본 연구는 수입사료가 우리나라 농업환경의 오염부하에 미치는 영향을 파악하고자 2005년을 기준년도로 하여 수입사료 품목별 수입량 및 비료성분량, 수입사료로 인한 가축 사양단계에서 비료성분 발생량을 추산하고, 농경지 작물별 재배면적과 양분요구도 분석을 통해 수입사료로 인한 농경지의 오염부하도를 분석하였다. 수입사료를 통해 국내로 도입되는 비료성분량은 질소 371천톤, 인산 140천톤, 가리 143천톤, 주요 수입품목인 곡류 및 식물성 유박류에서 유래하는

Cooling of nutrient solution is essential to improve the growth environment of crops in hydroponic culture during summer season in Korea. This study was carried out to provide fundamental data for development of the cooling system satisfying the required cooling load of nutrient solution in hydroponic greenhouse. A numerical model for prediction of the cooling load of nutrient solution in hydroponic greenhouse was developed, and the results by the model showed good agreements with those by experiments. Main factors effecting on cooling load were solar radiation and air temperature in weather data, and conductivity of planting board and area ratio of bed to floor in greenhouse parameters. Using the model developed, the design cooling load of nutrient solution in hydroponic greenhouse of 1,000m2(300pyong) was predicted to be 95,000 kJ/hr in Suwon and the vicinity.

For the assesment of pollutant loads, a monitoring has been conducted to identify hydrologic conditions and water quality of the Oenam watershed in Juam Lake, and the SWAT model integrated with GIS was applied to the watershed and evaluated for its applicability through calibration and verification using observed data. For the model application, digital maps were constructed for watershed boundary, land-use, soil series, digital elevation, and topographic input data of the Oenam watershed using Arcview. The observed runoff was 832.8 mm while the simulated runoff was 842.8 mm in 2003. The model results showed that the simulated runoff was in a good agreement with the observed data and indicated reasonable applicability of the model. In terms of nutrient load, the simulation results of T-N, T-P showed a similar trend to observed values. The observed T-N load was 10.8 kg/ha and the simulated T-N load was 7.6 kg/ha while the observed T-P load was 0.21 kg/ha and the simulated T-P load was 0.18 kg/ha. In general, SWAT model predicted observed runoff and loads of T-N and T-P after calibration with observed data in acceptable range. Overall, SWAT model was satisfactory in estimation of nutrient pollutant loads of the rural watershed.