• 공업화학
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• 제23권5호
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• pp.450-455
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• 2012

수용액으로부터 유독한 플루오레세인 염료 성분을 제거하는데 있어서 활성탄의 활용가능성을 살펴보았다. 회분식 실험을 통해 입상 활성탄에 대한 플루오레세인 염료의 흡착특성을 초기농도, 접촉시간 및 흡착온도를 변수로 하여 조사하였다. 실험결과는 활성탄이 수용액으로부터 플루오레세인 염료를 고효율로 제거할 수 있는 것으로 나타났다. 흡착 평형관계는 298~318 K의 온도범위에서 Freundlich 등온식이 잘 적용되었다. 흡착동력학적 연구로 부터 플루오레세인 염료의 흡착공정은 유사이차속도식에 잘 맞았으며 유사이차속도상수($k_2$)는 플루오레세인 염료 초기농도가 높을수록 감소하였다. 흡착자유에너지변화${\Delta}G^0$), 엔탈피변화${\Delta}H^0$), 엔트로피변화${\Delta}S^0$)를 계산하여 본 결과, 표준자유에너지 변화량이 -17.11~-20.50 kJ/mol로 자발적인 공정임을 알았다. 엔탈피변화량은 33.2 kJ/mol로 양의 값을 나타내어 활성탄에 대한 플루오레세인 염료의 흡착이 흡열반응임을 알 수 있었다.

• 청정기술
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• 제27권2호
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• pp.182-189
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• 2021

입상 활성탄(GAC)에 의한 disperse yellow 3(DY 3) 염료의 흡착을 초기농도, 접촉 시간, 온도 및 pH를 흡착변수로 하는 실험을 통해 등온흡착과 동력학적, 열역학적 파라미터에 대해 조사하였다. pH 변화실험에서 활성탄에 대한 DY 3의 흡착은 산성영역인 pH 3에서 흡착률이 가장 높았다. 이는 양(+)으로 하전된 활성탄 표면과 DY 3의 음이온(OH^-) 사이의 정전기적 인력에 기인한 것으로 판단되었다. DY 3의 흡착평형자료로부터 Langmuir 등온흡착식에 가장 잘 맞았으며, 계산된 분리계수(R_L) 값으로부터 활성탄이 DY 3을 효과적으로 제거할 수 있다는 것을 알았다. 또한, Temkin 식의 흡착열 관련 상수의 값이 20 J mol^-1을 넘지 않아 물리 흡착 공정임을 알 수 있었다. 동력학 실험은 농도별 실험과 온도별 실험 모두 유사 이차 속도식이 오차율 10.72% 이내였다. Weber와 Morris의 입자내 확산 모델의 플로트는 두 단계의 직선으로 나타났다. Stage 2(입자내 확산)의 기울기가 stage 1(경계층 확산)의 기울기보다 작게 나타나 입자 내 확산이 속도지배단계인 것을 확인하였다. 활성탄에 의한 DY 3 흡착의 자유에너지 변화는 298 ~ 318 K에서 모두 음의 값을 나타냈으며, 온도가 증가할수록 자발성이 더 높아졌다. 활성탄에 대한 DY 3의 흡착반응의 엔탈피 변화는 0.65 kJ mol^-1 로 흡열반응이었으며, 엔트로피 변화는 2.14 J mol^-1 K^-1로 양의 값(positive value)을 나타냈다.

• 상하수도학회지
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• 제24권6호
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• pp.661-674
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• 2010

Bacterial biomass and its activity were measured in two kinds of granular activated carbon (GAC), the experimental and existing biofiltration system in a drinking water plant. The bacterial biomass was around 210 to 250 nmol P/g WW with phospholipid concentration at acclimation of ozonation treatment. The phospholipid biomass shows more or less a declining gradient along filter depth and no clear seasonality in its values. On the other hand, the microbial activity of [$^3H$]-thymidine and [$^{14}C$]-acetate incorporation within cells increased significantly along the filter depth, showing the difference of three fold between the upper and bottom layer. These factors support the different microbial composition or metabolic activity along the depth of GAC column. Turnover rates, the rate of bacterial biomass and production of biofilm, ranged from 0.26 /hr to 0.37 /hr, indicating a highly rapid recovery itself at amature state. In the non-ozonation treatment, the bacterial biomass was lower than in the ozonation and biological activity also declined towards the filter depth. The biomass levels during cessation of ozonation in the existing GAC filters were 68% of the actively ozonated state.

• 상하수도학회지
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• 제10권1호
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• pp.121-130
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• 1996

Adsorption isotherms of three trihalomethanes(THMs: $CHCl_3$, $CHBrCl_2$ and $CHBr_2Cl$) and the other organics(p-chlorophenol and sucrose)on activated carbon fibers(ACFs) were measured. Adsorption capacities of the ACFs for these THMs were found to be comparable with or slightly larger than those of granular activated car bons(GACs) which have been widely used for trihalomethanes control in drinking water. Also, the breakthrough curve prediction was successfully carried out using a mathematical model on basis of the assumption that the adsorption equilibrium is instantaneously established when a THM solution contacts the ACF. In practice, THM removal from drinking water was investigated at water works using benchscale ACF adsorptJOn columns. The volume of water treated at a space velocity(SV) of about $100h^{-1}$ was approximately 40 l/g-ACF. The practical adsorption capacities of PCP and sucrose in column adsorption were in good agreement with those of theoretically calculated results using the batch adsorption measurments. And the saturation time model of these substrates in the columns was also agreed succesfully with practical measurments.

• Environmental Engineering Research
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• 제8권4호
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• pp.184-192
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• 2003

• 한국환경보건학회지
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• 제23권3호
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• pp.121-129
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• 1997

This study was performed to delineate the removal phenol in solutions using of ozone, ozone/$H_2O_2$ and ozone/GAC. The disinfection by-product of phenol by ozonation, hydroquinone, was analyzed and it's control process was investigated. The followings are the conclusions that were derived from this study. 1. The removal efficiency of phenol by ozonation was 58.37%, 48.34%, 42.15%, and 35.41% which the initial concentration of phenol was 5 mg/l, 10 mg/l, 15 mg/l, and 20 mg/l, respectively. 2. The removal efficiency of phenol by ozonation was 42.95% at pH 4.0 and 69.39% at pH 10, respectively. The removal efficiencies were gradually increased, as pH values were increased. 3. With the ozone/$H_2O_2$ combined system, the removal efficiency of phenol was 72.87%. It showed a more complete degradation of phenol with ozone/$H_2O_2$ compared with ozone alone. 4. When ozonation was followed by filtration on GAC, phenol was completely removed. 5. Oxidation, if carried to completion, truly destroys the organic compounds, converting them to carbon dioxide. Unless reaction completely processed, disinfection by-products would be produced. To remove them, ozone/GAC treatment was used. The results showed that disinfection by-product of phenol by ozonation, hydroquinone, was completely removed. These results suggested that ozone/GAC should also be an appropriate way to remove phenol and its by-product.

• 해양환경안전학회:학술대회논문집
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• 해양환경안전학회 2003년도 춘계학술발표회
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• pp.205-209
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• 2003

The various pretreatment processes were evaluated for removal of oil pollutants with weathered oil contaminated seawater in a reverse osmosis desalination process. Weathered oil contaminated seawater was made by biodegradation and photooxidation with oil containing seawater. Coagulation, ultrafiltration, advanced oxidation processes and granular activated carbon filtration was used with pretreatment for dissolved organic carbon. Crude oil was removed but. weathered oil contaminated seawater was not removed by biodegradation and coagulation. DOC and E260 was removed with about 20 % and 40 % by membrane filter of cut off molecular weight 500. So, the most of dissolved organic carbon in weathered oil contaminated seawater was revealed that molecular weight was lower than 500. It is difficult to remove DOC in weathered oil contaminated seawater by advanced oxidation processes treatment, but, E260 was removed more high. However, DOC in weathered oil contaminated seawater was easily adsorbed to GAC. It is revealed that DOC was removed by adsorption.

• Bulletin of the Korean Chemical Society
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• 제23권6호
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• pp.817-824
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• 2002

Granular activated carbon(GAC) is highly effective in removing organic compounds which are resistant to biological disintegration in wastewater treatment. However, GAC has reached its full adsorptive capacity, GAC needs to be regenerated before it can be used for a further adsorption cycle. Countercurrent oxidative reaction (COR) technique has been developed and evaluated for the regeneration of spent GAC. Various parameters such as flame temperature, the loss of carbon, destruction and removal efficiency (DRE) of organic compounds, surface area, surface structure, adsorptive capacity, etc. were examined to determine the performance of COR. The results of these tests showed that adosorptive capacity of regenerated GAC was completely recovered, the loss of carbon was controllable, flame temperature was high enough to insure complete destruction and removal $(\geq99.9999%)$ of specific organics of interest, polychlorinated biphenyls (PCBs), that are thermally stable, and on formation of toxic byproducts such as polychlorinated dibenzo-p-dioxins (PCDDs) or polychlorinated dibenzofurans (PCDFs) were detected during the regeneration process. The COR technique is environmentally benign, easy to use and less copital intensive than other available regeneration technologies.

• 청정기술
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• 제27권3호
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• pp.261-268
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• 2021

석탄계 입상 활성탄(CGAC)에 의한 acid black 1 (AB1) 염료의 평형, 동력학 및 열역학적 특성을 초기농도, 접촉 시간, 온도 및 pH 를 흡착변수로 하여 조사하였다. 활성탄에 의한 AB1의 흡착반응은 산성에서는 활성탄의 표면(H⁺)과 AB1이 가지고 있는 sulfite ion (SO₃^-), nitrite ion (NO₂^-) 사이의 정전기적 인력에 의해 일어났고, 최고 흡착률은 pH 3에서 97.7%였다. AB1의 등온 데이터는 Freundlich 등온식에 가장 잘 맞았으며, 계산된 분리계수(1/n) 값으로부터 활성탄에 의한 AB1의 흡착이 효과적인 처리과정이 될 수 있음을 알았다. Temkin 식의 흡착열 관련상수의 값은 물리 흡착 공정(< 20 J mol^-1)임을 나타냈다. 동역학 실험에서는 유사 2차 모델이 유사 1차 모델보다 더 일관성이 있었으며 추정된 평형 흡착량은 오차 백분율의 9.73% 이내에서 잘 일치하였다. 입자내 확산이 흡착 과정에서 속도 조절 단계였다. 활성화 에너지와 엔탈피 변화값으로부터 흡착반응이 물리흡착으로 진행되는 흡열반응임을 확인하였다. 엔트로피 변화는 활성탄 표면에서 AB1의 흡착이 일어나는 동안 고-액 계면에서 활발한 반응에 의해 엔트로피가 증가하는 것으로 나타났다. 자유에너지 변화는 온도증가와 함께 흡착반응의 자발성이 더 커지는 것을 나타냈다.

• 공업화학
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• 제26권2호
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• pp.210-216
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• 2015

석탄계 입상 활성탄을 사용하여 수용액으로부터 brilliant blue FCF 염료의 흡착에 대해 조사하였다. 회분식 실험은 흡착제의 양, 초기농도와 접촉시간과 온도를 흡착변수로 사용하여 수행하였다. 흡착평형자료는 Langmuir, Freundlich 및 Temkin 식을 사용하여 해석한 결과 Freundlich 식이 가장 좋은 일치도를 나타냈다. 평가된 Freundlich 상수(1/n = 0.129~0.212)로부터 이 흡착공정이 적절한 처리방법이 될 수 있음을 알았다. 흡착속도실험자료를 유사일차 및 유사이차 반응속도식에 적용해 본 결과는 유사이차반응속도식에 잘 맞는 것으로 나타났다. 음수값의 Gibbs 자유에너지(-4.81~-10.33 kJ/mol)와 양수값의 엔탈피(+78.59 kJ/mol)는 흡착이 자발적이고 흡열공정으로 진행된다는 것을 나타냈다.