• 한국환경복원기술학회지
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• 제13권2호
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• pp.80-94
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• 2010

The purpose of this study is suggest to restoration model of Pinus thunbergii in Saha-gu, Busan. The result of this study is summarized as follows. As the results of this study, vegetation restoration model is presented by separating community planting and edge planting. In community planting, as a group of canopy, there are 6 species; Pinus thunbergii, Quercus acutissima, Quercus dentata, Quercus serrata, Quercus alienna, Quercus variabilis. As a group of understory, there are 5 species; Platycarya strobilacea, Prunus sargentii, Styrax japonica, Eurya japonica, Morus bombycis. Also as a group of shrub, there were 15 kinds of species; Ulmus pavifolia, Ulmus davidiana, Lindera obtusiloba, Elaeagnus macrophylla, Mallotus japonicus, Ligustrum obtusifolium, Sorbus alnifolia, Rhus trichocarpa, Zanthoxylum schinifolium, Rosa wichuraiana, Rhus chinensis, Viburnum erosum, Rhododendron mucronulatum, Rhododendron yedoense, Indigofera pseudotinctoria. And as a group of edge vegetation, there were 10 kinds of species; Japanese Angelica, Symplocos chinensis, Pittosporum tobira, Lespedeza maximowiczii, Lespedeza bicolor, Rubus coreanus, Rubus idaeus, Vitis thunbergii, Ampelopsis brevipedunculata, Rosa multiflora. Vegetation restoration models of Pinus thunbergii community were calculated the units $400m^2$ for the average populations of the woody layer is 24 in canopy layer, 35 in understory layer, 410 in shrub layer, 34% herbaceous layer ground cover. And the average of breast-high area and canopy area is $10,852cm^2$ in canopy layer, in understory layer $1,546cm^2$, in shrub layer $1,158,660cm^2$. The shortest distance between trees is calculated as 2.0m in canopy layer, 1.9m in understory layer.

• 한국조경학회지
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• 제29권1호
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• pp.51-66
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• 2001

The purpose of this study is to suggest the ecological management based on ecological characteristics of urban forest in Bucheon city. The actual vegetation area in the survey sites(7,426,587$m^2$) consisted of Robinuia pseudoacacia forest(61.6%; 5,574,168 $m^2$), Pinus rigida forest(6.1%), Quercus mongolica community(3.2%), Q.spp.community(2.9%), etc. According to the importance value of artificial planting forest, 58(/300$m^2$) survey plots were divided into 6 groups; 1) R. pseudoacacia forest, 2) R. pseudoacacia-Q.serrata community, 3) R. pseudoacacia-Q.mongolica community, 4) P.rigide forest, 5) P.rigida-Q.serrata community, 6) P.rigida-Q. mongolica community. As the result, the artificial planting forest was expected to the proceeded to Q. serrata community and Q.mongolica community. The ecological succesion stage in the survey sites (7,426,587$m^2$) was divided into 5 states based on actual vegetation, succession trend of artificial planting forest in Bucheon; 1) Stage of impossible succession(4.7%, 2)Stage of inducible succession(78.7%), 3) Stage of progressive succession(2.7%), 4)Sage of last succession(1.4%), 5)Stage of native plant forest(12.5%). The ecological management of urban forest was suggested as the management method for succession promotion, according to density controlling and native species planting in Bucheon. Individual numbers of R. pseudoacacia might be reduced to 6~8 individuals/300$m^2$ at canopy, 9~21 individuals/300$m^2$ at under-story by selective cutting in order to keep 63~70% of total basal area at R. pseudoacacia forest. Individual numbers of P.rigida might be reduced to 8~9 individuals/300$m^2$ at canopy, 27~30individuals/300$m^2$ at under-story by selective cutting in order to keep 68~75% of total basal area at P. rigida forest. 24 species that were selective by constancy analysis were chosen as the ecological appropriate species. Since, this studyis discussing the ares of urban forest and botanical ecology, it is suggested that a study on the relations between of environmental factors such as soil, climate, and vegetation will be performed in the future.

• 한국환경복원기술학회지
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• 제14권1호
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• pp.57-65
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• 2011

The composition of species for each community of Quercus by vegetation and soil survey, the community classification by TWINSPAN, the structural characteristics of communities were used and analyzed during the period of 2000~2004 for Quercus mongolica forest. And the resulting suggestions for a subsequent planting model for forest are as follows. The Quercus mongolica community had the highest importance value for Quercus mongolica followed sequentially by Acer pseudosieboldianum, Acer mono, Rhododendron schlippenbachii, Tilia amurensis, Fraxinus rhynchophylla, and Fraxinus sieboldiana. As a result of suggesting a planting modeling for the Quercus mongolica communities in the areas with the warmth index of both $60.90{\sim}79.79^{\circ}C$ and $53.96{\sim}64.82^{\circ}C$, Quercus mongolica was absolutely dominant in case of the subtree layer for the accompaniment species of distribution in the planting modeling by tree layer in the two areas depending on the warmth index, while there were distinct differences shown in case of the lower tree layer. While Acer pseudosieboldianum, Tilia amurensis, Fraxinus rhynchophylla, Sorbus alnifolia, Acer mono, etc. were appeared in the subtree layer for the areas with the warmth index of $60.90{\sim}79.79^{\circ}C$. Cornus controversa, Quercus mongolica, Fraxinus sieboldiana, etc. were many appeared in the subtree layer for the areas with the warmth index of $53.96{\sim}64.82^{\circ}C$. And, when we made ecological Quercus mongolica community, subtree layer planting is different by warmth index.

• 인간식물환경학회지
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• 제22권6호
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• pp.541-550
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• 2019

This study is to find out the proper planting and utilization plans for climbing plants in urban community gardens. As a result, a majority of respondents claimed that it is acceptable to plant climbing plants in their plots of the community garden. In particular, those who have experiences with gardening activities responded that climbing plants could be allowed in the community gardens. There was a high tendency to use climbing plants in community gardens for aesthetic or ornamental use and for creating fences. Many respondents also claimed that the climbing plants should be planted outside or on the edge of the garden and that the plants should not cross over to other plots. Those who responded that the climbing plants should be planted outside or on the edge of the community garden wanted to use the plants for aesthetic or ornamental use. Those who wanted to use the plants for creating shades responded that the plants should be planted outside or on the edge of the garden. For proper planting of climbing plants in the community garden, it is necessary to consider the height of the vertical plant support depending to the gap between the plots in the community gardens, the shape and color of flowers, leaves, and stems for aesthetic use, and mixing of plants for the duration of the shade period. Accordingly, introduction of climbing plants can be considered to increase the diversity of plants in urban community gardens.

• 한국조경학회지
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• 제39권2호
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• pp.91-102
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• 2011

본 연구에서는 국내 현실을 고려한 도시공원의 생태적 배식기법을 마련하기 위해 여의도공원 자연생태의 숲의 조성단계별 문제점과 원인을 고찰하여 개선방안을 제시하였다. 실시설계단계에서는 가장 중요한 배식모델과 도면작성이 불명확하게 제시되었고, 식재수량 및 규격이 비현실적이었다. 시공단계에서는 설계도면과 다른 유사수종 및 다른 규격의 수목이 식재되었고, 목표군락에 따른 토양환경 기반 조성이 이루어지지 못해 생태적 배식에 한계가 있었다. 관리단계에서는 하자보식 처리가 미흡하고, 하자보수 담보기간 이후의 관리대책이 부재하였다. 도시공원 생태숲 조성을 위한 단계별 개선방안을 제시하였다. 실시설계단계에서는 반드시 목표 배식모델을 고려하여 교목층, 아교목층, 관목층별 식재도면을 작성해야 하고, 수목 자원조사결과를 통해 현실적으로 가능한 식재종 및 규격을 제시해야 한다. 시공단계에서는 이식대상 수목에 인식표를 부착하여 적정한 식재종 및 규격으로 식재가 이루어져야 하며, 수종 변경시 식재모델에 적합한지를 검토하도록 시방서에 명기하고, 규격 변경시 실제규격으로 준공처리를 하고, 목표모델에 적합한 토양이 유입될 수 있도록 반입 토양의 의무적인 분석이 필요하다. 관리단계에서는 관급수목에 대한 하자처리를 위해 설계시 일정 할증율을 반영하고, 하자보수 담보기간을 2년에서 5년으로 확대하며, 시간변화에 따른 목표군락별 변화과정을 관찰할 수 있도록 준공후 5년 동안 모니터링 의무화 등이 필요하다.

• 한국환경복원기술학회지
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• 제14권1호
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• pp.89-104
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• 2011

This study was carried out to the development of ecological planting model to make up of coastal windbreak forest on the Suncheon-bay in Sucheon-si, Korea. Make up of coastal windbreak forest in this site was needed for appropriate bioresource, biodiversity and ecological structure, and for conservation of the eco-tour resource and protection of human life and property by the unforeseen disaster from the coast. Based on the plant-social principle, the planting model of windbreak forest was developed to facilitate growth of trees, considering planting locations. The ecological planting model for the coastal windbreak was composed of warm temperate evergreen and windbreak forest which is spreading around the inland area in Korea. The horizontal forest style was composed of forest edge community and inner forest community, and the vertical forest style was composed of upper, middle, low and ground planting class. The target of the present model was quasi-natural forest, and the species of tree were selected based on the adaptability to surroundings depending on a goal to create a forest and forest style. To achieve both functions of wind break forest and visual effect in short period of time, small trees and seedlings were planted with high-density of 40,000/ha in an expectation of easy natural maintenance in the future. The significance of the present study is a suggestion for a guideline to create ecological coastal windbreak forest in the Suncheon-bay in which the harmony of human life and the ecological conservation is of great importance. Also, the ecological coastal windbreak forest model should be developed further through the long term monitoring after construction of forest.

• 한국조경학회지
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• 제21권2호
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• pp.107-119
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• 1993

This study was conducted to increase to increase the plant species diversity, which was based on the analysis of plant community structure and the survey of human's disturbance degree in Mt. Yongma and Mt. Acha urban nature park, Seoul. The plant community were divided into four groups by TWINSPAN and DCA. These groups were Pinus rigida-P. densiflora community, Quercus mongolica-Q.aliena-Q.accutissima community, Robinia pseudoacaia-Q.accutissima-Poplus${\times}$albaglandulosa community and R.pseudoacacia community. The successional trends of tree species seems to be from P.densiflora, P.rigida, Sorbus alniflora to Q.mongolica, Q.aliena and from P.${\times}$albaglandulosa, R.pseudoacacia, through Q.accutissima, to Q. mongolica, Q.aliena. The species diversity of plant community was high in natual plant community but was low in artificial planting community respectively. Number of species, number of species individuals, indices of species diversity was lowered and soil hardness was increased by the user's trampling, undercutting work and planting P.koraiensis after thinning. In the basis of study results, we proposed the management plan for the urban forest.

• 한국조경학회지
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• 제43권1호
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• pp.16-28
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• 2015

본 연구는 인천광역시 남구의 주민 생활과 밀접한 생활권 주변 지역과 커뮤니티 공간을 연계한 커뮤니티형 그린웨이 조성방안을 제시하여 생활권 녹지의 확충 및 지역 커뮤니티 형성을 도모하고자 하였다. 도시생태 특성으로 토지이용과 녹피율을 조사 분석하여 녹지 확보 필요성을 제시하였고, 커뮤니티 형성을 위한 거주지 주변 시설을 유형별로 분석하였다. 남구를 생활권별로 구분하여 커뮤니티형 그린웨이 노선을 설정하였고, 노선별 특성을 분석 및 유형화하여 유형별 커뮤니티형 그린웨이 조성방안을 제시하였다. 인천광역시 남구는 시가지 87.7%, 녹지 및 오픈스페이스가 12.3%이었고, 녹피율은 17.51%로 녹지가 매우 부족하였다. 녹지의 반 이상이 도시외곽에 분포한 면적이 넓은 산림으로서 도시 내 주민 생활권 주변의 녹지확보가 필요하였다. 남구의 커뮤니티 형성을 위한 시설은 교육시설 7.7%, 공원시설 1.7%, 녹지시설이 1.9% 등으로 교육시설의 비율이 높았다. 남구의 생활권을 총 31개로 구분하였고, 생활권 내 커뮤니티 시설과 녹지를 연계할 수 있는 커뮤니형 그린웨이 20개 노선을 선정하였다. 노선별 특성은 토지이용 및 가로환경과 커뮤니티 시설 측면으로 종합 분석하여 도출하였다. 커뮤니티형 그린웨이의 유형화는 그린웨이 계획의 기능과 목적, 주변 토지이용현황, 커뮤니티 시설 유형을 고려하여 6가지 유형으로 구분하였다. 유형별 조성방안은 그린웨이 기능과 목적에 따른 조성방향, 주거지역과 상업업무 지역으로 구분한 토지이용 유형별 조성방향, 근린생활형, 교육형, 종교형, 레크리에이션형 등 커뮤니티 시설 유형별 조성방향을 제안하였다. 또한 그린웨이 녹화유형별 녹화구상에 적합한 녹화방법으로 벽면녹화, 옥상녹화, 베란다 녹화와 같은 건축물 차원과 공원, 학교, 공공기관, 도로, 주차장, 자투리공간과 같은 단지차원으로 구분하여 각 그린웨이 유형별 조성방안을 제안하였다.

• 한국환경과학회지
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• 제32권3호
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• pp.161-171
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• 2023

The present study evaluated growth factors affecting oak community plantations through literature review and a field survey. Specifically, 41 related literature sources were analyzed and field surveys were conducted to collect growth data. Previous studies were analyzed to identify variables with high frequency of use. The frequency of use was in the order of tree size > environment > planting density > forest age. Analysis of factors impacting height and diameter growth revealed that the growth rate of species other than Quercus variabilis was negative in the field survey. This may be because of differences between the actual trees planted and specifications in the construction drawings, which may be attributed to the site conditions and decisions made by the project subject during construction. Furthermore, simple linear regression analysis was conducted with time, height at planting, density, and species code as the independent variables and growth rate as the dependent variable. A strong positive linear correlation was noted between height and diameter. This work builds a foundation for developing a forest restoration model and simulation program based on a regression model derived from the four variables tested.

• 한국조경학회지
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• 제25권4호
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• pp.123-140
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• 1998

The flora of Kunsan Wolmyong park was 77 families, 168 genera, 240 species, 2 subspecies, 35 varieties, 1 formae or 278taxa. Using the Phytosociology method, 12 plant communities were recognized ; Alnus japonica, Pinus densiflora, Pinus thunbergii, Pinus rigida, Castanea crenata, Quercus acutissima, Robinia pseudo-acacia, Alnus hirsuta, Quercus serrata, Aluns firma, Liriope platyphylla and Reynoutria communities. Similarity between different communities was low for most of the cases except for Pinus densiflora, Pinus Thunbergii and Pinus rigida communities kept comparely high with ond another. Species diversity was analyzed by species richness(SR), species diversity index(H') and evenness(J'). Castanea crenata, Robinia pseudo-acacia and Alnus firma communities were higher in SR, H' than the other communities. But Pinus rigida, Quercus acutissima and castanea crenata communities were higher in evenness than the other communities. To investigate the plant community structure and to establish restoration counter plan of a Wolmyeng Park in Kunsan City. As a remedial approach, following is propesed. first, Establishment of an adequate planting plan and development of slope stalilization method by planting native species. second, Sellection of adequate species by planting experiments for pioneer species, native species, and dietary species. third, Landscape planting zones should be managed artificially, the others be managed with ecological approach.