• 상하수도학회지
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• 제25권5호
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• pp.777-782
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• 2011

The residual treatment facilities in WTP(water treatment plant) play an important role in solid-liquid separation. At present, it is difficult to solve problems related with thickening and dewatering of WTP sludge, and discharging waste water to river. The quantity of residuals generated from water treatment plants depends upon the raw water quality, dosage of chemicals used, performance of the treatment process, method of sludge removal, efficiency of sedimentation, and backwashing frequency. Sludge production by the physical separation of SS(Suspended Solid) occurs under quiescent conditions in the primary clarifier, where SSs are allowed to settle and to consolidate on the clarifier bottom. Raw primary sludge results when the settled solids are hydraulically removed from the tank. In this study, Drawing characteristics of the sludge thickening in the thickener of Water Treatment Plants was simulated by Using CFD(Computational Fluid Dynamics.

• 상하수도학회지
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• 제28권2호
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• pp.249-255
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• 2014

So many drinking water treatment plants are under various difficulties by new reinforced effluent standards. Since the target turbidity, much higher than annual average, for designing sludge thickener have to be set to confront high turbidity season, the sludge at thickener should be put up for a long time during usual days. So the soluble manganese and chloroform may be formed under the anaerobic environment in the sludge thickener when the sludge retention time is longer with low turbidity. This phenomenon results in difficulties to keep regulatory level of the discharged effluent. For an effort to overcome the problems, a sludge aeration was successfully implemented into the thickening process. As a result, the final effluent quality and sludge volume were much improved; 41 % of manganese, 62 % of chloroform and 35 % of sludge volume. Additionally, effluent quality was improved ; 61 % of Manganese on aeration with pH control and we could make sure of stability effluent quality despite a long sludge retention time. We recommended the standard of installation sludge aeration equipment to nationally supply water treatment plant under effluent water quality problem ; Manganese, Chloroform, etc.

• 한국지반환경공학회 논문집
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• 제16권5호
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• pp.27-33
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• 2015

정수공정 중에 응집된 망간은 슬러지 농축조에 체류하는 동안 재용출 되어 배출수의 망간 허용기준치를 초과하는 문제가 발생되고 있다. 본 연구에서는 정수공정 중에 슬러지 농축조 배출수의 pH를 조정함으로써 망간 농도에 미치는 pH의 영향에 대하여 연구하였다. 초기 pH 6.1에서는 응집된 슬러지로부터 망간이 재용출 되어 청정지역 배출 기준인 2mg/L를 초과하였으나 NaOH, KOH, CaO, $Ca(OH)_2$, $CaCO_3$ 등 알칼리 물질을 이용하여 pH를 상승시켰을 경우 망간 농도를 청정지역 배출 기준 이하로 낮출 수 있었다. 또한 알칼리성 물질로서 석회석 광산에서 선별과정 중 발생하는 폐석회석을 이용하여 정수장 슬러지의 망간 재용출을 억제할 수 있는 가능성을 확인하였다.

• 환경위생공학
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• 제8권1호
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• pp.117-127
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• 1993

When incineration method is utilized as a disposal process of sludge, the treatment generally consists of thickening, dewatering and incineration, implying that sludge dewaterability has a colose relationship with operating condition of a thickener. Dewatering factors should be, therefore investigated for achieving effective sludge treatment. No research on this has been performed in Korea. This study has focused on the evaluation on the effects of thickener operating variables on sludge dewatering, including sludge feed types and retention time. Mixing ratio of the first and the second sludge and operation time were varied in order to observe the change of dewaterability and optimum input of chemical conditioner.

• 상하수도학회지
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• 제28권4호
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• pp.479-489
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• 2014

Membrane backwashing waste shows seasonally different characteristics and it has bad settleability differently from general backwashing waste in water treatment plant. When chemicals was injected to membrane backwashing waste, the settleability was better than chemicals was not injected. However, when settled lower sludge was not discharged, flowing sludge continuously was concentrated over a certain surface and floatation penomena occurred according to flowing velocity. When the lower sludge was discharged continuously in the thickener to prevent floatation penomena of turbidity materials, the depth of sludge surface was the least and the settleability increased.

• 상하수도학회지
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• 제21권6호
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• pp.709-715
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• 2007

The dewaterability of a sludge can be characterized by two ways: the residual moisture content in the sludge cake after dewatering process, and the filtration of the sludge. Time to filter (TTF) represents filtration processes that are special cases of the flow through a solid matrix concept. TTF characterizes a resistance to filtration. The sludge resistance, in turn, can be subdivided into resistances associated with the solid phase and the liquid phase to evaluate the effect of each of the two phases on sludge dewaterability. In order to determine the dewatering characteristics of the water sludge samples, TTF and zeta potential were measured. For these studies cationic polymer was chosen for water sludge dewatering experiments. The zeta potential of thickener sludges neared from minus values to zero values till 4 days after sampling. The dewaterability of thickener sludges using cationic polymer was deteriorated according to the increase of detention time. As the detention time was increased from 4 to 10 days, the optimal dose of the polymer was increased from 4 to 8mg/L. Therefore, the optimal detention time plays an important part for the dewaterability of a sludge.

• 대한환경공학회지
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• 제36권2호
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• pp.113-118
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• 2014

전 국가적으로 많은 정수장에서는 강화된 수질기준을 준수하는데 많은 어려움을 겪고 있다. 일반적으로 정수장 배출수처리시설은 고탁도를 기준으로 설계되기 때문에, 평상시에는 설계된 기간보다 장기간 체류할 수밖에 없는 실정이다. 평균 혹은 저탁도 원수가 유입되는 대부분 기간 동안 슬러지는 농축조에서 장기체류하기 때문에 혐기화되어, 용해성 망간 및 클로로포름이 형성된다. 위 문제를 해결하기 위해서 경제적이고, 손쉽게 도입 가능한 슬러지 폭기 공법을 개발하였으며, 본 연구는 이 공법의 원리 및 효과를 분석한 것이다. 슬러지 폭기 공법의 원리는 산화된 입자성 망간이 용해성 망간으로 환원되는 것을 방지하며, 생성된 클로로포름을 대기중으로 배출 제거시키며, 슬러지 입자를 균질화 시켜 침강성을 개선하는 것이다. 위 공법의 효과분석을 위하여 정수장 농축조에서 슬러지를 폭기시킨 후 상징수의 망간 및 클로로포름을 측정하고, 슬러지의 고-액 계면의 높이를 측정한 결과, 비폭기 경우에 비해 망간은 41%, 클로로포름은 62% 슬러지 부피는 35% 감소되는 효과를 얻었다.

• 한국습지학회지
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• 제17권4호
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• pp.414-420
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• 2015

질소는 수계 부영양화를 유발하는 주요 원인이며, 수계 보호를 위해 반드시 처리해야 하는 오염물질이다. 본 연구에서는 고농도 질소를 처리하여 하수처리장 운전 효율 증대를 위한 방안을 연구하고자 하였다. 약 250일간 하수처리장 농축조상징액을 이용하여 실험실 규모 반응조를 운전하였다. 실험실 반응조 운전은 안정적인 아질산화 반응을 유도하고, 관련 운전 인자 영향을 분석하고자 하였다. 연구 결과 체류시간 조절을 통해 인위적으로 아질산화 반응이 유도가능한 것을 확인하였으며, 안정적인 아질산화 반응이 유도되는 구간을 파악하였다. 특히, 체류시간 1일 조건에서는 90%에 가까운 고효율의 아질산화율을 보이는 것을 확인하였다. 특히 ammonium nitrogen load는 암모니아성 질소 제거율과 아질산화율에 영향을 미치는 것으로 나타났다. 높은 ammonium nitrogen load 조건에서는 아질산화율과 암모니아성 질소 효율이 감소하였다. 반면, 낮은 ammonium nitrogen load 조건에서는 아질산화율이 감소하는 것으로 나타났다. 이는 아질산화 반응을 위해 암모니아성질소 농도 및 체류시간의 조절이 필요하다는 것을 의미한다. 농축조 상징액과 같은 슬러지 처리 공정 내 고농도 질소를 함유한 폐수는 아질산화 반응을 적용할 수 있으며, 이는 하수처리장 개조 방안으로 제안 될 수 있을 것으로 판단된다.

• 상하수도학회지
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• 제8권1호
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• pp.44-52
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• 1994

The purpose of this experimental research was focused to improve the quality of the effluent and the yielded sludge when the papermill wastewater was treated by the indirect aerated submerged biofilter as a second treatment method of papermill wastewater. Changing the various experimental factors(Nutrient additions or not, HRT, F/M ratio, recirculation ratio, etc) with indirect aerated biofilter, the results obtained are as follows. 1. Because of the microbes concentration could be sustained to $9,000mg/l$ in submerged biofilter and then the volumetric organic loads could be increased to $2.7kg-BOD/m^3/day$(that of activated sludge is $0.8kg-BOD/m^3/day$), the reactor volume can be reduced to one third of the activated sludge treatment. 2. Because of the yield coefficient(Y) and the endogenous decay coefficient(kd) were revealed 0.4 and 0.07/d, the yielded sludge volume was reduced by for compared with that of the activated sludgg process. 3. The concentration of the sloughed sludge in the reactor was 2.62~4.01%, so the thickener could be omitted in the papermill wastewater sludge treatment process. 4. When the operating was conducted at HRT of 4hrs, the treatment efficiencies of BOD and COD were obtained 80% and 70%, Therefore operating time can be reduced to one half of the activated sludge treatment.

• 한국환경과학회지
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• 제13권6호
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• pp.571-579
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• 2004

There is a need to improve the efficiency of the existing sanitary treatment facilities, because the effluent standard becomes more stricter and septic sludge increased. Thus, operating processes of sanitary treatment system in M city changed with installation of additional facilities. Process modifications were as follows: Dilution water was added to the next process after primary aeration tank. Some secondary sedimentation sludge was recycled to primary aerator so that most of the organics were stabilized in primary aeration tank under automatic control of dissolved oxygen. The line of effluent from dewatering process flowing to the activated sludge tank was changed to the primary aerator. The primary sedimentation sludge line was linked to a thickener. Polymer was added to the activated sludge tank. The effluent of primary aerator and aerobic digester was recycled from the 5th to the 1st sector. As consequencies of above process modifications, the improvement of removal efficiency was achieved as BOD 54%, COD 42%, SS 61%, T-N 39%, and T-P 12%, respectively.