• 제목/요약/키워드: Biotope planting

검색결과 22건 처리시간 0.021초

생태면적률 적용을 통한 도시 내 벽면녹화의 지역적 효과 분석 - 서울시 중구를 사례로 - (Analysis of the Regional Effectiveness of Urban Wall-Planting Applied by a Biotope Area Ratio - Case of Jung-gu District in Seoul -)

  • 강태순;이명우
    • 한국조경학회지
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    • 제42권5호
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    • pp.88-100
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    • 2014
  • 최근 고밀도 시가지의 가장 중요한 해결과제 중 하나는 생태기능의 향상이다. 녹지 확대가 불가능하지만 활용할 수 있는 벽면이 많은 이 지역에서는 벽면녹화가 그 생태기능 향상을 위한 좋은 대체방법이 된다. 본 연구의 목적은 고밀도 시가지 내 전체적으로 벽면녹화가 조성되었을 경우, 그 지역에 미치는 효과를 생태면적률로서 분석하는 것이다. 이를 위해서는 지역적 벽면녹화계획 사례가 필요하므로, 먼저 벽면녹화 유형들을 설정하고, 사례 대상지역에 적용하였다. 연구 결과, 벽면녹화 유형은 형태적, 기능적 특성에 따라 4가지로 설정되었다. A type은 단순형과 기능형, B type은 복합형과 기능형, C type은 단순형과 경관형, D type은 복합형과 경관형의 특징을 지닌다. 사례대상지역으로 서울시 중구를 선정하고, 2011년 6월부터 8월까지 3개월 동안 예비조사 1회, 본 조사 2회에 걸쳐 전수 조사하였다. 최종적으로 결정된 벽면녹화 가능지역은 총 498개소, 총 길이 8,449m, 총 입면적 $23,754.90m^2$이다. 또한 이 대상벽면을 각 유형별로 분류하고 면적산정을 해 본 결과, A type $1,936.65m^2$, B type $5,875.30m^2$, C type $12,487.85m^2$, D type $3,455.10m^2$으로 나타났다. 녹화가능한 벽면의 전체 입면적을 통해 생태면적률 증가분을 분석하였다. 먼저 중구 전체지역에 대한 생태면적률을 총생태면적률, 인공지역에 대한 생태면적률을 순생태면적률이라 정의하였다. 총생태면적률은 현재 17.97%, 조성 후엔 0.10%가 증가하게 된다. 순생태면적률은 현재 4.73%, 조성 후엔 0.11%가 증가하게 된다. 이는 현재의 순생태면적률 4.73%에 대해 2.28%에 해당하는 수치로서, 평면적 자연녹지복원이 거의 어려운 인공지역 $9,256m^2$를 입면녹화를 통해 자연녹지로 복원한 면적이라는 의미를 지닌다. 결과적으로 고밀도 시가지 전체에 조성된 벽면녹화는 그 지역 생태기능 향상에 의미 있는 영향을 미치는 것으로 확인되었다. 또한 입면의 경관적 가치까지 고려해 본다면 벽면녹화의 지역적 효과는 더욱 클 것으로 예상된다.

Biotope Networking in a Metropolitan Area of Daegu -The Case of Susung gu-

  • Ra, Jung-Hwa;Park, In-Hwan;Sagong, Jung-Hee
    • Journal of the Korean Institute of Landscape Architecture International Edition
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    • 제1호
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    • pp.1-12
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    • 2001
  • The biotope network of Susung gu is characterized as dense residence zones forming its core that enable partial biotope in and around the residential zones. First, in district I, it is possible to make these zones connected to the third district. In district II, which is abundant in biotope, it is very important not to continue destoyi9ng the existing biotopes. In the case of district III, old residence zones have fill the severe gap between forests and the Sinchun river, through redevelopment, which covers more than 30% of the biotope area with large scaled linear residence areas. In the case of district IV, limited destruction of biotope and the improvement of nature areas were suggested as the alternative for preservation of biotopes. Consequently, in the construction of the biotope network in Su-sung gu, the maintenance of existing biotopes is required. Int he old residence zones, as redevelopment occurs, by maintaining biotope area of more than 30% and making the scale of residential complexes more than 1ha, it is possible for old residence zones to accomplish the role of providing important green spaces. In the case of newly developed residential zones, by reducing the rate of pavement of traffic conducts, utilizing small sized parks at the junctions and the plantation of trees along the corridors, the entire residence zones are able to accomplish the role of providing important green space. The problem houses and connecting the inner green space of the private houses with the green spaces of the streets in some areas. Futhermore, green spaces of forests must not be used for urban development. Dual planting on sidewalks, planting plots dispersed among streets and median strips must be established on road, too.

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생태적 접근방법에 의한 식생복원 및 관리계획 (Natural Vegetation Restoration and Management Plan by Ecological Approach)

  • 이경재;최송현;강현경
    • 한국환경생태학회지
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    • 제8권1호
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    • pp.58-67
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    • 1994
  • Object of this study is to suggest the plan for natural vegetation restoration and management by ecological approach. The concept of biotope planting technique was introduced in order to restore the natural vegetation in the northern part of Mt. Nam in Seoul, and Quercus mongolica forests was surveyed so as to obtain the basic data. This study focused on the vegetational context between northern part of Mt. Nam and develop-reserved site. The results are following ; 1. It is suitable to plant 25~30 trees in $100\m^2$ with trees of DBH 10cm and below at intervals of about 2m in canopy layer. In the case of subtree layer of DBH 2cm, about 30 trees were planted at an Intervals of 1.5~2m around in $100\m^2$. 2. In the last step of nature vegetation restoration, it is desiable that canopy density is $5/100\m^2$ and 녀btree one is 10~20/$100\m^2$. 3. Management plans was proposed to use the native species of Mt. Nam around and to investigate the ecological situation once a year such as species introduce, dead-tree, soil, fauna etc.

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A Study on the Evaluation of Functional Aspect Value of Individual Biotope -Focused on the Habitat Function of Biotope-

  • Kim, Han Soo
    • 한국환경생태학회지
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    • 제29권2호
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    • pp.263-278
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    • 2015
  • This study is intended to evaluate the value of functional aspect from the viewpoint of habitat. The indicators that are used in biotope evaluations are various, but most of them use the criteria to evaluate the naturality. This evaluation method cannot appropriately reflect the functional characteristics coming from relation to the surrounding biotope. In this study, the connectivity, cohesion and diversity between individual biotope are quantitatively measured by a landscape index. It is hard to draw the functional value of individual biotopes because the landscape index related to connectivity, cohesion and diversity comes from a landscape having a number of biotopes. The concept of contribution was used to overcome this limitation. The concept of contribution is to quantify how much each individual biotope contributes to the connectivity, cohesion, and diversity in a certain range of landscape by deriving the amount of change in the landscape index according to the presence or absence of each individual biotope. In order to understand the characteristics of evaluation results in functional aspect, this research has done a comparative analysis of the previous research findings in the same target area. According to the result of the research, individual biotopes such as artificial forests, fragmented natural forests, and small planting sites were highly rated.

산림생태계 복원유형별 토양동물 변화 (The Change of Soil Animals by Forest Ecosystem Restoration Types)

  • 강현미;송재탁;최송현;김동효
    • 한국환경생태학회지
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    • 제31권1호
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    • pp.62-71
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    • 2017
  • 본 연구에서는 식생 복원 유형별 토양동물의 변화를 알아보기 위해 비오톱이식공법, 산림표토포설, 소경목군락식재, 다층구조군락식재를 적용한 조사구와 이를 비교할 대조구를 선정하였다. 토양동물의 변화를 통한 토양동물자연도 분석 결과, 대조구는 환경에 민감한 동물군과 둔감한 동물군이 골고루 출현하고 있어 토양동물자연도가 높게 확인되었다. 식재를 통해 복원된 조사구의 경우, 비오톱이식공법의 토양동물자연도가 대조구와 유사한 수준까지 도달해 있었으며, 이보다 낮은 수준이긴 하나 소경목군락식재, 다층구조군락식재지역의 토양동물 또한 점진적으로 회복되고 있었다. 가장 낮은 토양동물자연도를 보인 조사구는 산림표토포설지역으로 확인되었다. 이를 통해 비오톱이식공법이 식재를 통해 복원된 조사구가 다른 조사구에 비해 토양동물의 회복이 좀 더 빨리 이루어지고 있음을 파악할 수 있었다. 이는 산림 내부의 숲을 그대로 굴취한 후 이식하는 것으로 표토와 심토의 일부분이 함께 옮겨지기 때문으로 판단된다.

경관생태학적 도시숲 관리를 위한 비오톱 평가지표 및 유형 분류에 관한 연구 (A Study on the Biotope Evaluation and Classification of Urban Forests for Landscape Ecological Management)

  • 오정학;조재형;조현제;최명섭;권진오
    • 한국지리정보학회지
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    • 제11권4호
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    • pp.101-111
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    • 2008
  • 최근 부각되고 있는 도시지역의 환경문제 해결을 위해서는 다각적인 접근방법이 요구되는데, 도시지역에 산재해 있는 도시숲의 효율적 조성 및 관리는 그 방법 중 하나가 될 수 있다. 이에 본 연구에서는 도시숲의 경관생태학적 관리를 위한 평가지표를 설정하고, 대전광역시와 울산광역시 시가지에 분포하는 도시녹지를 대상으로 생물서식공간으로서의 비오톱 유형을 구분하였으며, 그 기능적 특성에 기초한 등급과 식생경관의 구성적 특성을 평가하였다. 평가지표 및 방법은 국내의 연구사례가 드물어 유럽에서 사용되고 있는 지표를 국내 실정에 맞게 수정 보완하였으며, 최종 결과는 합산평가 매트릭스법을 사용하여 분석하였다. 분석결과, 비오톱 유형은 기존 문헌의 조사결과와는 달리 면적이 다양성에 미치는 영향은 적은 것으로 분석되었으며, 중점 비오톱 등급은 공원의 면적 차이와 성립위치 및 인위적 간섭정도의 차이로 인해 남선공원과 함월산은 3등급, 보문산과 염포산은 4등급으로 나타났다. 생물서식공간으로서의 비오톱 기능평가 등급을 분석한 결과, 지역에 관계없이 3~5등급 즉 보통 이하로 나타나, 서식공간의 제공이라는 기능적 역할은 상대적으로 낮게 나타난 것으로 분석되었다.

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친환경 고속도로의 건설 방향 (The Prospects of Highway Road in Consideration of Natural Environment)

  • 전기성;김태수
    • 한국환경복원기술학회지
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    • 제3권3호
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    • pp.105-112
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    • 2000
  • For the purpose of building up the construction prospects of highway in consideration of natural environment. The tree planting and flower seeding in highway road side using native species were offered to natural landscape and resting area landscaping for peoples, and these area were 194place. The tree planting and flower seeding activity is to improve driving circumstances, and to conserve living and natural environment along the highways. And, preparation of ecotone and biotope at the highway surroundings for natural ecosystem conservation is an important activity, and planting of natural plants is generally carried out near wildlife ecoroads in order to give the way for animals. The primary purpose of this tree planting and seeding is not only to reduce environmental pollution, but also to enhance the ecological surroundings of highway circumference. Ultimately, It is essential that the constructive method of highway think over such as ecological environment and road design, surveying and management, construction, highway maintenance etc.

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남산도시자연공원내 생물서식공간 조성에 관한 연구 (A Study of Creating a Biotope in Namsan Urban Natural Park)

  • 강현경;이수동
    • 한국환경복원기술학회지
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    • 제9권2호
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    • pp.45-58
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    • 2006
  • This study was aimed to propose the plan of creating a biotope reflecting an ecological education as well as its function as the habitats of amphibian in Namsan Urban Natural Park in Seoul. There were Cheonil mineral spring area which was located on the southern side of Namsan, wetlands which was already created on the east valley(800$m^2$) and a buffer area of the circumference(1,100$m^2$) as the biotope sites. Major fields of this study include a survey of the staus, a basic plan, a master plan; a survey of this site was focused on topography, water system, existing vegetation, wildbird, amphibian, trail; a detailed plan was focused on flow plan, planting plan, facility plan. Existing vegetation was classified into 8 types; Pinus densiflora forest, Pinus densiflora planted area, Prunus sargentii-Quercus spp. forest, Pinus rigida forest, Robinia pseudoacacia forest, artificial green space, wetlands, south beltway. There were Pinus densiflora planted area and Prunus sargentii-Quercus spp. forest as major vegetations of this site. 14 species and 33 individuals of wildbirds appeared, Rana temporaria ornativentris and Hynobius leechi were investigated in the wetlands.In particular, habitats of amphibian were divided eco-zone, buffer-zone and restore-zone, and habitats and facilities which would be suitable for the characteristics of each space were planned. As a result, environment elements of good habitats including spawn wetlands of amphibian, harbor of amphibian, water plant of wetland, wild shrubs forest, ecological landscape forest, wetland observation trail, fence of wetland protection and ramp by pebble and log were created at the site. The amphibian biotope of Namsan is rated high as an important space for conserving biodiversity. Accordingly, continuous monitoring of this biotope as a urban habitat is required as the environment changes.

충주시 학교외부공간 피복유형에 따른 온열환경 및 생태면적률 비교 (Comparison of Thermal Environment and Biotope Area Rate according to Land Cover Types of Outside Space of School located in Chung-ju)

  • 주진희;반종현;윤용한
    • 한국환경과학회지
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    • 제19권9호
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    • pp.1103-1108
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    • 2010
  • This study was conducted to be used as basic data of environmental friendly construction planning by comparing and analyzing thermal environment, find particles and biotope area rate according to land cover types of outside space of schools located in Chung-ju. When meteorological factors were analyzed according to land cover types, for temperature planting area and paved area showed low-and high-temperature ranges, respectively, and relative humidity was negatively related with temperature as low-and high-temperature ranges corresponded to high-and low-humidity ranges, respectively. For Wet Bulb Globe Temperature Index (WBGT) by land cover types, it was observed to be artificial grass> bare land> natural grass. Find particles were different according to land cover types of playground with being bare land> artificial grass> natural grass in the order. Bare land playground, where there were artificial factors and no absorption of fine particles through stomata of leaves as a function of natural circulation, recorded the highest level of $39.8\;{\mu}g/m^3$ and the level was relatively higher compared to the levels by season in Chung-ju. Biotope area rate showed the order of M elementary school> K elementary school> C commercial high school. That was considered to be caused by the difference of land cover type of school playground accounting for a large part of a school.

초지지붕에서의 시간경과에 따른 식생변화 (Changes in Plant Species on a Grass Roof over Time)

  • 이영무
    • 한국조경학회지
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    • 제34권6호
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    • pp.39-53
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    • 2007
  • Unlike conventional roof landscaping, where various kinds of plants and structures are employed, a grass roof is a roof on which herbaceous plants are grown in planting medium and which is not accessed or maintained, mainly because it doesn't have sufficient load capacity to support a regular roof garden. They are mostly built on existing roofs, whether flat slab or gabled. Planting on roofs has numerous advantages, such as creating a biotope, purifying urban air, adding moisture to the atmosphere, storing rain water, preventing flash floods, reducing energy use for heating and air conditioning, enhancing the urban landscape and providing relaxation to the city dwellers, not to mention the alleviation of global warming by absorbing $CO_2$. In addition to the general merits of roof planting, the grass roof has its own unique qualities. Only herbaceous species are planted on the roof, resulting in light weight which allows roofs of existing buildings to be planted without structural reinforcement. The species chosen are mostly short, tough perennials that don't need to be maintained. These conditions provide an ideal situation where massive planting can be done in urban areas where roofs are often the only and definitely the largest space available to be planted. If roofs are planted on a massive scale they can play a significant role in alleviating global warming, heat island effects and energy shortages. Despite the advantages of grass roofs, there are some problems. The most significant problem is the invasion of neighboring plants. They may be brought in with the planting medium, by birds or by wind. These plants have little aesthetic value comparing to the chosen species and are usually taller. Eventually they dominate and prevail over the original species. The intended planting design disappears and the roof comes to look wild. Since the primary value of a grass roof is ecological, a change in attitude towards what constitutes beauty on the roofscape is necessary. Instead of keeping the roof neat through constant maintenance, people must learn that the wild grass with bird's nests on their roof is more beautiful as it is.