• 한국환경농학회지
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• 제28권1호
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• pp.38-46
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• 2009

Livestock manure is an important source of nutrients for crop production. However, farmers typically do not know the exact nutrient values for livestock manure. In many instances, manure has been viewed as a waste, and as a result it is applied close to the source resulting in over application of nutrients. Thus, the goal of nutrient application has often been applied to reduce the application expense rather than to maximize crop income. This results in wasted money and potentially negative impacts on water quality. Several livestock manure management scenarios were created based on agronomic nutrient requirements using the Utilization of Animal Manure as a Plant Nutrient (AMANURE) software to investigate water quality impacts with the National Agricultural Pesticide Risk Analysis (NAPRA) WWW modeling system. Application of manure at agronomic rates can result in high nitrate-nitrogen losses for some soil types, especially when applied in late fall. The application of manure at an agronomic rate does not necessarily equate to adequate water quality protection, and farmers must take care applying manure at agronomic rates, because nitrate-nitrogen loss potential varies spatially and temporarily. Nutrient loss probability maps for Indiana at 5%, 10%, 25%, and 50% values were created to demonstrate potential water quality impacts when livestock manure is applied to cropland at agronomic rates. The NAPRA WWW system coupled with AMANURE can be used to identify site-specific livestock manure management plans that are environmentally sound and agronomically appropriate.

• 한국농공학회:학술대회논문집
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• 한국농공학회 1999년도 Proceedings of the 1999 Annual Conference The Korean Society of Agricutural Engineers
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• pp.651-656
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• 1999

This study was carried out to investigate the paddy soil and water quality in Boryung freshwater reservoir watershed during the non-cropping season. Soil pH of the Boryung freshwater reservoir watershed were 5.39∼5.78. Total-N and P contents were high by the accumulation of chemical fertilizer partly. Heavy metal content of paddy soils were natural background level. Water pH of the Boryung freshwater reservoir watershed ranged from 6.82 to 8.64. Total-N content affected by a livestock wastes and sewage water were the higher than that of others and total-P content showed below 0.1mg/L. Nitrate nitrogen contents was very high according to the influence a livestock waste and sewage water partly. Heavy metal contents of wateers were natural background level.

• 한국환경농학회지
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• 제15권4호
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• pp.506-519
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• 1996

The water quality in the rural areas is degrading due to a variety of causes such as the increase of the urban sewage and industrial wastes, the disposal of solid wastes, the growth of livestock waste, the growth of leisure facilities, the establishment of agricultural industry estates and etc. The water pollutants are scarce while the effluent is increasing from wide scattered sources. The technology specifically designed for the rural wastes water treatment plant needs to be implemented with improvement of agricultural water quality. 1. An integrated management measures against water pollution sources. The prevention of water pollution is the best measures in the environmental pollution. Hence, the most effective measures needs to be against the sources. Small-scale water treatment plants needs to be constructed in each village in the rural areas. As for the industrial effluent, the effluent discharge needs to be strictly monitored. Government subsidy for the establishment of treatment plant for livestock wastes is necessary. 2. The establishment of national-wide network for agricultural water quality. The network for agricultural water quality have been operated to conserve the agricultural water quality, and to develop management policies by the assessment of water pollution in the rural areas. The results of agricultural water quality network indicates that the water quality is degrading not only around urban areas but also in the distant rural areas, and the water quality at the pumping stations and weirs is worse than that of reservoirs. 3. The legal, systematic, and technical approaches for the agricultural water quality management. The actions currently implemented for the improvement of agricultural water quality involve temporary measures such as the improvement of irrigation facilities. These contingency measures are not effective in the long-term, and sometimes bring secondary pollution. Therefore, integrated measures covering the whole water environment such as the flow, quality, river morphology, aquatic ecosystem, and the surrounding environment, need be invented and implemented. Besides, the legal, systematic, and technical frameworks for the management are not fully established so far. The technology for the treatment of rural water pollution should be refined afterwards, and the research for the development of rural waste water treatment plant should be carried out.

• 유기물자원화
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• 제7권1호
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• pp.43-52
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• 1999

본 연구는 축산분뇨 퇴비화시 부자재인 톱밥을 석탄회로 대체하기 위하여 수행하였다. 축산분뇨와 톱밥의 혼합비율을 부피비 1:1로 고정하고 이때 톱밥을 어느 정도 석탄회로 대체 가능한지를 조사하였다. 각 혼합비율에 대해 조사된 톱밥과 석탄회의 혼합비율은 부피비로 40:10, 35:15, 30:20, 25:25, 20:30, 15:35, 10:40이었다. 축사에서 스크레퍼 방식과 슬러리 방식에 의하여 배출되는 축산분뇨, 톱밥과 석탄회를 앞에서와 같은 혼합비율로 섞은 부자재를 부피비 1:1로 혼합하여 퇴비화하면서 온도, 수분, pH, 유기물, 질소 및 유기물/질소 비 등을 조사하여 다음과 같은 결과를 얻었다. 온도의 변화는 슬러리 방식보다 스크레파 방식에서 톱밥비율이 높을수록 빨리 최고온도($63.5^{\circ}C$)에 도달하였다. 수분 함량의 변화는 스크레파 방식 및 슬러리 방식 공히 톱밥과 석탄회를 부피비로 동일비율(1:1) 혼합하였을 때 42 %와 54 % 범위의 수분함량으로 발효에 비교적 좋은 조건을 유지하였다. pH는 분뇨, 톱밥, 석탄회 비율 50 : 25 : 25 투입시 전체적으로 pH 7~10으로 약알카리성 내지 알카리성이었다. 유기물함량은 톱밥 혼입량이 석탄회보다 많을수록 증가되나 퇴비화가 진행됨에 따라 별다른 변화는 보이지 않았다. 질소함량은 톱밥 혼입량 증가에 따라 늘어났으나, 발효과정 진행에 따라서는 일정한 경향을 나타내지 않았다. 유기물/질소 비는 톱밥 혼입량이 증가할수록 증가하였지만, 발효과정 중 큰 변화는 볼 수 없었다.

• 한국환경보건학회지
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• 제15권2호
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• pp.51-58
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• 1989

In order to estimate unit loading factors of N, and P for controlling eutrophication of Youngsan lake. This study was performed in 4 kinds of pollutant sources from domestic sewage, industrial waste water, livestock stall waste water and drainage of agricultural area during the period from april to october 1988. These results were as follows: 1. The sewage flow for domestic waste water was 191.2 l/capita, day and that of the gray and toilet waste water among the domestic waste water were shown 152.9 l/capita, day(80%) and 38.3 l/capita, day(20%), respectively. 2. The unit loading factor total nitrogen(T-N) for domestic waste water was 7.582g/capita, day, and that of the gray and toilet waste water among the domestic waste water were 1.826g/ capita, day(24.1%) and 5.756g/capita, day(75.9%), respectively. The other hand, the unit loading factors of total phosphorus(T-P) for domestic waste water was 0.925g/capita, day, and that of gray and toilet waste water among the domestic waste water were 0.470g/capita, day(50.8%) and 0.455g/capita, day(49.2%), respectively. 3. In offering Price per million won, the T-P loading factor for drinking manufacture, confectionery manufacture, beer-manufacture and fibre manufacture in the industrial pollutant sources estimate to be 0.350g/day, 0.099g/day, 32.351g/day and 1.536g/day, while T-N loading factor about them in the industrial pollutant sources estimate to be 4.117g/day, 2.414g/day, 106.726g/day and 60.504g/day, respectively. 4. The T-P loading factor according to wash-water of milch cow and pig were 6.735g/day and 18.526g/day, in case of T-N they were 42.397g/day and 27.226g/day, respectively. 5. The T-P loading factor for pollutants drainage in the Paddy fields, fields and forests area were 0.082g/are, day, 0.014g/are, day and 0.002g/are, day, and the T-N loading factor were 0.309g/are, day, 0.158g/are, day and 0.064g/are, day, respectively. The diffrent of the loading factor for pollutants discharges in the agricultural area were resulted from the rainful intensity, the rainful, the amount of fertilization manure, and etc.

• 한국물환경학회지
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• 제22권4호
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• pp.711-719
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• 2006

The effluent from anaerobic digestion process of slurry-type piggery waste has a characteristic of very low C/N ratio. Because of high nitrogen content, it is necessary to evaluate nitrogen removal alternative rather than conventional nitrification-denitrification scheme. In this study, two parallel treatment schemes of SBR-like partial nitritation reactor coupled with anaerobic ammonium oxidation (ANAMMOX) reactor, and a nitritation reactor followed by nitrite denitrification process were evaluated with a slurry-type piggery waste. The feed to reactors adjusted with various $NH_4-N$ and organics concentration. The nitrite accumulation was successfully accomplished at the loading rate of about $1.0kgNH_4-N/m^3-day$. The $NO_2-N/NH_4-N$ ratio 1~2.6 in nitritated effluent that operated at HRT of 1 day indicated that SBR-like partial nitritation was applicable to ANAMMOX operation. Meanwhile, the nitrite accumulation of 87% was achieved at SBR operated with HRT of 3 days and $0.4mgO_2/L$ for denitritation. Experimental results further suggested that HRT (SRT) and free ammonia(FA) rather than DO are an effective control parameter for nitrite accumulation in piggery waste.

• 한국토양비료학회지
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• 제20권2호
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• pp.123-129
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• 1987

수도(水稻)의 축산폐수(畜産廢水) 피해(被害)에 대한 물관리(管理) 및 개량제(改良劑) 시용효과(施用效果)를 구명(究明)하기 위하여 사양토(砂壤土)에서 2년간(年間) pot 시험(試驗)한 결과(結果)는 다음과 같다. <시험(試驗) 1> 물관리(管理) 및 개량제(改良劑) 시용효과(施用效果)(1985) 1. 수도수량(水稻收量)은 상시담수구(常時湛水區)가 간단관수구(間斷灌水區) 보다 많다고 개량제(改良劑) 시용(施用)으로 증수(增收)되는 경향(傾向)이였으며 개량제중(改良劑中) Zeolite와 규회석(硅灰石)이 효과(效果)가 좋았음. 2. 고중(藁重) 및 식물체중(植物體中) 질소함량(窒素含量)은 시용질소(施用窒素) 및 폐수관개량(廢水灌漑量)이 많을수록 증가(增加)하였으나 개량제(改良劑) 시용(施用)으로 감소(減少) 하였음. <시험(試驗) 2> 규회석(硅灰石) 시용효과(施用效果)(1986) 3. 수도수량(水稻收量)은 규회석(硅灰石) 시용량(施用量)이 증가(增加)할수록 증수(增收)되었으며 규회석시용(硅灰石施用)에 의(依)한 증수원인(增收原因)은 등숙율(登熟率) 및 수당입수(穗當粒數)의 증가(增加)에 있었고 질소시용량(窒素施用量)이 3g/pot (관행(慣行))구(區)에서는 규회석(硅灰石) 60g/pot 시용(施用)이 적량(適量)으로 생각되었다. 4. 불임수수(不稔穗數)는 시용질소(施用窒素) 및 폐수중(廢水中) 질소농도(窒素濃度)가 증가(增加)됨에 따라 증가(增加)하는 경향(傾向)이었으며 규회석시용(硅灰石施用)으로 크게 감소(減少)되었다.

• Asian-Australasian Journal of Animal Sciences
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• 제12권4호
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• pp.651-656
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• 1999

In current animal production in Japan, a large surplus of nitrogen and phosphorus is given to animals as their feed which are mostly imported from outside of our own country. Today, an excess of nitrogen and phosphorus from animal manure has been spread out of the area of animal production and the surroundings. These components have become the major reason for eutrophication of ground, surface and inland water. Nutritional studies for the reduction of nitrogen and phosphorus from animal waste has been done by many researchers. The reduction of excess protein in animal feed and the supplementation of deficient essential amino acids to feed have a possibility to increase the biological value of feed and to reduce nitrogen excretion, especially, via urine. The use of phytase activity to degrade phytate and to release utilizable inorganic phosphorus make it possible to cut an excess supply of feed additive inorganic phosphorus and to reduce phosphorus excretion from animal waste.

• 한국지하수토양환경학회지:지하수토양환경
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• 제8권1호
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• pp.57-67
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• 2003

지하수 의존도가 큰 농촌지역에서 주로 사용하는 천부지하수는 오염에 민감하므로, 인간활동에 의한 질산성 질소 오염이 생활용수 공급에 큰 문제가 되고 있다. 농경활동과 함께 다양한 규모의 축사가 운영되고 있는 경기도 일죽지역 천부지하수에 대한 질산염 연구결과, 인위적 오염물질 유입이 예상되는 지점이 77%, 먹는물 수질기준을 초과하는 지점이 32～42%로 나타났다. 질소동위원소 분석 결과, 인위적 오염물질 유입이 예상되는 지점은 모두 $\delta^{15}$N-$NO_3$가 5$\textperthousand$ 이상으로 나타났으며, 59%지점이 동물분뇨에서 유래된 질소의 영향을 강하게 받고 있는 것으로 나타났다. 연구지역 천부지하수의 질산성 질소 주 오염 원인은 밀집된 축사로 밝혀졌으며, 운영이 종료된 축사라도 오랫동안 지하수질에 영향을 미치는 것으로 보인다. 축종에 따라 오염원의 화학적 특성이 다른데, 지표수게는 그 영향이 나타나지만, 지하로 유입되는 동안 반응에 의하여 일부 용질이 제거되므로 지하수에서는 오염원 차이에 의한 영향이 나타나지 않았다.

• 환경위생공학
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• 제6권1호
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• pp.7-25
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• 1991

Until now, pure drinking water grnerally menas the water without taste, odor, general bacteria, coliform, and other exotic substance. Such a definition has been changing recently due to the finding of numerous other inorganic and organic substances unknown to us. 10 years ago, major causes of death were infectious agents and parasites contained in water, but recently, it has become apparent that some substances contained in drinking water cause cancer and heart diseases. We must drink about 2L of water everyday in order to maintain healthy condition. Waters used for drinking include tap water, well water, spring water, filtered water, etc., but the quality of drinking water has more polluted due to the industrial development and population increase. For example, industrial waste waters from industrial plants pollute the water supply sources ; toxic substances contained in the waste waters pollute the ground water sources by penetrating the geological strata, and municipal, livestock, public building waste waters also pollute the water supply sources. Sometimes, the polluted surface waters were announced to be polluted by various kinds of orgainc substance, and it is reported that the pollution of ground water by orga nic substances has few in number but high in its concectration comparing with those of surface water. As the water quality pollution level increases, so the amount of disinfectant also increase. For example, chlorine solution, one of widely used disinfectants, creates trihalomethane(THM), a carcinogen, and halogen compounds. According to Oliver, through chlorine disinfection process, humine substance and chlorine create bolatile organic halide and nonvolatile organic halide by chemical reaction. There are tens or hundreds filtering devices, but filtering principles and maintenance metjhods are different, so their efficiency tests are needed. According to Smith, the effeciency tests aginst over 30 Ameican filtering devices show that 10 devices can remove 85% of volatile organics and further studies on filtered waters are underway. In consideration of important impacts of polluted drinking water on national health, authors studied the state of water quality pollution against tap water used as drinking water, filtration device passed water, ground water, and conserved drinking water ; tested the efficiency of filtration devices for tap water ; tried to sep up the detection method by using ion chromatography based on negative ion and positive ion by using single column, and attemped the simple filtration method for general households.