The anaerobic digestion process produces methane while stabilizing sludge. As of 2020, 62 anaerobic digesters in public wastewater treatment plants are operational in Korea. Many researchers have studied to improve digester performance. Thermal hydrolysis technology is one of the pre-treatment methods for treating sludge. Reduced retention time and enhanced biogas production are the main advantages of sludge disintegration at relatively high temperatures and pressures. But nutrients like nitrogen and phosphorus are released from the pre-treated sludge. Phosphorus is a non-renewable resource that is essential to food production. Wastewater receives 20% of the total phosphate discharge, while 90% of the influent phosphorus load is in sludge. For efficient phosphorus recovery, it is essential to comprehend the phosphorus release characteristics during wastewater treatment, including anaerobic digestion. Biological or chemical processes can achieve phosphorus removal to comply with the effluent discharge limits regulations. The three primary sources of phosphorus in sludge are aluminum-bound phosphorus (Al-P), polyphosphate in phosphorus-accumulating organisms (PAOs), and iron-bound phosphorus (Fe-P). Anaerobic digestion is the typical method for recovering carbon and phosphorus. However, previous research has demonstrated that most phosphorus in anaerobic digestion occurs as a solid phase coupled with heavy metals. Therefore, the poor mass transfer rate results in a slow phosphorus release. Due to the recent growth in interest and significance of phosphorus recovery, many researchers have studied to improve the quantity of phosphorus released into the liquid phase through chelation addition, process operation optimization, and disintegration using sludge pre-treatment. The study aims to investigate characteristics of the phosphorus release associated with the thermal hydrolysis breakdown of sludge and propose a method for recovering phosphorus in a wastewater treatment plant. When solubilizing sludge using thermal hydrolysis pre-treatment, organic phosphates, inorganic phosphates, and polyphosphates are converted into ortho-phosphate. Therefore, applying thermal hydrolysis, anaerobic digestion, and phosphorus recovery processes (struvite formation or microbial electrolysis cells) can recover carbon and phosphorus.

Several disposal processes for waste sludge from wastewater treatment plants such as landfill, ocean dump, incineration, reuse as fuels or fertilizers are practiced. However, ocean dumping is prohibited by international treat. New constructions of landfill sites or incineration facilities are limited by NIMBY and reuse processes are still suffering from low energy yield. Therefore, development of alternative processes for sludge disposal are currently needed. In this study, alternative technique for sludge solubilization using HVI (high voltage impulse) was suggested and verified experimentally. Sludge solubilization was carried out for 90 minutes using HVI discharge with peak voltage of 16 kV and pulse duration for 40 microsecond. About 3∼9 % of MLSS and MLVSS concentration were reduced, but the soluble COD, TN, TP of the sludge increased to 372 %, 56 % and 102 % respectively. It indicates that the flocs and/or cells of the sludge were damaged by HVI. These resulted in flocs-disintegration and cells-lysis, which means the internal matters were bursted out of the flocs as well as the cells. Thus, electrical conductivity in bulk solution was increased. All of the results verified that the HVI could be used as an alternative technique for sludge solubilization processes.

본 연구에서는 하수슬러지 가용화를 위한 불용성전극을 개발하여 전기화학적 특성을 확인 하였다. 이리듐을 주촉매로 사용하여 하수슬러지 가용화에 적합한 촉매를 선정하여 내구성이 우수하고 하수슬러지 전기분해에 적합한 기능성 전극 실험을 진행하였고 다음과 같은 결과를 얻었다. 전극의 코팅 소성온도를 주 촉매인 Ir의 질량감소가 적고, 흡열반응 구간인 300℃부터 500℃까지의 범위로 선정하고 실험을 하였다. 실험결과 350℃에서 촉매의 효율성이 가장 우수하게 나왔다. 각각의 바인더 별(Ta, Sn, W) 실험에서도 350℃에서 가장 큰 촉매효율성이 나타났다. 바인더로 사용한 탄탈럼, 주석, 텅스텐 중 탄탈럼이 다른 금속보다 주 촉매의 특성을 그대로 유지시키며 전극의 효율성을 향상시키는 것을 확인하 였다. 50%IrO2 전극의 경우 1.4 V(vs. Ag/AgCl) 약 29 mA/cm2 의 전류가 발생하여 전극의 효율을 평 가하였다.

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%.

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.

2014년 슬러지 발생량은 10,187ton/day로 2008년 기준 약 7,446ton/day에 비해 발생량이 약 37% 증가하였다. 하수슬러지의 발생량은 매년 증가할 것으로 예상되기 때문에 하수슬러지 발생량을 최소화 시키고 자원화하기 위한 여러 가지 대안 중 혐기성 소화방법과 슬러지 감량화 기술이 대안으로 제시되고 있다. 소화조는 장시간의 체류시간, 설계 값보다 낮은 소화효율 등의 고질적인 문제가 있으므로 슬러지를 효과적으로 처리 하기위해 이용 효율을 극대화하는 방안이 필요하다. 따라서 소화조 투입 전 단계에서 하수슬러지를 가용화하는 전처리를 실시하여 가수분해를 촉진시키고, 소화 효율을 높이는 방법을 이용하고 있다. 전처리 공정은 열적처리, 물리·화학적 처리, 생물학적 처리 등으로 구분되며, 이중 열적전처리 공정은 고온조건이나 저온조건에서 고분자 형태로 존재하는 슬러지를 저분자 형태로 전환시켜 바이오가스의 생산량과 소화효율을 증대시키는데 효과적인 것으로 알려져 있다. 열적전처리 중에서도 저온 열적전처리는 고온 열적전처리에 비해 공정 운전에 들어가는 에너지 소모량이 적고, 바이오가스 생산면에서도 효과적으로 알려져있다. 따라서 본 연구에서는 생슬러지 및 잉여슬러지를 대상으로 60~120 ℃, 30~120분 조건에서 실시한 저온 열적전처리 공정에 의한 물리·화학적 특성 변화를 분석하고, BMP test를 통하여 바이오 가스 생산율을 평가하였다. 용존성 물질로 존재하는 SCODCr, NH4+, PO43-, VFAs 분석결과, 생슬러지 및 잉여슬러지 모두 열적전처리 온도가 상승함에 따라 증가하는 것으로 나타났다. 가용화율은 120 ℃ 120분조건에서 SCODCr의 경우 가용화 전 각각 453mg/L, 1,698mg/L에서 열적전처리 후 최대 5,337mg/L, 8,769mg/L로 증가하였으며, TCODCr 중 SCODCr가 각각 약 12%, 18.6%차지하는 것으로 나타났다. 따라서 저온열적가용화 또한 슬러지의 세포 floc 파괴에 의한 내부 물질의 용출에 기인하여 가수분해 단계를 촉진시켜 소화효율을 향상시킬 수 있다고 판단된다.

하수처리장 운영 시 생성되는 하수슬러지는 하수처리장에서 배출되는 폐기물의 대부분을 차지한다. 발생한 하수슬러지의 처리는 퇴비화, 사료화, 매립, 소각, 에너지화, 재활용, 해양투기 등의 여러 방법으로 이루어졌다. 그러나 2013년 런던 협약 발효에 따라 처리 방법 중 30~40%를 차지하던 해양투기가 금지되었다. 해양투기 다음으로 많이 사용된 방법은 육상매립이나, 육상매립의 경우 부지 확보가 점차 어려워지고 환경규제의 강화로 매립하는 양이 감소되고 있다. 따라서 하수처리장에서 발생하는 슬러지를 최소화 하는 동시에 자원으로 활용할 수 있는 적정 기술의 필요성이 대두되고 있다. 여러 적정 기술 중 혐기성소화는 하수슬러지를 혐기 미생물을 이용하여 메탄을 생성하는 가용화하는 대표적인 방법이다. 혐기소화조 운영에 있어서 하수슬러지를 바로 투입하여 처리하는 경우 낮은 소화 효율을 보이므로 소화조 전단에 전처리 기술을 배치하여 소화 효율을 향상 시킬 수 있다. 이런 전처리 기술에는 효소에 의한 생물학적 처리, 초음파, 오존, 원심분리, 액체전단, 분쇄의 기계적 처리, 산화, 알칼리에 의한 화학적 처리, 열처리가 있다. 그 중 열전처리 공정은 슬러지의 부피 감량과 불필요한 화합물의 분해 뿐만 아니라 슬러지 내의 병원균도 제거 가능한 장점을 가진다. 본 연구를 통해 열전처리 공정의 특성을 확인하였으며 공정 이후 생성된 물질의 특성도 평가하였다. 실험은 회분식 반응기에서 진행 되었으며, 혐기조건을 만든 후 열을 가하여 운전하였다. 실험 조건은 온도, 시간, 슬러지 함량에 따라 설정하였다. 각 조건에 따른 시료를 분석한 결과 건조 중량 1g을 기준으로 휘발성유기물질의 초기 농도가 0.67 g 일 때 최대 0.002 g까지 감소가 확인되었다. 감소한 휘발성 유기물질은 용존 유기물 형태로 변경되었고, COD 0.071 - 0.158 g-C/L 또는 TC 0.04 - 0.085 g-C/L 의 증가가 확인되었다. 이외에 TN은 3 - 22 mg-N/L의 증가가 확인되었고, 질산성 질소 또는 아질산성 질소는 미량 발견되었으며, 암모니아 형태의 N이 0.34 - 10.36 mg-N/L로 존재하는 것이 확인되었다.

The objective of this study was to find optimum pretreatment conditions of ozone and microwave for solubilizationof thickened waste activated sludge (TWAS). Response surface analysis was applied to determine the combination of ozoneconcentration (0.03 to 0.1g O3/g total solid (TS)) and microwave temperature (100~170oC). The temperature significantlyaffected the solubilization degree of sludge (p<0.01). Within the design boundaries, the conditions predicted to maximizethe solubilization degree of 41.6% were determined to be 0.065g O3/g TS and 170oC. On the other hand, the solubilizationdegree with the ozone pretreatment alone was 2.7 to 12.2% at 0.03~0.1g O3/g TS. The results show that the combinationof ozone and microwave pretreatments is effective in solubilization of TWAS.

The purpose of this study was to improve low digestibility in anaerobic digestion facility of the sewage treatment plant. To perform this research, sludge digestion and digestion gas purification facilities in sewage treatment plant was applied. In the result of this study, it was very effective for sludge reduction from the improvement of digestive efficiency. In addition, it was confirmed that high purity CH4 (methane) was produced. This results can be useful as basic data to improve the low digestibility in anaerobic digestion processes.

Diverse studies are being conducted on sewage sludge treatment and recycling methods, but the demand for a lowcost treatment technology is high because the sewage sludge has an 80% or higher water content and a high energy consumption cost. We want to apply the thermal hydrolysis reaction that consumes a small amount of energy. The purpose of this study is to quantify the thermal conductivity of sewage sludge according to reaction temperature for optimal design of thermal hydrolysis reactor. We quantified continuously the thermal conductivity of dewatered sludge according to the reaction temperature. As the reation temperature increased, the dewatered sludge is thermally solubilized under a high temperature and pressure by the thermal hydrolysis reaction. Therefore, the bond water in the sludge cells comes out as free water, which changes the dewatered sludge from a solid phase to slurry of a liquid phase. As a result, the thermal conductivity of the sludge was more than 2.6 times lower than that of the water at 293 K, but at 470 K and above, became 0.708 W/m·K, which is about 4% lower than that of the water.

Sludge minimization from wastewater treatment plant is becoming more important to save disposal costs and to contribute to sustainable development. For the reduction of sludge production, solubilization and dewaterability of sludge are important factors in sludge processing. Ultrasonic treatment has been used to enhance sludge solubility and dewaterability with anaerobic digestion sludge, primary sludge, and activated sludge. At the ultrasonic power of 0.2 kW/L for 1 hour, anaerobic sludge and activated sludge showed higher solubilization efficiency than the primary sludge in terms of COD, proteins, and suspended solids. Ultrasonic treatment decreased sludge dewaterability and sludge settling characteristics up to 720 kJ/L of ultrasonic energy. In conclusion, ultrasonic treatment was effective for sludge solubilization but it deteriorate dewaterability (specific resistance) and settling characteristics (SVI) of sludge at the experimental conditions.