The emissions characteristics of particulate matters(PM) according to the types of wastes from industrial waste incinerator of 800 kg/hr treatment capacity were investigated. For this study, the incinerate waste are as follows; waste resin, waste wood, waste urethane, waste gunny, and waste paper. The particulate samples were collected to be emitted in stack and air pollution control(both cyclone and bag filter). In stack, the concentrations of PM were in the range of 2.61 to 26.51 ㎎/S㎥ and the major chemical species were C, Si, Cl, K, Na, Ca in all the wastes. In cyclone fly ash, the mean content of heavy metal were in the order of Fe > Zn > Pb > Cu > Mn > Cr > Ni > Cd > As > Hg and the heavy metal content of waste resin were Zn 34,197.5 mg/kg, Fe 27,587.6 mg/kg, Pb 6,055.8 mg/kg, respectively. In bag filter fly ash, the mean content of heavy metal were in the order of Zn > Pb > Fe > Cu > Mn > Cd > Cr > Ni > As > Hg and the heavy metal content of waste wood were Pb 36,405.2 mg/kg, Fe 15,762.9 mg/kg, Cu 9,989.5 mg/kg, Cd 2,230.1 mg/kg, respectively. Comparing the heavy metal content of both cyclone and bag filter, in cyclone, the Cr, Fe, Ni content were higher than in bag filter and the Cd, Cu, Hg content were lower than in bag filter.

한국원자력연구원에 위치한 KURT 지하처분연구시설은 2003년 부지조사를 시작으로 최근에 완공하였으며, 그 규모는 길이 약 180m, 폭 6m, 그리고 높이 6m의 말굽형 단면을 가진 터널이고 지하 약 90m 깊이에 위치하고 있다. 터널 굴착이 100m 정도 진행되었을 때, 신선한 암석 및 풍하가 진행된 암석, 그리고 균열 및 단층 충전물질로 채워진 부분을 대상으로 시료를 채취하여 광물 및 화학적 분석을 실시하였다. KURT 암반에는 일라이트, 스멕타이트, 녹니석과 같은 층상규산염광물들과 방해석 등이 단층 및 균열을 충전하고 있다. 일라이트나 스멕타이트는 단열대에 주로 혼합광물로 존재하고 있으며, 우세종에 따라 입도에 따른 함량비에 차이가 있다. 산화철로 피복된 암석과 단열충전물 시료에는 우라늄 및 토륨의 함량이 신선한 암석에 비해 높았으며, 이는 암석으로부터 서서히 용탈되거나 지하수 및 열수에 용존되어 있던 핵종 원소들이 단열을 따라 이동하면서 산화철 및 단열충전광물들에 의해 선택적으로 수착되거나 공침된 결과로 해석된다. 본 연구결과는 향후 지하심부 고준위방사성폐기물 처분관련 장기안정성 예측시 핵종 이동 및 지연에 영향을 끼치는 환경 인자 평가에 귀중한 자료로 활용될 것이다.

After examining the difference in the photosynthesis rate of corn according to the planting distance, the distance of 40 × 40 cm showed the lowest rate by 23 days after transplanting (May 31); however, there was no significant difference in the photosynthesis rate due to increased salt tolerance in the plant as time went by. As for the difference in growth features of a plant, the planting distance of 40×40cm showed a growing disorder due to the influence of salt by 23 days after transplantation (May 31); however, there was a desirable growth as time went by. For the difference in the salt content within a plant, the planting distance of 40×40cm tended to be higher than other planting distances, and the K⁺ content is much higher than other kinds of salt after examining the difference in salt absorption. As for the correlation between saline components within a plant, there was a significant negative correlation among K⁺, Ca²⁺, and Na⁺ while there was a significant positive correlation among Mg²⁺, Ca²⁺, and Na⁺. After examining the effectiveness of salt removal from soil according to corn cultivation, the planting distance of 30×30㎝ showed a remarkable decrease by 37 days, compared with 23 days, after transplantation in K⁺ by 28%, Ca²⁺ by 36.6 %, Mg²⁺ by 30.6 %, and Na⁺ by 22.9 %. And the salt content is higher in surface soil than in subsoil.

하수시설 콘크리트의 열화현상은 하수시설의 특수한 환경조건상 황산화세균 등의 서식에 의해 발생된 황화수소(H2S)에 기인하는 생화학적 부식이 대표적인 것으로 알려져 있으나, 국내의 경우 근본적으로 방지대책이 전혀 고려되지 않은 채 정비사업이 수행되고 있어 근본적으로 황산화세균을 억제할 수 있는 보수재료․공법의 개발이 시급히 필요한 실정이다. 이에 본 연구에서는 항균금속을 포함한 도포형 항균제를 개발한 후, 개발된 항균제의 황산화세균에 대한 항균성능과 항균제를 도포한 단면복구재의 부착강도, 흡수 및 투기저항성, 중성화 깊이, 염화물이온 침투깊이 및 화학저항성 등의 기초물성을 평가하였다.

In this study, thirteen villages in Chonnam province were selected as case study sites and the spatial distribution of the facilities in the villages was examined to provide basic information fur the establishment of rural plans. According to the questionnaire survey, various problem such as environmental pollution, position, scene, management etc. was brought owing to cattle shed, and dissension was more or less seen by scale of facilities, management of facilities and waste, regional factor(stock farming management condition, life style and attitude of inhabitants) and topographical factor (height, position physical aspect of a mountain, distance with water resources etc.) etc.. The facilities could be classified into 6 types based on the their spatial locations: 1) Type 1, facilities located at the waterside; 2) Type 2, facilities located at the entrance of village; 3) Type 3 facilities, scattered in the residential area: 4) Type 4 facilities, collectivized in village; 5) Type 5 facilities, adjoining village; and 6) Type 6 facilities, scattered irregularly inside and outside of village. Based on the classification, possible implementations for the reduction of environmental impacts were suggested. The results of this study could be used as an example of study on the distribution, classification, and rearrangement of environment-impacting facilities in rural areas for improvement of their roles in providing amenity resources.