• Title/Summary/Keyword: Sequence Batch Reactor(SBR)

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Advanced Treatment of Shipboard Sewage by SBR Process with BM (BM 미생물제제를 이용한 크루즈선 오·폐수 고도처리)

  • Kim, In-Soo;Chang, Jae-Soo;Lee, Eon-Sung;Koh, Sung-Cheol
    • Journal of Navigation and Port Research
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    • v.36 no.8
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    • pp.643-649
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    • 2012
  • Lab scale experiment study was carried out for biological treatment process development in cruise. SBR(Sequence Batch Reactor) process with BM(Beneficial Microorganisms) was investigated for practical application on shipboard sewage treatment. From the results it was suggested that SBR process with BM might be a suitable process for advanced cruise sewage treatment in terms of decrease in T-N and T-P, maintenance of useful microorganisms and control of sludge bulking. By adding BM to SBR system, about 40% of EPS in sludge was increased, about 74% of total nitrogen was reduced and the total phosphorus reduction averaged 75%.

Estimation of Dominant Bacterial Species in a Bench-Scale Shipboard Sewage Treatment Plant

  • Mansoor, Sana;Ji, Hyeon-Jo;Shin, Dae-Yeol;Jung, Byung-Gil;Choi, Young-Ik
    • Journal of Environmental Science International
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    • v.28 no.10
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    • pp.899-905
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    • 2019
  • Recently, an innovative method for wastewater treatment and nutrient removal was developed by combining the sequence batch reactor and membrane bioreactor to overcome pollution caused by shipboard sewage. This system is a modified form of the activated sludge process and involves repeated cycles of mixing and aeration. In the present study, the bacterial diversity and dominant microbial community in this wastewater treatment system were studied using the MACROGEN next generation sequencing technique. A high diversity of bacteria was observed in anaerobic and aerobic bioreactors, with approximately 486 species. Microbial diversity and the presence of beneficial species are crucial for an effective biological shipboard wastewater treatment system. The Arcobacter genus was dominant in the anaerobic tank, which mainly contained Arcobacter lanthieri (8.24%), followed by Acinetobacter jahnsonii (5.81%). However, the dominant bacterial species in the aerobic bioreactor were Terrimonas lutea (7.24%) and Rubrivivax gelatinosus (4.95%).

Advanced Wastewater Treatment on ship's sewage with new MARPOL73/78 ANNEX IV (MARPOL73/78 ANNEX IV의 개정발효에 따른 선박 오수의 고도처리)

  • Park, Sang-Ho;Lim, Jae-Dong;Park, Sung-Jeng;Kim, In-Soo
    • Proceedings of KOSOMES biannual meeting
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    • 2007.05a
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    • pp.91-96
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    • 2007
  • Lab scale experimental study was carried out for SBR process, to investigate the effects of influent ship sewage organic compound removal and Bacillus sp. state on design parameters. This process was able to remove nitrogen and phosphorus as well as organic matter efficiently. More than 95% of chemical oxygen demand(COD) were removed. In addition, about 97% of total nitrogen (T-N) was reduced. The total phosphorus(T-P) reduction averaged 93%. The performance load of SBR process was shown to be $0.095kg{\cdot}TOC/m^3{\cdot}day$. The pH was decreased from 8.1 to 7.0 within 30 min and increased to 7.3 at the end of anoxic stage, and these phenomena were explained. The sludge produced in the SBR process is characterized by low generation rate (about $0.36kg{\cdot}MLSS/kg{\cdot}TOC$) and excellent settleability. The number of Bacillus sp. in the SBR was 24.2%, indicating that Bacillus sp. was a predominant species in the reactor.

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Treatment Characteristics Using Full-Scale SBR System (Full-Scale SBR 공법을 이용한 처리특성)

  • Choo, Tai-Ho;Lee, Yong-Doo;Cho, Yong-Hyun
    • The Journal of the Korea Contents Association
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    • v.6 no.10
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    • pp.34-40
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    • 2006
  • In this study, the treatment of organic matters and nutrients like Nitrogen and Phosphorus with sequencing batch reactors (SBR) was conducted. The following conclusions can be summarized from the study. The influent BOD concentration was varied 19.6 to 40.0mg/L and the effluent was 3.0 to 14.8mg/L. The variations of BOD removal efficiency during the experimental period was $47.9{\sim}88.4%$ and the average was 80.8%. The average removal efficiency was stabilized with the passage of time. Also the COD concentration was flowed into as $12.2{\sim}32.0mg/L$ and the effluent concentration was varied 3.3 to 18.6 mg/L, and then the average COD removal efficiency was 57.3%(minimun 19.2% and maximum 78.6%). But fortunately, the COD removal efficiency was also stabilized as 70.2% after 79days. In the case of T-N, the influent concentration range was $7.53{\sim}14.99mg/L$ and the effluent concentration was 6.59mg/L(the average removal efficiency was 40.3%) until the first experiment time 79days. But after normalizing the system, it was 4.44mg/L (the average removal efficiency was 56.4%). Also the influent T-P concentration was varied from 0.77 to 1.91mg/L and the effluent concentration was $0.26{\sim}1.53mg/L$. The removal efficiency was varied from 5.3 to 71.7%. considerably, therefore the average removal efficiency was 42.6%. The reason was concluded that the sludge wasn't discharged for increasing MLSS concentration.

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