본 연구는 감자 플러그묘를 생산하기 위하여 시작품으로 제작된 폐쇄형 묘생산 시스템내의 전기에너지 소모를 분석하고, 에너지 수지를 구명하고자 수행되었다. 기온 20℃, 상대습도 90%, 광주기 16/8 h, PPF 50 μmol·m-2·s-l의 조건 하에서 5일 동안 발근과정을 거친 감자 경삽묘는 상대습도와 PPF를 각각 70%, 200 μmol·m-2·s-l로 조절한 가운데 15일간 육묘되었다. 폐쇄형 묘생산 시스템내의 전기에너지 소비는 인공광원 46%, 컴프레서 35%, 가열기 16%, 송풍기 2%, 가습기 1% 로 나타났다. 전기에너지 이용효율과 단피복사 에너지 이용효율은 각각 0.005과 0.054 로 나타났다. 향후 폐쇄형 시스템에서의 전기에너지 소모량을 절감시키면서 에너지 이용효율을 증대시키는 빙안이 모색된다면 감자 플러그묘 생산을 위한 폐쇄형 시스템의 실용성은 더욱 높아질 것이다.

The present study was carried out to investigate effect of FSH -P dose and energy level on normal embryo production after superovulation in Hanwoo. The results obtained were as follows ; 1. There was a significant effect of dose of FSH-P on normal embryo production in Hanwoo(P5.9), 40(4.9i5.7), 50mg(2.22.6). 2. The plasma P levels on the first treatment day were higher group( >4ng /ml) than lower group( <=4ng /ml), produced significicantly(P<0.05) higher number of normal embryos. 3. There was a significant effect of energy level on normal embryo production in Hanwoo(P6.0), number of normal embryos were higher than TDN 70%(5.16.5) and TDN 130%(4.42.6) 4. The donor returned to normal estrus after superovulation were 44.8, 28.4 and 29.9 days by TDN 70, 100 and 130%, respectively.

This experiment was conducted to find out the effects of the different cutting height on the chemical composition, energy production and relation of yields of Italian ryegrass, tall fescue and perennial ryegrass swards. It was carried out on the experimen

본 실험은 가을에 파종하여 월동전 예취 높이를 달리 하였을 때 공식초종의 탄수화물함량변화, 월동성 및 다음해 봄철 수랑에 미치는 영향을 구명하기 위해 초종(Italian ryegrass, tall fescue, perennial ryegrass)을 주구로 하고 월동전 예취 높이 (무예취, 6cm, 15cm)를 세구로 하여 분활구배치 3반복으로 설계하여 수행한 결과는 다음과 같다. 1. 초종별 예취 높이에 따른 목장내 온도변화는 tall fescue >

Anaerobic mesophilic batch tests of food waste and food waste leachate collected from food waste treatment facility were carried out to evaluate their ultimate biodegradability and two distinctive decay rate coefficients (k1 and k2) with their corresponding degradable substrate fractions (S1 and S2), respectively. Each 3 liter batch reactor was operated for more than 60 days at substrate to inoculum ratio (S/I) of 0.5 as an initial total volatile solids (TVS) mass basis. Result of Ultimate biodegradability of 74 ~ 83% for food waste and 85 ~ 90% for food waste leachate were obtained respectively. The readily biodegradable fraction of 85 ~ 93% (S1) of food waste Biodegradable Volatile Solids (BVS, So) degraded within the initial 15 days with a range of of 0.151 ~ 0.168 day−1, whereas the rest slowly biodegradable fraction (S2) of BVS degraded for more than 53 days with the long term batch decay rate coefficients of 0.009 ~ 0.010 day−1. For the food waste leachate, the readily biodegradable portion (S1) appeared to be 92 ~ 94% of BVS (So), which degrades with of 0.172 ~ 0.206 day−1 for an initial 15 days. Its corresponding long term batch decay rate coefficients were 0.005 ~ 0.009 day−1. It is recommended that the hydraulic retention times of mesophilic anaerobic digesters be 16 days for the food waste and 15 days for the food waste leachate, respectively. However a safety factor should be considered when designing a full scale plant.

To predict annual energy production (AEP) accurately in the wind farm where located in Seongsan, Jeju Island, Equivalent wind speed (EQ) which can consider vertical wind shear well than Hub height wind speed (HB) is calculated. AEP is produced by CFD model WindSim from National wind resource map. EQ shows a tendency to be underestimated about 2.7% (0.21 m/s) than HB. The difference becomes to be large at nighttime when wind shear is large. EQ can be also affected by atmospheric stability so that is classified by wind shear exponent (). AEP is increased by 11% when atmosphere becomes to be stabilized ( > 0.2) than it is convective ( < 0.1). However, it is found that extreme wind shear ( > 0.3) is hazardous for power generation. This results represent that AEP calculated by EQ can provide improved accuracy to short-term wind power forecast and wind resource assessment.

Results of reviews on bio-gas production and policy trends in the European Union (EU) are as follows. In the EU,Germany leads in bio-gas production with 29 TWh of energy produced through energy crops as of 2013. This could beachieved through renewable energy laws and increases in feed in tariff (FIT) schemes in Germany. In the EU, bio-gashas been verified to play an important role and contribute to greenhouse gas reduction. However, it is necessary to providea measure to improve sustainability criteria and decrease the consumer's share of expenses. If bio-gas is produced usingorganic wastes instead of energy crops, this problem can be solved. If the bio-gas production policies in the EU are appliedin South Korea, bio-gas market will be promoted and greenhouse gas emission can be reduced in the future.

Livestock Wastewater shall cause a high concentration of organic matter and nutrients such as rivers because of the lake and groundwater contamination, such as the accumulation of nutrients in the soil contained in the manure, livestock wastewater containing large amounts of organic matter that will flow to the river or appeal If eutrophication, and comfortable living environment to cause harm, such as odor and pest damage and can. Organic waste and organic waste, such as the world has a direct interest in acquiring the available resources and the development of clean energy from waste is a growing desire, is expected to contribute to the environment from waste materials industry growth by developing innovative technologies such as direct electrical energy production. In the case of livestock waste water and high concentration of organic material in addition to containing ammonia nitrogen, nitrate nitrogen for nitrification is created due to the electron acceptor is used as the fuel cell according to this has been reported to decrease the efficiency of electricity production. Therefore, to derive the electricity production efficiency due to organic concentration and ammonia nitrogen concentration in order to apply a microbial fuel cell (MFC) livestock wastewater treatment process in this study, and to derive the energy production potential with livestock waste water through the study. Lab. scale Reactor fabrication and operation to try to derive the reaction factor of the optimum operating conditions in accordance with the livestock wastewater applied through the evaluation of trends and removal efficiency of organic matter and nutrients in the microbial fuel cell. In addition, from the final research results, I try to present the direction of future research for the improvement of application possibilities and microbial fuel cell power generation efficiency of microbial fuel cell in the livestock wastewater treatment facilities.

Slaughter of cattle, pigs, and chickens has increased continuously. In particular, slaughter of chickens has been grown up about 150% in 2010 than that in 2003, that is approximately 120,000 tons. All of them are underwent consigned treatment even though those can be used as a resource and an energy source. With this regards, THR (Thermal Hydrolysis Reaction) leads to reduce water content drastically (<30% in sludge cakes). In addition, Dehydrated solid would be re-used as solid fuels (SRF) as well. In this study, We have applied THR to a plant (10 ton/day) on the basis of our lab and pilot results. Water content of sludge cakes showed with a ranges of 30 to 40% after solid-liquid separation. Dairy SRF produced 1.5 ton/day and its heat capacity for SRF has 6,500 kcal/kg. This gave the steam produced about 12 ton/day throughout the plant operation, suggesting that THR system would expect energy savings.

This paper examined energy consumption distribution by process and energy production-effect of MBT facilities inKorea. Generally, facilities that use fossil fuels for drying consumed energy about 70~80% in drying and exhaust gasestreatment process and energy distribution was heavily affected a position of drying and a kind of fuel. Energy production-effect by the ratio of input-energy to output-energy ranged from 4.54 to 9.60, however, if generation efficiency is reflected,it was standardized to low levels from 3.10~3.77. So we were able to confirm that the superiority of energy production-effect between facilities is not considerable.

This research was performed to simulate shellfish production systems and sales in Gamak Bay, South Korea. To study the way the shellfish system generates maxima, a numerical model was developed to simulate the model under a control and a number of different scenarios. The program calculates the EMERGY flows by multiplying the flows of energy and materials by the appropriate solar transformity. In this study, an energy systems model was built to simulate the variation of sustainability for oyster aquaculture. The results of the simulation based on 2005 data that as oyster production yield slightly increases, money and assets increase to a steady state. When the program is run control simulation, the system reaches carrying capacity after 8 years. The simulation of models with price of purchased inputs increased with 3.5% inflation rate per year showed maximum benefit of shellfish production occurs after 6 years but amounts are less than control simulation, and then decreases slightly in money and yield results. The results with 3.5% inflation and increase of oyster price annually showed steady and slightly increase of money and yield.