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MBR/NF/RO를 이용한 가축폐수처리와 후탈질/응집가압부상을 이용한 잉여슬러지 및 농축수 처리 기술
나유미(Yu Mee Na),배종복(Jong Bok Bae),문태훈(Tae Hun Moon),황윤영(Yun Young Hwang),이양우(Yang Woo Lee) 大韓環境工學會 2013 대한환경공학회지 Vol.35 No.6
가축분뇨 공공처리시설 및 개별농가에서도 적용이 가능하도록 경제적이고 운영이 비교적 쉽고 간단하며 부지가 적게 소요되는 컴팩트한 처리시설을 개발하기 위하여 안성에 있는 M농가에 실규모의 처리시설(100톤/일)을 설치하고 공공처리시설 방류수 수질기준까지 처리할 수 있도록 운영하였다. 벨트프레스 탈수기를 통해 고액분리된 액상 가축분뇨는 MBR/NF/RO를 통해 처리되고 NF/RO농축수 및 가축분뇨처리 슬러지는 혼합한 뒤 탈질을 거쳐 응집가압부상을 통해 처리된다. MBR/NF/RO처리수와 가압부상조 유출수를 혼합 방류하면 공공처리장 수질기준 BOD 30 mg/L, T-N 60 mg/L, T-P 8 mg/L 이하가 달성된다. 가압부상 농축 슬러지는 벨트프레스 탈수기로 유입되어 고상 가축분뇨와 함께 탈수되어 분리된 고형물의 수분함량은 90%로 톱밥과 혼합되어 퇴비로 활용된다. Full scale livestock wastewater treatment plant (100 t/d) was constructed and operated to develop compact and cost effective treatment process for public plant as well as individual farm. Liquid form of livestock wastewater after belt press filter was treated through MBR/NF/RO. NF/RO brine water was mixed with livestock wastewater sludge and treated using denitrification, coagulation and air flotation process. Mixed effluent of NF/RO and air flotation meet public livestock wastewater treatment standard, BOD, T-N and T-P, 30 mg/L, 60 mg/L, 8 mg/L below, respectively. Condensed sludge of air flotation returned belt press filter. Dewatered cake contained 90% water and could be used fertilizer after mixing sawdust.
박석순(Seok Soon Park),나유미(Yu Mee Na),나은혜(Eun Hye Na) 한국환경영향평가학회 2001 환경영향평가 Vol.10 No.2
This paper presents the policy directions of total maximum daily loads(TMDL), which was recently adopted in Korea, for scientific management of water quality. The basic principles of water quality management are also discussed in this paper, along with the TMDL policy in United States as well as the previous policy in Korea. We discussed several unreasonable points out of the previous approaches, such as regulation of all point sources with equal standards, negligence of an assimilative capacity of the receiving water, and emphasis only on drinking water supply, etc.. For successful applications of the TMDL policy in Korea, the following directions are suggested: 1) the unit drainage basin for each TMDL application should be given, 2) the water body where the water quality standards should be maintained, needs to be guided, 3) the water quality parameters of TMDL should be given, 4) the technical guidances should be given for applications of water quality models, and 5) the seasonal TMDL would be allowed. In order to maximize the benefits of the TMDL policy, the local governments would need to implement the following strategies: 1) the increment of an assimilative capacity of the receiving water, 2) the effective controls of the non-point source pollution, 3) the advanced treatment of the point sources, 4) application of system optimization techniques along with effluent trade, and 5) utilization of watershed management systems.