This study is to offer the basic information and materials for the restoration of the urban forest and the ecologically healthy and continuous green belt through the investigation and the analysis on the vegetation in Madong Park, Iksan-City. The flora of Madong Neighborhood park was composed of 65 families, 153 genera, 169 species, 19 varieties， 2 formae or 196 taxa. Some characteristics of the plants in this area have represented such as Th-D4- Rs type in biological type, erect form (35.71%), in growth type， 21 taxa in naturalized plants. The life form spectra investigated from Iksan neighborhood park was recognized as the following Th :21. 9%, H:17.4%, Th(w):11.7%, G:9.7%, M:6.6%, Ch:5.1%, HH(Th):4.1%, HH: 1. 5%. By the Z-M method 2 plant communities was recognized PÍnus thunbergii community and PÍnus rigida community. The pattern of successional trend of tree species might be suggested : p. rigida and P. th unberglÏ • Q uercus variabjJis and Q acutissima • Q serrata community. Finally, The vegetation of the Madong neighborhood park must not allowed any more. Nothing can be better than native states in preserving the ecosystems.

본 연구는 도시공원의 효율적 관리를 위해 모색되고 있는 도시공원의 주민참여관리제도의 이론적 토대와 기초자료를 마련하기 위한 목적으로 수행되었다. 이를 위해 서울시 도봉구의 초안산근린공원을 찾은 이용객들을 대상으로 사회.경제적 특성, 공원에 대한 관심도, 공원의 관리현황에 대한 인식, 공원관리에의 참여의사 등을 내용으로 설문조사를 실시하였으며, 회수된 75부의 설문지 중 유효표본은 63부였다. 응답자들의 공원에 대한 관심도가 비교적 높게 나타났으며, 공원의 관리현황을 긍정적으로 인식하고 있었다. 공원관리에의 참여의사에 있어서 응답자들은 비교적 강한 참여의사를 지니고 있었으며, 이러한 경향은 노령층과 고소득층, 공원에 대한 관심도가 높은 응답자에게서 더욱 강하게 나타났다. 특히, 공원에 대한 관심도 수준에 따른 공원관리에의 참여 의식 차이는 기존의 연구결과를 뒷받침하는 것이었다.

In order to investigate the effect of air temperature reduction on an urban neighborhood park, air temperature data from five inside locations (forest, pine tree, lawn, brick and pergola) depending on surface types and three outside locations (Suwon, Maetan and Kwonsun) depending on urban forms were collected during the summer 2016 and compared. The forest location had the lowest mean air temperature amongst all locations sampled, though the mean difference between this and the other four locations in the park was relatively small (0.2-0.5℃). In the daytime, the greatest mean difference between the forest location and the two locations exposed to direct beam solar radiation (brick and lawn) was 0.5-0.8℃ (Max. 1.6-2.1℃). In the nighttime, the mean difference between the forest location and the other four locations in the park was small, though differences between the forest location and locations with grass cover (pine tree and lawn) reached a maximum of 0.9-1.7℃. Comparing air temperature between sunny and shaded locations, the shaded locations showed a maximum of 1.5℃ lower temperature in the daytime and 0.7℃ higher in the nighttime. Comparing the air temperature of the forest location with those of the residential (Kwonsun) and apartment (Maetan) locations, the mean air temperature difference was 0.8-1.0℃, higher than those measured between the forest location and the other park locations. The temperatures measured in the forest location were mean 0.9-1.3℃ (Max. 2.0-3.9℃) lower in the daytime than for the residential and apartment locations and mean 0.4-1.0℃ (Max. 1.3-3.1℃) lower in the nighttime. During the hottest period of each month, the difference was greater than the mean monthly differences, with temperatures in the residential and apartment locations mean 1.0-1.6℃ higher than those measured in the forest location. The effect of air temperature reduction on sampling locations within the park and a relatively high thermal environment on the urban sampling locations was clearly evident in the daytime, and the shading effect of trees in the forest location must be most effective. In the nighttime, areas with a high sky view factor and surface types with high evapotranspiration potential (e.g. grass) showed the maximum air temperature reduction. In the urban areas outside the park, the low-rise building area, with a high sky view factor, showed high air temperature due to the effect of solar (shortwave) radiation during the daytime, while in the nighttime the area with high-rise buildings, and hence a low sky view factor, showed high air temperature due to the effect of terrestrial (longwave) radiation emitted by surrounding high-rise building surfaces. The effect of air temperature reduction on the park with a high thermal environment in the city was clearly evident in the daytime, and the shading effect of trees in the forest location must be most effective. In the nighttime, areas with high sky view factor and surface types (e.g., grass) with evapotranspiration effect showed maximum air temperature reduction. In the urban areas outside the park, the high sky view factor area (low-rise building area) showed high air temperature due to the effect of solar (shortwave) radiation during the daytime, but in the nighttime the low sky view factor area (high-rise building area) showed high air temperature due to the effect of terrestrial (longwave) radiation emitted surrounding high-rise building surfaces.