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        검색결과 109

        101.
        2000.06 KCI 등재 서비스 종료(열람 제한)
        본 연구는 제주도에 있어서 인산 시비량 차이(0, 5, 15, 25, 35 kg/10a)에 따른 차풀의 생육반응, 수량성 및 사료가치를 검토하고, 적정 인산 시비량을 구명하기 위하여 1998년 3월부터1998년 9월까지 시험하였다. 개화기까지의 일수는 인산 시비량이 증가됨에 따라 점차적으로 지연되었다 초장, 본당 분지수 및 엽수, 경직경, 엽록소 측정치 등은 인산 시비량이 증가됨에 따라 점차적으로 증가하였으나, 본당 고엽수는 적어지는 경향이었다. 생초수량은 무인산구에서 3,291kg/10a이었으나 인산 시비량이 많아짐에 따라 점차적으로 증가되어 25kg/10a과 35kg/10a 시비구에서는 각각 10a당 5,200 kg과 5,230kg이었으나, 두처리간에는 유의성이 없었다. 건초, 조단백질 및 TDN수량도 생초수량의 변화와 비슷한 경향이었다. 조단백질, 조지방, 가용성무질소물, TDN 함량은 인산 시비량이 증가됨에 따라 많아지는 경향이었으나, 조회분과 조섬유 함량은 낮아졌다.
        103.
        1999.06 KCI 등재 서비스 종료(열람 제한)
        초기배아의 발생과정동안 배아와 모체에서 발현되는 여러 cytokine은 착상을 위한 신호물질로 중요한 역할을 한다. 그 중 interleukin-1 (IL-1)는 배아와 모체간의 상호 신호전달체로서 성공적인 착상을 위한 필수적인 요소로 작용한다고 알려져 있다. 따라서 본 연구에서는 초기배아의 발생과정에 있어서 IL-1 유전자의 역할을 규명하기 위해 생쥐 초기배아에서의 IL-l 유전자의 발현양상을 역전사중합효소연쇄반응을 통해 조사하였고, IL-l 유전자의
        104.
        1997.10 KCI 등재 서비스 종료(열람 제한)
        To predict diffusion and movement of air pollutants in coastal urban region a numerical simulation shoud be consider atmospheric flow field with land-sea breeze, mountain-valley wind and urban effects. In this study we used Lagrangian particle dispersion method in the atmospheric flow field of Pusan coastal region to depict diffusion and movement of the pollutants emited from particular sources and employed two grid system, one for large scale calculating region with the coarse mesh grid (CMG) and the other for the small region with the fine mesh grid (FMG). It was found that the dispersion pattern of the pollutants followed local circulation system in coastal urban area and while air pollutants exhausted from Sasang moved into Baekyang and Jang moutain, air pollutants from Janglim moved into Hwameong-dong region.
        105.
        1996.06 KCI 등재 서비스 종료(열람 제한)
        In genneral, Businger expression is used for determining a turbulance diffusion coefficient. In this study, it is applied to the surface elements of cities such as Asphalt, Ground, Grass, Pond. We set up 5 m-height bar and measured the dry temperature and wet temperature at the height of 0.13, 0.27, 0.5, 1.0, 3.0, 5.0 m. In addition we measured the wind gradient and wind velocity at the height 3 m, solar radiation continuously for 48 hours on the surface. Compared the measured data to Businger expression, the result showed that Businger expression can be well applied to the complex surface of the city.
        106.
        1995.06 KCI 등재 서비스 종료(열람 제한)
        To predict reasonably the movement and the concentration of the pollutants in the coastal area. A simulation model should be prepared considering detail topography with land-sea and the urban effects, and the resolution near the source. The explicit method can not be applied due to the unstability of the numerical calculation in high horizontal-grid resolution, while the ADI scheme satisfied with the high horizontal grid resolution and can be used in the fine mesh system which shows the detail topography, atmospheric flow The ADI method which studied the high horizontal grid resolution was excellent. The two dimentional model used in the study using ADI method is proved as a reasonable model to predict the wind field in any small scale area including mountainous coastal urban area.
        109.
        1994.03 KCI 등재 서비스 종료(열람 제한)
        Dispersion characteristics of air pollutants in the mountainous coastal area are investigated in considering with the mesoscale local circulations using a two dimensional numerical model with two kinds of topograpy of 500m and 300m. In the model, land-sea breezes and mountain-valley wind are mainly considered under the condition of the absence of large scale prevailing flow in the circulation analysis, and the pollutants dispersion is traced by the Lagrangian methods. According to the results, the wind velocity is affected by topography and is stronger in the case of 500m height mountain than that of 300m, the pollutants that source is near the coast transported over the mountain and dispersed to behind inland area. It is classified that the topography change control affects the wind velocity and the circulations. The pollutants that source is different transported and concentrated to behind inland and/or diffused to the sea area by the combination of the wind system with topographic changes. The results can be applied to the air pollution control with the arrangement design of industrial area and the planning of coastal developments.
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