• 제목/요약/키워드: Planting Layer

검색결과 117건 처리시간 0.023초

조경식재공간에서 다층식재의 실태분석 -수도권 아파트와 근린공원을 중심으로- (An Analysis of Status Quo on the Multi-layer Planting at the landscape Planting Area in Apartment and Neighborhood Parks in Seoul Metropolitan Area)

  • 심우경;이동익
    • 한국조경학회지
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    • 제29권1호
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    • pp.140-151
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    • 2001
  • This study based on the theoretical understanding of multi-layer planting which have engineering, ecological and landscape benefits, was conducted to find out the status of multi-layer planting in the apartment and neighborhood park in Seoul. This study was also aimed to seek for the problematic matters, and suggest a solution on the current multi-layer planting. The results of this study were as follows; 1) Since landscape woody plants have been classified just as tree and shrub in Korea, the classification for the multi-layer planting has been unreasonable, and landscape woody plants might have been classified as tree, sub-tree and shrub, or upper, middle, and lower-layer, It could be defined that upper layer is over eight meters in full growth, middle over 3-8 meters and lower under 3 meters. 2) In apartments, the upper layer consisted of eighteen species, the middle and lower layer seven species each. In neighborhood parks, the upper layer consisted of fifteen species, and the middle and lower layer five species each. 3) In terms of planting year of the surveyed areas, there were no differences in the number of species when planting year of the apartment was divided into two groups, the first half(1900-1995) and the second(1996-2000). But, in terms of individual occupation, the percentage was decreased in upper layer, while there was increasing in middle and lower layer. 4) As the result of survey of multi-layered area, it appeared that apartment was shown 0.65 percent and neighborhood park 0.61 percent of the planted area, which was less than 1 percentage of landscape architecturally planted area. 5) In apartment, the number of individual in middle layers has been increased in the first half and the second, but with respect to the correlation with multi-layered area, the apartments had the "$\rho$=0.208", saying that increasing middle layer was scattered planting instead of multi-layered planting. 6) In planting at the apartments in Korea, the planting density was limited, because the layer division was restricted to only tree and shrub. On the contrary, it was divided into upper, middle and lower tree in Japan. Therefore, in Korea, it should be classified as the planting density by dividing into tree, sub-tree, and shrubs, or upper, middle and lower tree by the law. And, it should be considered that the multi-layered planting has a proper organic relation as well as the planting density.g density.

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Relationship between Vertical Root Distribution and Yield Traits in IRRI's New Plant Type Rice

  • Kim, Bo-Kyeong;Kang, Si-Yong;Shin, Hyun-tak;Yang, Sae-Jun
    • 한국작물학회지
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    • 제44권1호
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    • pp.20-25
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    • 1999
  • This experiment was conducted to elucidate the relation-ship between vertical distribution of rice roots and yield traits under field conditions. Eight IRRI's new plant type rices (NPTRs) were tested in a volcanic ash soil paddy field under dense (IO 10 cm) and common (20 20 cm) planting densities. These lines were evaluated to have more spikelet numbers per panicle (SNP), lower filled grain rate (FGR), and lower rough grain weight per hill (RGWH). In dense planting, rough grain weight per stem (RGWS) was increased due to heavier culm and leaf dry weight (CLDW), and both RGWS and CLDW were related with the percentage of root distribution (%RWI) in the 10~30 cm soil layer, while in common planting, RGWS was not closely related with CLDW. SNP was highly related with root dry weight (RDW) in the 0~10cm soil layer. FGR was mainly affected by ROW in the 10~30 cm soil layer under both planting densities. RGWS was positively correlated with top dry weight (TDW) and harvest index (HI), and TDW was positively correlated with RWI under common planting or %RWI under dense planting, and HI was positively correlated with RWI in the 10~30 cm soil layer only under dense planting. RGWS was closely related with root weight index by dry weight (RWI) in the 10~30 cm soil layer and %RWI in the 0~30 cm or 10~30 cm soil layer under dense planting, and with only RWI in the 10~30 cm soil layer under common planting. But RGWH showed the close positive relationship with RDW and RWI in the 10~30 cm soil layer under dense planting, while under common planting, it showed the close positive relationship with RWI and %RWI in the 10~30 cm soil layer or %RWI in the 0~30 cm soil layer. The deeper root system in rice, especially under dense planting, is important for high yield of NPTRs focusing on the increment of top mass production and harvest index.

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옥상녹화 식재기법에 따른 식생변화 - 이입식물을 중심으로 - (Rooftop Planting Methods and Invading Species)

  • 최희선;안동만
    • 한국환경복원기술학회지
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    • 제7권3호
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    • pp.35-47
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    • 2004
  • In order to study changes in vegetation pursuant to rooftop revegetation plantation methods, plantation methods for rooftop revegetation were divided into two types through an analysis of recent trends. Then, Planted plants and invasive plants on sites where the planting methods were introduced were monitored. Planting methods were divided into mono-layer meadow cover type and multi-layer planting cover type. They showed some differences in terms of the availability of wetland, the structure of vegetation layers, the planted species, and the material of mulching. According to the results of monitoring the two sample sites for different plantation methods, the number of invasive plants was higher in multi-layer planting cover type and the ratio of naturalized plants was higher by 30% in average in mono-layer meadow cover type. The main reason for such a result is that the natural soil used in the multi-layer planting cover type likely contained some seeds. Moreover, it's harder for invasive plant seeds to germinate in volcanic rocks than in natural soil. Also, it is attributable to wetlands available in multi-layer planting cover type and diverse living environments created by multi-layer planting. The reason of the ratio of naturalized plants being higher by at least 10% in mono-layer meadow cover type is the character of naturalized plants being stronger in unfavorable conditions than nature plants are. Accordingly, the germination rate in the volcanic rock mulching has likely contributed in raising the introduction and germination of naturalized plants. The results showed that multi-layer planting cover type using wetland creation and nature soil can increase the number of invasive plants and lower the ratio of naturalized plants. However, since seeds contained in the natural soil can affect the growth of planted plants, this needs to be clarified, It was judged that mono-layer meadow cover type may affect more greatly on the germination and growth of invasive plants than on those of planted plants, Its potential adoption in highly urbanized areas was examined. By complementing with the mutual benefits of each plantation method, it appeared possible to shift to a rooftop revegetation system suitable to the site.

도시지역 곰솔림의 식생복원모델 (Vegetation Restoration Model of Pinus thunbergii in Urban Areas)

  • 김석규
    • 환경영향평가
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    • 제20권2호
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    • pp.151-162
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    • 2011
  • The purpose of this study is suggest to restoration model of Pinus thunbergii in Saha-gu, Busan Metropolitan City. 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. The community planting species of tree layer were Pinus thunbergii and Quercus acutissima and Quercus dentata and Quercus serrata and Quercus alienna and Quercus variabilis. The community planting species of subtree layer were Platycarya strobilacea and Prunus sargentii and Styrax japonica and Eurya japonica and Morus bombycis. The community planting species of shrub layer are Ulmus pavifolia and Ulmus davidiana and Lindera obtusiloba and Elaeagnus macrophylla and Mallotus japonicus and Ligustrum obtusifolium and Sorbus alnifolia and Rhus trichocarpa and Zanthoxylum schinifolium and Rosa wichuraiana and Rhus chinensis and Viburnum erosum and Rhododendron mucronulatum and Rhododendron yedoense and Indigofera pseudotinctoria. And the planting species of edge vegetation are Japanese Angelica and Symplocos chinensis and Pittosporum tobira and Lespedeza maximowiczii and Lespedeza bicolor and Rubus coreanus and Rubus idaeus and Vitis thunbergii and Ampelopsis brevipedunculata and Rosa multiflora. Considering the population of individuals up to layers in each $400m^2$ area, it was composed of 24 in tree layer, 35 in subtree layer, 410 in shrub layer and 34% herb layer in the Pinus thunbergii community. And the average of breast-high area and canopy area was $10,852cm^2$ in tree layer, in subtree layer $1,546cm^2$, in shrub layer $1,158,660cm^2$. The shortest distance between trees was calculated as 2.0m in tree layer, 1.9m in subtree layer.

폐기물매립지 인공식재지반 조성 사례연구 -수도권매립지 제방이격구간 식재층을 대상으로- (A Case Study on the Creating Artificial Planting Ground on the Waste Landfill Sites -In Case of the Bank Isolated Section Planting Layer at the Landfills of Satellite Cities of Seoul-)

  • 조주형;이재근
    • 한국조경학회지
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    • 제29권1호
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    • pp.131-139
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    • 2001
  • This paper aims at surveying through case studies the planting possibility on the interval artificial ground between the bank and the core landfill of the first section of works in the SUDOKWON Landfill area landfill area which was completed, followed by the layer-on-layer landfill process involving the latch or sealing layer against emitting landfill gas from the reclaimed waste. The survey results are as follows; 1. The layers of the artificial planting ground on the landfill were established on the basis of top-on-top procedure for a waste layer, a topping soil layer (T=50cm), a gas blocking layer (broken stones T=30cm), a filter layer (non-woven fabric 700g), a sheet protecting soil layer (T=20cm), and a blocking layer (HDPE SHEET 2.0mm), an irrigation layer (SAND T=30cm), a filter layer (non-woven fabric 700g), a sheet protecting soil layer (T=20cm), and a blocking layer (HDPE SHEET 2.0mm), an irrigation layer (SAND T=30cm), a filter layer (non-woven fabric 700g), a planting layer (T=90cm+), a top mound (T=2m). 2. Since no direct damage on the planting layer affected by the landfill gas was detected, planting is found to be still possible and successful except the severely unequal subsidence portion. 3. The mortality rate is discovered different on different trees: Pinus thunbergii (H3.0$\times$W1.0m) 11.25%, Pinus thunbergii (H2.5$\times$W0.8m) 4.73%, Koelreuteira paniculata 8.67%, Hibiscus syriacus 5.68%, Deutzia parviflora 6.50%, Forsythia koreana 8.17%, Rho. yedoense v. poukhanese 32.22%, and Spiraea pru v. symplicifolia 18.89%; although the last two of which are generally considered to have a strong generic growing character, they are subject to be weakened when exposed to the contaminated microclimate of the site like landfill gas. 4. The damage rates, on Pinus thunbergii, Koelreuteria paniculata, Hibiscus syracus, Forsythia koreana, Deutzia parviflora, Rho. yedoense v. poukhanense were shown to decrease to 7.31-17.69% in the second check (June 2000) lower than 5.77-46.92% in the first examination (June 1999), whereas the damage on Spiraea pru v. symplicifolia relatively increased. It is believed that preparatory method of the air pollution, change of temperature, odor by emitting landfill gas, and minute dust from vehicles should be made, and a research on this matter will be conducted in the near future.

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펄라이트로 조성된 토양층의 하중 (Load of Soil Layers Established with Perlite)

  • 이성기;류남형;허근영
    • 한국조경학회지
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    • 제30권1호
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    • pp.87-95
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    • 2002
  • This study was carried out to investigate the load of soil layers affected by soil depth in artificial soil alone or in blends with Loam with various ratio. The artificial soils were perlite large grain, perlite small grain, and perlite small grains blended with Loam (sand 46%, silt 40%, clay 14%) at a ratio of 8:2, 6:4, 5:5 (v/v). The soil layers were divided into a planting layer and a well-drained layer, then the weight of each layer in the air-dried state and in the field capacity were determined. The data were subjected to correlation analysis, regression analysis, and paired samples t-test. The summarized results are as follows; 1) In the air-dried state, the regression equations of the well-drained layer weight(kg/m2) in perlite large grain, planting layer weight in perlite small grain, planting layer weight in perlite small grain biended with loam(8:2, v/v), perlite small grain blended with loam(6:4, v/v), and perlite small grain blended with loam(5:5, v/v) were; 1.65824*X+0.026, 1.52292*X-0.052, 3.21468*X+0.515, 6.17549*X+ 0.083, and 6.02100*X + 33.133, respectively, where X is soil depth measured in Centimeters. 2) In the field capacity, the regression equations of the well-drained layer weight(kg/m2) in perlite large grain, planting layer weight in perlite small grain, planting layer weight in perlite small grain blended with loam(8:2, v/v), perlite small grain blended with loam(6:4, v/v), and perlite small grain blended with loam(5:5, v/v) were 5.055*X - 2.006, 7.073*X + 100.008, 8.092*X + 116.676, 10.766*X + 100.112, and 10.974*X + 124.423, respectively, where X is the soil depth measured in Centimeters. 3) All of the equations mentioned above were statistically reliable and therefore easily applicable in practical business affairs.

서울시 아파트단지내 조경수목 배식특성 및 개선 연구 (Improvement Planting Method and Characteristics of Planting Design with Ornamental Trees in Apartment Complex, Seoul)

  • 이경재;한봉호;이수동
    • 한국환경생태학회지
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    • 제18권2호
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    • pp.236-248
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    • 2004
  • 본 연구는 서울시에 조성된 아파트단지내 녹지를 대상으로 식재개념, 식재밀도, 식재유형 및 패턴 등 배식특성을 조사.분석하여 개선방안을 제시하고자 실시하였다. 대상지는 아파트단지 녹지면적이 크게 달라지는 시기의 대표대상지인 1978년에 준공된 강서구 화곡주공아파트(2단지)(용적률:99%), 1983년에 준공되 강남구 삼익그린아파트(2차)(용적률:175%), 1992년에 준공된 강서구 동신대아아파트(용적률:225%)를 선정하였으며 녹지를 전면녹지, 측면녹지, 후면녹지로 구분하였다. 대상지의 녹지유형별 식재개념은 경관식재로만 이루어져 시기에 따른 차이는 없었으며 식재종에 있어서도 외래종 조경수목이 주를 이루어 녹지공간별 차이는 없었다. 아파트단지의 식재밀도은 교목 및 아교목층 0.0~0.2주/$m^{2}$로 관목층의 식재밀도가 부족하였으나 조성시기에 따른 식재밀도의 차이는 없었다. 층위구조는 교목.아교목층과 관목층 수목이 각각 다른 위치에 평면적으로 식재된 단층구조이었으며 녹지공간과 관계없이 독립식재, 열식재, 부등변삼각식재가 주로 활용되었다. 아파트 단지내 녹지는 공가별 식재개념에 따라 식재종, 식재밀도, 층위구조, 식재패턴이 다양하게 이루어져야 하므로 식재개념에 차별화시키기 위하여 전면녹지는 시각적 차폐와 미적인 기능, 후면녹지는 녹지량 증지 및 생태적 개념, 측면녹지는 녹지량을 증진을 주된 목적으로 조성할 것을 제안하였다.

도시림 식생의 생태적 특성과 복원모델 (Ecological Characteristics and Restoration Model of Vegetation in the Urban Forest)

  • 김석규;주경중;남정칠;박승범
    • 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.

식생 군집분석과 종간친화력 분석을 통한 서울형 다층구조 식재모델 제안 (Suggestions for Multi-Layer Planting Model in Seoul Area Based on a Cluster Analysis and Interspecific Association)

  • 김민경;심우경
    • 한국조경학회지
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    • 제38권4호
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    • pp.106-127
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    • 2010
  • 최근 생태환경 조성을 위한 다층구조 식재는 식생복원 등 환경사업뿐만 아니라 군락식재의 방법으로서 활용이 확산되고 있으나, 실제 조경 식재 설계에 있어 다층식재 기법을 활용하는 데에는 어려움이 있었다. 본 연구는 서울지역의 숲 구조를 분석하여 다층식재 시 활용 가능한 기초적 다층 식재모델 개발을 목적으로 하고 있다. 이를 위해 생태분석프로그램인 PC ORD 4.0(MjM Soft, 2002) 프로그램을 활용, ISA(Indicator Species Analysis) 분석을 통한 적정 군집수를 설정하여 군집분석을 실시하였다. 그 결과 상수리나무군락, 신갈나무-팔배나무군락, 소나무-리기다소나무군락, 신갈나무-진달래군락, 선갈나무-노간주나무군락, 소나무-진달래군락, 선갈나무-철쭉나무군락 등의 7개의 자연 식생군락으로 분석되었다. 그리고 대상지에 출현한 빈도 10% 이상의 식물종간의 종간친화력 검정을 통하여, 자연식생에서의 수반종과 함께 수급 및 유통이 가능한 대체 유사종을 제시함으로써 활용도를 높였다. 위의 결과를 종합한 7개 자연식생군락을 기초로 하여, 군락 내 종간 친화력이 있는 식물종을 재선정하여 조경 식재 설계 시 활용할 수 있는 다층식재 모델을 제안하였다. 개발된 다층식재 모델은 변환우점도 값의 평균값을 기준으로 하여 평균 목표피도를 제시함으로써 식재설계 시 폭넓게 응용할 수 있도록 하였다.

일본 고베시(신호시(神戶市)) 로코(육갑(六甲))아일랜드 임해매립지의 완충녹지 식재기법 연구 (Planting Method of Buffer Green Space in the Reclaimed Seaside Areas, Rokko Island, Kobe, Japan)

  • 한봉호;김종엽;최진우;조용현
    • 한국환경생태학회지
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    • 제24권2호
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    • pp.157-165
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    • 2010
  • 본 연구는 일본 고베시 로코아일랜드 완충녹지의 공간기능별 지형구조, 식재개념, 식재구조를 조사분석하여 해안매립도시의 토지이용을 고려한 완충녹지 식재기법 연구 기초자료를 제공하고자 수행하였다. 로코아일랜드(총면적 580ha)는 대규모 완충녹지를 박스형으로 조성하여 외곽부의 항만물류 산업용지와 도시내부 도시기능용지로 구획되었다. 완충녹지 지형구조는 편향마운딩형, 병렬마운딩형, 복합마운딩형이었고, 북쪽의 녹지폭은 50m, 동쪽의 녹지폭은 8~32m, 서쪽의 녹지폭은 37.5m, 경사도는 $18\sim25^{\circ}$, 성토고는 2~15m이었다. 공간기능별 재개념은 해안측 사면부는 경관식재와 완충식재, 도시내부는 경관식재와 녹음식재를 적용하였다. 북측 완충녹지 식재구조 조사결과, 종가시나무, 녹나무, 후박나무, 녹보리똥나무 등 난온대 상록활엽수를 식재하였고, $100mm^2$단위의 종수 및 식재밀도는 최대 교목 9종 22주, 아교목 9종 15주, 관목 3종 67주로 전 층위 14종 104주이었다. 녹피율은 교목층 69~139%, 아교목층 26~38%, 관목층 6~7%, 전 층위 101~184%, 녹지용적계수는 교목층 $1.40\sim3.12m^3/m^2$, 아교목층 $0.43\sim0.55m^3/m^2$, 관목층 $0.06m^3/m^2$, 전 층위 $1.89\sim3.73m^3/m^2$이었다.