• Title/Summary/Keyword: BOD vs. COD ratio

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Treatability Study for the Nightsoil and Septic Tank Sludge by Anaerobic Digestion (혐기성(嫌氣性) 소화방식(消化方式)에 의한 분뇨(糞尿)와 정화조(淨化槽)슬러지의 혼합처리(混合處理) 실험(實驗)에 관한 연구(硏究))

  • Lee, Kwang Ho;Shin, Eung Bai;Ham, Kun Yeun
    • KSCE Journal of Civil and Environmental Engineering Research
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    • v.2 no.1
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    • pp.69-80
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    • 1982
  • This study was performed to increase the treatment efficiency of the existing anaerobic digestion facilities of the nightsoil treatment plants. Bench-scale anaerobic digesters were operated to evaluate the effect of the ratio (7:3 and 9:1) of the mixture of nightsoil and septic tank sludge on treatment efficiency. The laboratory experiments have demonstrated that the ratio of the mixture does have an effect on the organic removal efficiency. The nightsoil to septage ratio of 7 to 3 appears to yield a higher efficiency than the ratio of 9 to 1. The percent removals of 7 to 3 ratio are 87 % BOD, 82 % COD, 66 % TS, and 78 %. VS whereas those of 9 to 1 ratio are 80 % BOD, 80 % COD, 63 % TS, and 76 % VS. This study also showed that the mixed treatment of the nightsoil and septic tank sludge will be possible at the nightsoil treatment plant.

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COD Pollutants Load Estimation Schemes in Lake Shihwa and Incheon Coastal Zone (시화호 및 인천연안의 COD 오염부하량 추정기법)

  • Cho Hong-Yeon;Cho Bum-Jun
    • Journal of Korean Society of Coastal and Ocean Engineers
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    • v.18 no.3
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    • pp.262-267
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    • 2006
  • For the concentration management in COD parameters, it requires the measurement and estimation of the COD pollutants load (hereinafter PL) in the watershed. The estimation method of the PL, however, is provided only based on the BOD parameters. The development of COD PL estimation schemes is expected to execute total PL management in coastal zone and needs to more observation and much time. This study provides COD PL estimation schemes using statistical information about ratio analysis with COD & BOD concentration of rivers and drainages of an industrial complex in Lake Shiwha and Incheon Coastal Zone watershed. The COD PL is computed with ease by multiplying the conversion factor, which is calculated as the sum of the average and 1 to 3 (safety factors) times standard deviation. The conversion factor of Lake Shihwa and Incheon Coastal Zone is estimated as 1.7, 2.3 and 2.9 with respect to the safety factor 1, 2, and 3, respectively.

Decomposition Characteristics of Municipal Solid Wastes in Lysimeter Without Leachate Discharge (침출수 무배출식 모형매립조를 이용한 도시폐기물 분해특성)

  • 류돈식;이해승;이찬기
    • Journal of environmental and Sanitary engineering
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    • v.15 no.2
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    • pp.49-57
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    • 2000
  • The objective of this study is to find solid waste decomposition in landfill without leachate discharge. This study was observed variation of landfill gas production rate and leachate for stabilization assessment, and using four sets of lysimeter as experimental apparatus. Soild waste decomposition was accelerated in without leachate discharge system by sufficient moisture for methane bacteria. And gas production rate was between 54.2ℓ/kg VS∼335.9ℓ/kg VS in each lysimeter. Generation time of methane gas was showed different in each lysimeter, but it was much faster than literature research. The time of stabilization phase were began as follows : L-1 400 day, L-2 350 day, L-3 170 day and L-4 70 day respectively. Decreasing times of BOD/COD ratio and C/N ratio were necessary more than literature research because organic matter was not discharge such as wash out.

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Assessment on Environmental Stabilization of Used Open Dumping Landfill - A Case Study of Kamkok Landfill - (사용종료 비위생 매립지의 환경 안정성 평가 - 감곡 매립지 사례 연구 -)

  • Park, Sangchan;Cho, Byeongreal;Jeong, Jihye;Lee, Minhee;Kim, Taeyoung;Park, Jongho
    • Journal of the Korean GEO-environmental Society
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    • v.9 no.6
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    • pp.13-19
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    • 2008
  • The objectives of this paper are to investigate states of these open dumping landfills for managing, utilizing and stabilization of a municipal solid waste landfill site in environmentally secure conditions. The result of the physical analysis of the landfill showed that it is composed of between 29.72-63.84% organic matter, 32.88% vinyl plastic. The environmental assessment of the landfill site confirmed that the landfill is at a maturation phase due to 0.18 of $BOD_5$/CODcr of leachate. VS and FS of TS Was respectively 30.37%, 32.34% and C/N ratio was 21.8. Surface water around landfill was BOD 10.7 mg/g, SS 37.8 mg/g, E-Coli 31,157(MPN/$100m{\ell}$) and Ground water was $COD_{Mn}$ 1.13-1.38 mg/g, $NO_3-N$ 1.025-4.075 mg/g. Leachat indicated T-P 0.002-0.028 mg/g, $NH_3-N$ 4.0-21.0 mg/g. The soil contamination of around landfill didn't appear as below of the regulation of Soil Environment Conservation Act. The Landfill Gas was $CH_4$ 13.25%, $CO_2$ 6.17%, H2S and CO was not detected. Also Surface Water was not detected $CO_2$, $CH_4$, $H_2S$, CO.

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