본 연구에서는 건축폐기물로 분류되는 레미콘회수수를 재활용함과 동시에 지구온난화의 주범 인 CO2의 자원화를 위한 시스템의 공정최적화를 진행하였다. 레미콘회수수를 이용한 액상탄산화 반응에 서 가장 중요한 공정은 Ca2+를 용출하는 공정이다. 일정량의 레미콘회수수를 이용해 고순도의 CaCO3을 생성하기 위해 Ca2+ 용출시 질산에 의해 낮아지는 pH 농도를 기준으로 실험을 진행하였으며, CO2는 발전기 배기가스를 이용해 MEA용액에 포집하였다. 본 연구를 통해 1톤의 레미콘회수수에서 최대 11 kg의 CaCO3를 합성할 수 있었다. 생성된 CaCO3 분석결과 제지용으로 사용 가능한 것을 확인하였다.

본 연구는 잉여슬러지와 차아염소산나트륨을 혼합하여 제조한 차아염소산나트륨 처리 슬러지를 침지형 분리막이 설치된 생물반응조에 주입하여 수처리 미생물에 기질을 공급하고 수처리에 적합한 pH와 알칼리도를 유지함으로써 응집제 주입 없이 방류수의 총질소 농도 20 mg/L, 총인 농도 0.2 mg/L 이하로 처리할 수 있는 MBR 하수처리공정을 개발하였다. 개발된 공정은 별도의 응집제 주입 없이 질소와 인의 법적 방류수 수질기준 을 만족하였고, 향후 하수처리장 약품비용 절감에도 기여할 것으로 기대된다.

본 연구에서는 산기량의 변화에 따른 임계 투과유속을 투과유속단법으로 측정하였다. 유효 막 면적이 85 cm2이고 공칭 세공크기가 0.4 μm인 중공사형 막모듈을 MLSS 5,000 mg/L인 활성슬러지 수용액에 침지시켜 투과 실험하였다. 산기시 키지 않을 경우 임계 투과유속은 15.2 L/m2⋅h로 측정되었으나 산기량을 100에서 1,000 mL/min까지 증가시키면 임계 투과 유속이 20.6에서 32.5 L/m2⋅h까지 크게 상승하였다.

Waste SiC powders obtained from silicon wafer sludge have very low density and a narrow particle size distribution of 10-20 μm. A scarce yield of C and Si is expected when SiC powders are incorporated into the Fe melt without briquetting. Here, the briquetting variables of the SiC powders are studied as a function of the sintering temperature, pressure, and type and contents of the binders to improve the yield. It is experimentally confirmed that Si and C from the sintered briquette can be incorporated effectively into the Fe melt when the waste SiC powders milled for 30 min with 20 wt.% Fe binder are sintered at 1100oC upon compaction using a pressure of 250 MPa. XRF-WDS analysis shows that an yield of about 90% is obtained when the SiC briquette is kept in the Fe melt at 1650oC for more than 1 h.

정수슬러지를 탄화 및 활성처리하여 흡착제를 제조하였으며, 이를 이용한 황화수소 흡착특성을 고찰하였다. 제조 된 흡착제에 대한 BET측정 및 SEM 등 물성분석을 실시하였으며, 황화수소를 대상으로 회분식의 흡착평형실험 을 실시하였다. 실험변수로는 활성처리시 적용되는 약품종류 및 농도 등이 적용되었다. 실험결과, 정수슬러지는 탄화나 약품첨착과정을 통해 커다란 성능 향상이 이뤄짐을 알 수 있었다.

본 연구에서는 사인파형 투과유속 운전방식을 중공사형 분리막에 적용하여 운전시간에 따른 막간차압(TMP)을 측 정하였다. 유효 막면적이 100 cm2이고 공칭 세공크기가 0.45 μm인 중공사막 모듈을 MLSS 5,000 mg/L 활성슬러지 용액으로 투과 실험하였다. 연속적인 단계별 투과유속 변화법으로 임계 투과유속을 측정하였으며 그 값은 26.6 L/m2⋅hr이었다. 여과 운전/정지이완(FR), 정지이완시 역세척(FR/BW) 및 사인파형 투과유속 연속운전(SFCO) 방식에 따른 TMP를 측정하였다. 임 계 투과유속보다 낮은 15, 20 및 25 L/m2⋅hr에서는 SFCO 운전방식이 FR 및 FR/BW에 비하여 효과적이었다. 그러나 임계 투과유속 이상에서는 FR/BW 운전방식이 SFCO보다 효과적으로 막오염을 제어할 수 있음을 확인하였다.

최근 방류수 수질 강화에 따라 총인 처리시설의 설치와 응집제 사용량이 증가하고 있다. 본 연구는 유입하수에 포함된 응집제 성분(Al3+, Fe3+ 등)을 활용하여 PO43-와 응집시킴으로써 하수처리공정에 별도의 응집제 주입 없이 총인 농도를 0.2mg/L 이하로 제거할 수 있는 MBR 하수처리공정을 개발하는 것이다. 활성슬러지와 차아염소산나트륨으로 제조한 알칼리슬러지를 MBR 공법의 생물반응조에 주입하여 적정 pH를 유지시킴으로써 유입하수 중의 용존성 이온을 상호 응집시켜 고형화 하였고 분리막으로 고액 분리하여 하수처리수의 총인 농도를 0.2mg/L이하로 달성하였다. 이 연구를 통해 개발한 공법은 응집제 주입 없이 하수처리수의 총인 농도를 0.2mg/L이하로 제거하여 약품비용을 절감에 기여할 것으로 예상된다.

본 연구에서는 dimethylformamide (DMF)와 acetone의 혼합용액에 산화그래핀(graphene oxide, GO)을 분산시키고 기질 고분자인 PVdF (polyvinylidene fluoride)를 도입하여 전기방사법으로 나노섬유를 제조하였다. 또한 PVdF/GO 복합 나노 섬유를 평막 형태로 적층시켜 기공크기 0.4 μm인 정밀여과막을 제조하였다. 그리고 GO의 고유한 항균 특성으로 생물학적 오염을 줄일 수 있는 PVdF/GO 복합막의 막오염을 평가하기 위하여 막간 압력차(transmembrane pressure, TMP)를 측정하였 다. 유효 막면적이 0.01 m2인 PVdF/GO 평막과 상용화된 MBR용 CPVC (chlorinated polyvinyl chloride) 평막을 MLSS 4,500 mg/L인 활성슬러지 수용액 내에서 동시에 투과 실험하였다. 공기를 주입하지 않을 경우, 투과유속이 10 L/m2⋅h일 때 PVdF/GO 막의 TMP는 CPVC 막의 최대 79%까지 감소하였다. 또한 운전/휴직 방식으로 운전할 경우, 10 L/m2⋅h일 때 PVdF/GO 막의 TMP는 CPVC 막의 최대 69%까지 감소함을 확인하였다.

Recently, Korea’s municipal wastewater treatment plants generated amount of wastewater sludge per day. However, ocean dumping of sewage sludge has been prohibited since 2012 by the London dumping convention and protocol and thus removal or treatment of wastewater sludge from field sites is an important issue on the ground site. The hydrothermal carbonization is one of attractive thermo-chemical method to upgrade sewage sludge to produce solid fuel with benefit method from the use of no chemical catalytic. Hydrothermal carbonization improved that the upgrading fuel properties and increased materials and energy recovery ,which is conducted at temperatures ranging from 200 to 350°C with a reaction time of 30 min. Hydrothermal carbonization increased the heating value though the increase of the carbon and fixed carbon content of solid fuel due to dehydration and decarboxylation reaction. Therefore, after the hydrothermal carbonization, the H/C and O/C ratios decreased because of the chemical conversion. Energy retention efficiency suggest that the optimum temperature of hydrothermal carbonization to produce more energy-rich solid fuel is approximately 200°C.

The performance of the new aerobic digestion system combined with inorganic sludge separation unit and sludge solubilization unit, CaviTec II, is evaluated. Anaerobic digester effluent sludge is used for feed sludge of CaviTec II system. By addition of CaviTec II, the amount of cake generated is reduced by 27%, and the soluble nitrogen is reduced by 92%.

The residents'odor complaint is steadily increasing by odor causing from sewage system. A current drainage facilities and septic tank are included in the individual sewerage according to Sewerage Act. However, definitions and legal standards of drainage tank are insufficient. In addition, specifications and maintenance standards related to structure and size are not established.In this research, effect of drainage tank in individual sewage facilities on the odor occurrence was studied and the concentrations of H2S and composite odor were measured.From the measurements, the concentration of H2S and composite odor were 1 ppm ~ 5 ppm and 1.04 OU ~ 4.05 OU, respectively, before pump operation. Also, the concentration of H2S and composite odor were 5 ppm ~ 33 ppm and 5.10 OU ~ 35.04 OU, respectively, after pump operation. The concentration of SS in the effluent from drainage tank was ranged from 840 mg/L to 1,980 mg/L. These high concentration of SS seemed to be the major source of foul smell when high concentrated suspended solids in the public sewerage system were decomposed and then emitted.In this research, correlation coefficient (R2) between H2S and composite odor before and after pumping were 0.925 and 0.918, respectively.

The need of reusing sewage sludge is highly increasing as the amount of domestic sewage sludge is growing and sewage management strategies were reinforced. Accordingly, in this research, we studied the composting possibility of sludge in sewage treatment plant J, using dryer facility with indirect system by conducting component analysis of dried sludge and experiment on cultivating crops. It was observed from the component analysis, that the dried sludge is appropriate for both decomposed manure standard of Ministry of Environment and fertilizer standard of Rural Development Administration. Besides, in the experiment on cultivating lettuce, the experimental group(soil + dried sludge) was superior to the control group(soil + bed soil) in apparent condition of leaves tensity and damage by disease and pest. In case of cultivating tomato, the experimental group showed stronger durability of fruits dangling on stems compared to the control group after 9 weeks. Consequently, the excess sludge dried by indirect heating system in the sewage treatment plant J is appropriate for the standard of both Ministry of Environment and Rural Development Administration and show good result in experiment on cultivating crops therefore it can be reused for composting.

본 실험은 실험실적 규모의 침지식 평막형 분리막이 장착된 활성슬러지 생물반응기에 인공폐수를 사용하여 수행하였다. 분리막 운전은 MLSS 5,000 mg/L 활성슬러지 용액을 일정 유량으로 계속 투과시키는 방식과 주기적으로 10분여과/2분휴지 방식으로 구분하여 실시하였다. 산기량은 0.25 L/min로 일정하게 유지한 상태에서 투과유속을 10에서 25 L/m2⋅hr까지 증가시키면서 막간차압을 측정하였다. 또한 분리막 오염 상태를 판단하기 위하여 완전막힘, 표준막힘, 중간막힘, 비압축성케이크 및 선형압축성 케이크 오염 모델을 실험값에 적용하였다. 10분운전/2분휴지 운전방식에서는 매 주기마다 펄스형태로 막간차압이 변화하므로 최고점 및 최저점 연결선으로 구분하여 막오염 모델을 적용하였다. 활성슬러지 케이크 막오염은 이상의 5가지 오염 모델 중 선형압축성 케이크 오염 모델이 모든 투과실험 결과와 가장 잘 일치하였다.

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.

Various treatment system for residuals have applied to save water resources, but most of them were not be satisfied with legal standard consistently. In this study, submerged membrane treatment system was operated to treat water treatment plant residuals and operation parameters was evaluated. Result of this experiment, high concentration organic matters contributed to high increase Transmembrane pressure(TMP) of membrane system(from 0.05 bar to 0.35 bar). And backwash process was effective to stabilize membrane system operation. After Cleaning-In-Place(CIP), permeability was recovered about 100 % from first operation condition. Inorganic matters (Fe, Mn, Al, Ca, Mg) were not effective membrane filtration performance. The quality of residual treatment was satisfied with drinking water quality standard and a treated water from that system was suitable for water reuse.

It is essential to decrease energy consumption and excess sludge to economically operate sewage treatment plant. This becomes more important along with a ban on sea dumping and exhaustion of resource. Therefore, many researchers have been study on energy consumption reduction and strategies for minimization of excess sludge production from the activated sludge process. The aeration cost account for a high proportion of maintenance cost because sufficient air is necessary to keep nitrifying bacteria activity of which the oxygen affinity is inferior to that of heterotrophic bacteria. Also, additional costs are incurred to stabilize excess sludge and decrease the volume of sludge. There were anoxic, aerobic, membrane, deairation and concentration zone in this MBR process. Continuous aeration was provided to prevent membrane fouling in membrane zone and intermittent aeration was provided in aerobic zone through ammonia sensor. So, there was the minimum oxygen to remove NH4-N below limited quantity that could be eliminated in membrane zone. As the result of this control, energy consumption of aeration system declined by between 10.4 % and 19.1 %. Besides, we could maintain high MLSS concentration in concentration zone and this induced the microorganisms to be in starved condition. Consequentially, the amount of excess sludge decrease by about 15 %.

The performance of inorganic sludge separation system is evaluated. Anaerobic digester effluent sludge is used for feed sludge of this system and hydrocyclone is used for inorganic sludge separation. For phosphorus removal and recovery MgCl2 is pumped into MAP growth tank, a component of inorganic sludge separation system. Using this system inorganic sludge which contained less than 40 % of organic matter can be discharged stably and the maximum amount of separated inorganic sludge is 13.4 % of influent sludge based on dry solid. The amount of phosphorus recovered as MAP(as P) is 16.7 % to influent T-P.

Nanotechnology has become one of the fastest developing technologies and recently applied to a variety of industries. Thus, increasing number of nano materials including various nanoparticles would be discharged into wastewater and consequently entering a biological wastewater treatment process. However, the impact of the nano particles on biological wastewater treatment has not been estimated intensively. In this research, we investigated the effect of silica nanoparticle on the oxygen uptake rates (OURs) of activated sludge used in a conventional wastewater treatment process. The inhibition (%) values were estimated from the results of OURs experiments for the silica nanoparticles with various sizes of 10-15, 45-50, and 70-100 nm and concentrations of 50, 250, and 500 ppm. As results, the inhibition value was increased as the size of silica nano particles decreased and the injected concentration increased. The maximum inhibition value was investigated as 37.4 % for the silica nanoparticles with the size of 45-50 nm and concentration of 50 ppm. Additionally, the effect of size and concentration on the inhibition should be considered cautiously in case that the aggregation of particles occurred seriously so that the size of individual particles was increased in aquatic solution.

In order to investigate the effective pretreatment methods in WAS(=waste activated sludge) solubilization, the values of SCOD yield per unit SS (SCOD/gSS.hr) were compared. After the hydrodynamic cavitation with pH of 12.5, SCOD increased to 7800 mg/L, SS decreased to 45 % and the solubilization rate was 29 %. Combination of alkality (pH 12.5) and the cavitation seems to be the optimal condition for sludge solubilization. After the cavitational pretreatment, efficiencies of anaerobic digestion of the unfiltered sludge(the control), raw sludge and pretreated sludge were evaluated with BMP(=biochemical methane potential) tests.For evaluation of the biodegradability characteristics of pretreated sewage sludge, the methane production has been measured for 6 months. The methane production of pretreated sludge increased 1.4 times than that of untreated sludge. The result indicates that the cavitationally pretreated sludge was a better biodegradability substrate in anaerobic condition compared to raw sludge. It is obvious that cavitational pretreatment could enhance not only solubilization but also biodegradability of WAS. In conclusion, cavitational pretreatment of WAS to convert the particulate into soluble portion was shown to be effective in enhancing the digestibility of the WAS.

A lab-scale Anaerobic Baffled Reactor (ABR) was applied to treat a primary sludge taken from a municipal wastewater treatment plant. In this experiment, acidogenic reaction was promoted by operating the ABR with short hydraulic retention time (HRT) to produce sufficient volatile fatty acids (VFA) instead of production of methane. The performance of ABR on the VFA production and total solids reduction was observed with different operating conditions with 2, 4, 6, and 8 days of HRT. Corresponding organic loading rates were 6.7, 3.4, 2.2, and 1.6 kgCODcr /m3·day. As HRT increased the removal rate of TCOD was also increased (82.5, 84.2, 96.9, and 95.9 % in average for HRT of 2, 4, 6, and 8 days, respectively) because the settlement of solids was enhanced in the baffle by the decrease of upflow velocity. At HRT of 2 days the average concentration of VFA in the effluent was measured at 1,306±552 mgCOD/L corresponding to 107 % increment as compared to the VFA concentration in the influent. However, as HRT increased VFA concentraiotn was decreased to 143±552 mgCOD/L at HRT of 8 days. The reduction rates of total solids were 12.2, 26.5, 24.8, and 43.0 % for HRT of 2, 4, 6, and 8 days. As HRT increased the hydrolysis of organic particulate matters in the reactor was enhanced due to the increasing of solids retention time in the baffle zone with low upflow velocity in long HRT condition. Consequently, we found that a primary sludge became a good source of VFA production by the application of ABR process with HRT less than 4 days and the 12-26 % of total solids reduction was expected at these conditions.