• 한국농림기상학회지
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• 제5권3호
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• pp.158-165
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• 2003

앞으로 건강 기능식품 및 농산촌의 단기 소득자원으로 활용될 수 있는 유망 수종인 마가목에 대한 기초 자료를 제공하고자 우리나라 마가목 천연분포 지역중 지리적으로 내륙과 떨어져 있고 온대습윤 지역에 속하며 사면이 동해와 접해 있어 전형적인 해양성 기후의 특징을 나타내고 있는 울릉도 지역의 마가목 천연림에 대하여 해발고별로 분포 특성을 파악하고 Thornthwaite의 기후학적 방법으로 기상인자를 추정한 결과는 다음과 같다. 1971년부터 2000년까지 울릉도 기상관측소에서 측정된 년 강수량과 추정된 잠재증발산량을 식물의 생육기와 생육휴지기로 구분하여 비교ㆍ분석한 결과, 전자는 년 강수량의 68%에 달하는 수분이 공급되는 반면에 81%의 수분이 증발산에 의하여 소모되는 것으로 추정되며, 후자는 32%의 수분 공급에 비하여 19%만이 소모되는 것으로 나타나 수분수지 측면에서 마가목을 비롯한 다른 수종들의 생육에 많은 도움을 주고 있는 것으로 판단된다. 조사된 자료들을 기초로 울릉도의 해발고별 월평균 기온과 잠재증발산량을 추정하여 비교ㆍ분석한 결과, 해발고도가 증가하면서 전체적인 수분수지 측면에서는 양호한 경향을 나타내는 것으로 판단되며, 주생육 온도범위는 66.8＜W＜95.0, -21.5＜CI＜-7.7인 것으로 분석되어 마가목의 분포와 적지 선정을 하는데 있어서 객관적인 기준이 될 수 있을 것으로 판단된다. 울릉도 마가목 천연집단의 해발고별 분포특성을 파악하기 위해 식생 조사를 실시한 결과 교목층은 총 10종이 출현하였으며, 마가목(46.85), 너도밤나무(13.43), 고로쇠나무(12.41), 피나무(12.03) 등의 순서로 중요치가 높게 나타났고 아교목층에서는 교목층 보다 7종이 더 많은 총 11종이 출현하였으며, 고로쇠나무(13.16), 너도밤나무(12.68), 당단풍나무(11.37), 마가목(10.76) 등의 순서로 높은 중요치를 나타내었다. 이것은 마가목 천연집단 내에서 상당한 수준의 종간경쟁이 이루어지고 있음을 나타내는 결과라고 추정할 수 있으며, 관목층에서도 동일한 경향을 나타내었다. 관목층은 총 25종이 출현하였으며, 조릿대(22.09), 만병초(10.51) 등이 높은 중요치를 나타내는 특징을 보였고 그 다음으로 고로쇠나무(9.83), 너도밤나무(7.84), 마가목(7.08) 등의 순서로 높은 중요치를 나타내고 있었다. 교목층에서는 만병초와 섬벚나무, 푸조나무 아교목층에서는 동백나무, 만병초, 섬벚나무, 섬피나무, 관목층에서는 자금우, 말오줌때, 새비나무, 섬댕강나무, 줄사철나무 등과 같은 특이종도 출현하였다. 본 조사지의 층위 구조별 종다양도(H') 및 균재도 (J')를 분석한 결과, 교목층에서는 0.6199ㆍ0.6199, 아교목층 1.0859ㆍ0.8825, 관목층 1.1390ㆍ0.8148으로 분석되었으며 우점도(1-J')는 대체적으로 낮게 나타나 다수의 종에 의해서 지배됨을 알 수 있었다.

• 한국환경생태학회지
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• 제24권6호
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• pp.751-762
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• 2010

본 연구는 초고층 건축물 외부공간의 식물 피복 상태가 온도변화에 미치는 영향을 파악하고자 서울시에 위치한 초고층 건축물 12개소를 대상으로 연구를 수행하였다. 초고층 건축물 외부공간의 토지 피복 유형별 온도 차이 분석을 위해 6개 유형(외곽도로, 포장지, 관목/초지, 단층교목식재지, 다층식재지, 수경시설)으로 건축물외부공간의 피복유형을 구분하였으며 토지이용유형별 대표지점에서 온도를 실측하였다. 건축물 12개소의 주변 환경차이를 고려하기 위해 외곽도로의 중앙부에 대조구를 선정하여 온도를 측정한 후 일원배치 분산분석을 토대로 유사한 온도경향을 보이는 대상지를 4개 그룹으로 분류하였다. 분류된 그룹의 토지 피복 유형과 외부 공간 온도와의 일원배치 분산분석결과, 주로 단층교목식재지, 수경시설, 다층식재지는 저온역에 속하였으며, 관목/초지, 포장지, 외곽도로는 고온역에 속하였다. 저온역과 고온역의 온도차이는 약 $1.06{\sim}6.17^{\circ}C$의 차이를 보였다. 그러나 조성된 식재지와 수경시설 면적의 협소, 건축물로 인한 일사도달량의 저감과 반사량의 증가 등으로 초고층 건축물 외부공간 온도에 미치는 영향이 다양하게 나타났다. 이에 각 공간에 필요한 녹지량과 수공간의 면적을 조성 전 미리 산출하여, 효과를 발휘할 수 있는 최소한의 면적과 녹지량을 확보할 필요성이 있었다.

• 한국환경복원기술학회지
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• 제7권2호
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• pp.75-86
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• 2004

This study aims to figure out ecological characteristic of natural forests focusing on vegetation as a way of ecological renovation for the restoration of naturalness for golf courses that were constructed in the Country and to present vegetation models and appropriate tree species for the purpose. The study site is P golf club, which is located in Gapyong-gun, Kyeonggi Province. The site is within a forest where the grade from the natural ecology map is the first one and the level from the green index accounts for the eight, thus showing a typical environment for a golf course in terms of location. The location of the site explains a reason for restoration. The major substance of the study is to conduct ecological evaluation of vegetation structures around and inside the golf course and to present a vegetation model. In order to evaluate the ecological characteristics of the vegetation structures, the analysis of the study covered succession stages, multi-layer vegetation structures and species diversity. Plant communities that have high species diversity were selected for the vegetation model and proper density and species were proposed considering the number of species and individuals and distances between trees. The vegetation restoration model targets succession into an oak forest. Within a unit of 100 $m^2$, the recommended model include a tall-tree layer with 11 trees such as Quercus serrata and Quercus mongolica, a sub-tall-tree layer with 12 trees including Quercus mongolica, Quercus serrata, Prunus sargentii, Fraxinus rhynchophylla and Acer pseudo sieboldianum, a shrub layer with 32 trees from 16 species, and a grass layer with a cover rate of 45 %. The proposed vegetation restoration model needs to apply to : 1) damaged natural forests by the construction of golf courses; 2) boundaries between golf courses and surrounding forests; 3) buffer zones; 4) open spaces in between courses; and 5) areas between greens and tees where open spaces are available in a mass. In conclusion, one of the most important factors in presenting a vegetation model for the restoration of naturalness in the golf course and other damaged forests is to provide multi-layer vegetation structures that are composed of native species. As for the specific application for the site, it is recommended to manage the vegetation in such a way that the environment of the site can have a similar environment to the surrounding forest which is expected to succeed into an oaks-dominant one.

• 한국환경복원기술학회지
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• 제6권1호
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• pp.28-33
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• 2003

In this study, we observed air temperature to make clear that land coverage condition and stand form has a certain relationship to air temperature during the night in various green space. And with revolution analysis, we interpreted relationship of air temperature distribution in the green space, The way of analysis is this land coverage rate and air temperature, of number of tree volume of tree air temperature. With this experimental result, we can propose green plan, which is taking into consideration lower effect of air temperature. In this result, lower zone is formed in forest and water area, higher zone is formed in paved surface and barren ground. but this gap is a little. arbor+subarbor area, in the point of water area surrounded stand is formed relative lower air temperature. As a result to make up efficiency lower air temperature area, it is needed to make water area which has surrounded forest, and it is needed to make stand form lower air temperature 2~3 layer forest. In order of arbor, subarbor, shrub, the lower air temperature is more effect.

• The Korean Journal of Ecology
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• 제18권2호
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• pp.243-253
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• 1995

Seral changes in environmental factors and recovery of soil fertility during abandoned field succession after shifting cultivation were investigated in eastern Kangwon-Do, Korea. Relative light intensity of herb and shrub layer decreased gradually until 50 years and increased slightly thereafter. Amount of litter and nutrients derived from it were depicted as a parabola form showing the gradual increment during the first 50 years and slight decrease thereafter. Organic matter, pH value, total-N and Mg of soil were plotted as an early depletion-mid pinnacle form showing the extrems depletion during the first 10 years, abrupt increase in about 20 or 50 years and gradual decrease thereafter. Ca, Al, Mn and Na of soil were depicted as a pinnacle form showing the peak in about 20 or 50 years. Thickness and field capacity of soil increased gradually, but K and total-P did not show any tendency as succession proceeded. The soil fertility, overall capacity of soil nutrients and water for plant growth, was plotted as the early depletion-mid pinnacle form.

• 농촌계획
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• 제17권3호
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• pp.15-25
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• 2011

This paper is to contribute for management and restoration as a basic study of vegetation structure in Aemirang Hill, Nakdongjeongmaek. To verify the characteristics of vegetation structure, we set up 25 plots($100m^2$). The result of community analysis was used by TWINSPAN classification. The communities were classified 7 types i.e. Quercus variabilis community, Quercus mongolica community, Pinus densiflora community, Pinus densiflora-Quercus mongolica community, Q. mongolica-Quercus variabilis community, Quercus mongolica-Betula davurica community, Larix leptolepis community. Pinus densiflora community and Pinus densiflora-Quercus mongolica community are progressively transforming a Quercus mongolica community that is called Pinus densiflora next succession stage. Whereas the communities that has dominant Quercus variabilis and Quercus mongolica did not appear a next generation succession tree such as Carpinus laxiflora, Carpinus cordata in the under story and shrub layer. Therefore, Aemirang Hill's ecological succession was to maintain the status condition. Aemirang Hill's diversity index is 0.5738 to 0.8906. It were analyzed that diversity index was lower than other places.

• The Korean Journal of Ecology
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• 제18권4호
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• pp.451-462
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• 1995

A comparative study on the minimal areas and the community structures in pine IPinus densiflora) and oak (Quercus mongolica) frests was carried out. Basic tools used in the present study were species diversity and classical ayntaxonomy (Z.-M. School) of the phytocoenosis. Total 120 nest-quadrats in 40 stands situated at the syngeographical region of the Lindero-Quercion mongolicae were investigated. Each stand was classified on the basis of species combination, and species abundance was computed with net contribution degree (NCD). Composition ratio of plant-from and rate of actual species diversity (ASD) to syntaxa were computed for better interpretation of the minimal areas. Four syntaxa were structured: Saso-Quercetum mongolicae, Viola albida-Quercus mongolica community, Carex hummilis-Pinus densiflora community and Juniperus rigida-Pinus densiflora community. Their minimal areas were determined as 305, 196, 169, and 81 ㎡, respectively. Aconsistent regularity between species composition ratio and community structure in the multi-layered plant community was hardly found. The minimal areas increased linearly with increasing rate of ASD, and a phytocoenosis developed by diverse arboreta in the understory and shrub-layer should be investigated with larger sampling sizes.

• 한국환경생태학회지
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• 제12권3호
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• pp.279-289
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• 1998

상록활엽수림의 식생구조 변화를 모니터링 하기 위하여 완도수목원에 20개의 고정시험구를 1996년에 설치했다. 20개의 고정시험구는 10개의 시험구와 대조구로 구분했으며, 시험구는 적정밀도로 택벌한 후 상록활엽수를 식재했다. 시험처리전 20개 고정시험구의 식생구조는 붉가시나무, 붉가시나무와 개서어나무, 소나무 등이 우점하였고, 소나무군락과 낙엽활엽수군락에서 붉가시나무군락으로 천이되는 식생구조를 나타냈다. 시험처리시험구는 붉가시나무와 소나무가 우점하는 식생구조로 바뀌었고, 관목층과 지피층의 출현종수, 개체수, 피도 등이 증가하였다.

• Journal of Ecology and Environment
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• 제34권4호
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• pp.347-355
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• 2011

Effects of forest thinning on community level properties have not been understood yet in Korea. We investigated regeneration patterns and trajectories after a disturbance by applying a chronosequence approach. Light availability, litter and woody debris cover, and species composition were determined for twenty 50 m line-transect samples representing a disturbance duration gradient (within 11 years). Environmental factors such as light availability and coverage of woody debris and litter changed abruptly after thinning and then returned to the pre-disturbance state. Although species richness was gained at shrub and ground layer in a limited way in both forests, cover of various functional types revealed diversity in their responses. Notably, Alnus firma stands exhibited a larger increment of cover in woody plants. Ordination analysis revealed different regeneration trajectories between natural and planted stands. Based on ordination analysis, rehabilitated stands showed movement to alternative states compared with natural ones, reflecting lower resilience to perturbation (i.e., lower stability). Our results suggest that community resilience to artificial thinning depends on properties of the dominant species. But to get more explanatory ecological information, longer-term static observations are required.

• 한국환경복원기술학회지
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• 제8권1호
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• pp.17-26
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• 2005

Ecological corridor is the facility to connect two habitats fragmented by roads, dam, housing and industrial area. Critics of faunal corridors have suggested that they are simply an untested application of unproved island biogeography theory. But, everyone agree that ecological corridor is important useful structural components that help animal movement in fragmented landscapes. There are 52 ecological corridors in Korea. We investigated 43 ecological corridors of these and recorded the size of corridor, planting species, management and growth condition. We compared planting species to nearby exiting vegetation species and structure. We found that there are no considerations for many aspects of planting, for example, planting species, structure, animal migration and behavior, surrounding vegetation etc. Expecially, It was ignored management of plants, difference of surrounding vegetation, lacks of diverse planting species and structure. We suggest planting the native species of tall tree, shrub and ground cover, edge planting for transitional space between road and natural habitat, planting for foraging and breeding of target animal, diverse layer vegetation, and open space of center for rapid animal dispersal.