이 용출되었지만, pH 4에서는 청정지역 허용기준인 3 ppm 이하의 농도로 용출되었다. Mn-AC에 대한 X-선 회절기 분석결과 첨착된 망간은 $Mn_2O_3$로 밝혀졌다. Mn-AC를 이용한 3가 비소와 페놀의 동시처리 실험결과 3가 비소는 낮은 pH에서 AC보다 높은 산화율을 보였으나, 중성 이상의 pH에서는 AC가 더욱 높은 산화율을 보였다. 활성탄에 망간을 첨착시킴으로서, 비표면적이 13% 감소하였고 이로서 Mn-AC에 의한 페놀제거율은 AC에 비해 8% 정도 줄어들었다. 3가 비소 산화 및 페놀 흡착실험을 통하여 Mn-AC는 복합오염물을 갖는 폐수의 동시처리에 적용될 수 있음을 알 수 있었다.

• 상하수도학회지
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• 제13권4호
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• pp.62-71
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• 1999

The containment retardation capacities of four different aquifers were evaluated in a preliminary study for development of bank filtration in the Young San river area. $NO_3-N$, $NO_2-N$, $NH_4^+-N$, Fe, Mn, phenol, and chloride were selected as the target contaminants and a nonreactive tracer, respectively. Batch isotherm tests were conducted to measure the partition coefficients of the target contaminants. The mass transport parameters of nonreactive tracer were estimated from column tests. From the results of bath isotherm tests, it was shown that lower stream aquifer materials have greater partition coefficients of $NO_3-N$, $NH_4^+-N$, Mn, and phenol than the upper stream aquifer materials; however, there was no significant position-dependent trend for Fe. All aquifer materials tested have the same range of partition coefficients for $NO_2-N$. Column tests showed that the molecular diffusion of Cl- was much less than the mechanical dispersion; and there was no significant difference between the estimated dispersivities of tested aquifer materials. Consequently, it seems that the difference in the containment retardation capacities between four aquifers tested in this study would primarily result not from hydrodynamic dispersion but from partitioning.

• 상하수도학회지
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• 제18권2호
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• pp.165-173
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• 2004

Behavior of hazardous organic compounds including bisphenol A, phtalic acid, and phosphoric acid in low pressure nanofiltration process were investigated. In the case of NTR729HF, rejection of all target organic compounds except 2-H-Benzothiazol and 2-isopropyl phenol was more than 90%. The lowest rejection for 2-H-Benzothiazol was observed in another membranes. The UTC60 and UTC20 showed similar rejection characteristics of hazardous organic compounds. Although the rejection of Bisphenol A, n-buthyl benzenesulfoneamide, N-ethyl-p-toluensulfonamide, 2-H-benzothiazol, p-t-butylphenol and 2-isopropyl phenol was less than 30%, the rejection of tributyl phosphate, triethyl phosphate, camphor, 2,2,4 trimethyl 1,3 pentandiol and diphenyl amine was more than 90% in the case of UTC60 and UTC20. The rejection characteristics of various hazardous organic compounds were converted into one parameter Ks, which was proposed in the diffusion-convection model. The Ks of hazardous organic compounds were discussed by comparing with their solute size represented by Stokes radius. The diffusion convection model considering Ks was successful to interpret rejection characteristics of hazardous organic compounds by low-pressure nanofiltration membranes.

• 한국환경과학회지
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• 제8권2호
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• pp.241-248
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• 1999

The photocatalytic decolorization and photodegradation of wastewater contamininated with dyes such as methyleneblue tetrahydrate(MBT), methyl orange(MO), phenol red(PR) and the mixed dyes have been studied using a batch reactor in the presence of aerotropic and titania. Degussa P25 titanium oxide was used as the photocatalyst and proved to be effective for the dyes-degradation when irradiated with UV-light source emitting the wavelength of 253.7 nm in the presence of air. In addition to removing the color from the wastewater, the photocatalytic reaction simultaneously reduced the COD and optical density which suggests that the dissolved organic compounds have been photooxidized. The reaction rate of disappearance of the dyes were measured as a function of the irradiation times. The photooxidative procedure of the aquatic solution have the first order reaction-kinetics. The rate constants were increased in the order of PR < MBT < $gL^{-1}-TiO_2$ powder were irradiated with the UV -light source.

• 한국물환경학회지
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• 제21권5호
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• pp.505-510
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• 2005

The objective of this study was to remove non-biodegradable matters and ammonia ion in livestock wastewater using Fenton oxidation and Zeolite adsorption process. After coagulation process as 1st treatment, non-biodegradable matters remained after 1st treatment were removed by using OH radical produced in Fenton oxidation process. Zeolite as cation adsoption process was used to remove ammonia ion in 2nd treatment water. As a result of treatment using these processes, NBDCOD removal efficiency was over 90% and ammonia ion was almost removed. Most aromatics or polynuclear aromatics like benzene, phenol and scatol in livestock wastewater wasn't detected after Fenton oxidation process.

• 한국물환경학회지
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• 제22권1호
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• pp.66-73
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• 2006

The purpose of this study was done to evaluate degradation characteristics of non-biodegradable organic matters including aromatic compounds in livestock wastewater using CFZ process. The CFZ process is consisted of coagulation/sedimentation, Fenton oxidation and zeolite adsoption process. degradation charateristics of each treatment water including livestock wastewater were analyzed by UV scanning, FT-IR and GC/MS. After coagulation/sedimentation process as 1st treatment, non-biodegradable matters remained after 1st treatment were removed by using OH radical produced in Fenton oxidation process. As a result of treatment using these processes, NBDCOD removal efficiency was over 90%. Increase of $E_2/E_3$ ratio (absorbance at 250 and 365 nm) in each treatment water means that aromaticity of livestock wastewater decreased. In case of GC/MS, most aromatics or polynuclear aromatics like benzene, phenol and scatol in livestock wastewater almost wasn't detected after oxidation using OH radical.

• 한국환경과학회지
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• 제11권6호
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• pp.553-560
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• 2002

The research was performed to compare to the biofilm characteristics and phenol removal efficiency in RBCs(Rotating Biological Contactor) using Rhodococcus sp. EL-GT(single population) and activated sludge(mixed population) as inoculum. Both reactors showed similar tendency on variations of dry weight, thickness and dry density of biofilm. However, the growth of biofilm thickness in 3 and 4 stage of single population reactor has sustained longer than that of the mixed population reactor. Unlike the mixed population reactor, the dry density of biofilm in the single population reactor had a difference between 1, 2 stage and 3, 4 stage. The single population reactor was stably operated without the decrease of phenol removal efficiency in the range of pH 6 ~ 9 and 15mM phenol was completely degraded in these pH ranges. But in case of the mixed population reactor, the phenol degradability was dramatically decreased at over 5mM phenol concentration because of the overgrowth and detachment of its biofilm.