• Journal of the Korean Society of Marine Environment & Safety
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• v.13 no.4
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• pp.27-35
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• 2007

In order to take measures for solving conflicts between the relevant Ministries of Korean government such as MOMAF(Ministry of Maritime Affairs and Fisheries) and MAF(Ministry of Agriculture and Forestry) and the relevant industry circles such as KSA(Korea Swine Association) and KODA(Korea Ocean Dumping Association) regarding the prohibition of ocean dumping of livestock excreta wastes from land, the present conditions of marine disposal of livestock excreta wastes and the standpoints of MOMAF, MAF, KSA and KODA were reviewed in Korea. As measures for solving the conflicts, the followings were proposed; A prior examination into the possibility of the treatment and/or disposal on shore for the total amount of livestock excreta wastes in Korea, measures for solving civil appeals against the problems arising from the treatment and/or disposal on shore of livestock excreta wastes, a prior examination into the possibility of the execution of the amendments to the relevant rules and regulations of Korean marine pollution prevention law for the prohibition of ocean dumping of livestock excreta wastes, measures for supporting the relevant industry circles such as KSA and KODA which were expected to suffer from the prohibition of ocean dumping, and an overall review of the national system for ocean dumping of terrestrial wastes in nationwide level.

• Proceedings of KOSOMES biannual meeting
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• 2007.11a
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• pp.197-205
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• 2007

In order to take measures for solving conflicts between Korean government such as MOMAF(Ministry of Maritime Affairs and Fisheries) and MAF(Ministry of Agriculture and Forestry) and the relevant industry circles such as KSA(Korea Swine Association) and KODA(Korea Ocean Dumping Association) regarding the prohibition of marine disposal of livestock. excreta wastes from land, the present conditions of marine disposal of livestock excreta wastes and the standpoints of MOMAF, MAF, KSA and KODA were reviewed in Korea.

• Magazine of the Korean Society of Agricultural Engineers
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• v.38 no.5
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• pp.106-115
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• 1996

This study was carried out to provide fundamental data for reuse of resources and prevention of environmental pollution Actual states of environmental pollution by biological production facilities were investigated. Various pollution loads and quantity of wastes from greenhouse and animal housings estimated. In greenhouse contents of investigation were wastes of plastic cover, noise of heater and fan, air pollutant of heater, and wastes of soilless culture system, etc. In animal housings, those were actual state of livestock waste treatment and reuse, pollutant mass unit discharge, noise pollution, and malodorant, etc. The main pollutants discharged from greenhouses were wastes of plastic cover, rockwool, and waste fluid of nutrient solution. Developments of waste disposal methods for plastic cover and rockwool are required. And recycle technique of nutrient solution for soilless culture should be developed and propagated. With the buildup of legal control, pollutant mass discharged from livestock wastes are, on the decrease. The other side, reuse of livestock excreta increased. Most animal housings are located near the dwelling house. Malodorant and noise from animal housings have bad effects on the rural living conditions. So developments of integrated complex for small scale livestock farms are required.

• Korean Journal of Environmental Agriculture
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• v.19 no.2
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• pp.171-176
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• 2000

A wastewater treatment pond system was developed for treatment and recycling of dairy cattle excreta of $5\;m^1$ per day. The wastes were diluted by the water used for clearing stalls. The system was composed of three ponds in series. A submerged gas collector for the recovery of methane was installed at the bottom of secondary pond with water depth of 2.4m. This paper deals mainly with performance of methane fermentation of secondary pond which is faclutative one. The average $BOD_5$, SS, TN, and TP concentrations of influent into secondary pond were 49.1, 53.4, 48.6, and 5.3 mg/l, and those of effluent from it were 27.9, 45.7, 30.8, 3.2 mg/l respectively. Methane fermentation of 2.4-meter-deep secondary pond bottom was well established at $16^{\circ}C$ and gas garnered from the collector at that temperature was 80% methane. Literature on methane fermentation of wastewater treatment ponds shows that methane bacteria grow well around $24^{\circ}C$, the rate of daily accumulation and decomposition of sludge is approximately equal at $19^{\circ}C$, and activities of methanogenic bacteria are ceased below $14^{\circ}C$. The good methane fermentation of the pond bottom around $16^{\circ}C$, about $3^{\circ}C$ lower than $19^{\circ}C$, results from temperature stability, anaerobic condition, and neutral pH of the bottom sludge layer. It is recommended that the depth of pond water could be 2.4m. Gas from the collector during active methane fermentation was almost 83% methane, less than 17% nitrogen. Carbon dioxide was less than 1% of the gas, which indicates that carbon dioxide produced in bottom sludges was dissolved in the overlaying water column. Thus a purified methane can be collected and used as energy source. Sludge accumulation on the pond bottom for a nine month period was 1.3cm and annual sludge depth can be estimated to be 1.7cm. Design of additional pond depth of 0.3m can lead to 15 - 20 year sludge removal.