Development of Biological Filtration Process for Effective Nitrogen Removal in Tertiary Treatment of Sewage

생물막 여과반응기를 이용한 고도질소 제거법의 개발

  • Jeong, Jin-Woo (Department of Water Supply & Sewerage Policy, Environmental Management Corporation) ;
  • Kim, Sung-Won (Department of Civil&Environmental Engineering, Korea University) ;
  • Tsuno, Hiroshi (Department of Urban and Environmental Engineering, Kyoto University)
  • 정진우 (환경관리공단 상하수도지원처) ;
  • 김성원 (고려대학교 공과대학 토목환경공학과) ;
  • 津野洋 (교토대학교 대학원 공학연구과 도시환경공학과)
  • Received : 2005.09.12
  • Accepted : 2005.11.24
  • Published : 2006.03.30

Abstract

The treatment performance and operational parameters of a tertiary wastewater treatment process a biological filtration system were investigated. The biological filtration system consisted of a nitrification filter (Fiter 1) and a polishing filter with anoxic and aerobic parts (Filter 2). SS, T-C-BOD, and T-N in effluent were kept stable at less than 3, 5 mg/L, and 5 mgN/L, respectively, under a HRT in Filter (filter-bed) of 0.37~2.3 h. T-N at the outlet of Filter 2 were about 1~5 mgN/L under the condition of LV of 50~202 m/d. In Filter 2, denitrification was accomplished under LV of 50~168 m/d in a 1 m filter-bed. However, the denitrification capacity reached the maximum when the linear velocity was increased to 202 m/d. Relationship between increase in microorganism and headloss was clearer in Filter 2. As a result, the denitrification rate increased from 1.0~2.3 kgN/($m^3-filter-bed{\cdot}d$) as the headloss increased. The COD removal rate was 6.0~9.6 kgCOD/($m^3-filter-bed{\cdot}d$) when operated with Filters 1 and 2. These results mean that captured bacteria contributed a part of COD consumption and denitrification. The maximum nitrification and denitrification rate was 0.5 and 4 kgN/($m^3-filter-bed{\cdot}d$) in Filter 1 and 2.The ratio of backwashing water to the treated water was about 5~10 %. In Filter 1, wasted sludge in backwashing was only 0.7~5.3 gSS/($m^3$-treated water). In Filter 2, added methanol was converted into sludge and its value was 8.0~24 gSS/($m^3$-treated water). These results proved that this process is both convenient to install as tertiary treatment and cost effective to build and operate.

Keywords

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