• 제목/요약/키워드: ARTIFICIAL VEGETATION

검색결과 329건 처리시간 0.034초

인공식재에 의해 교란된 산림의 식생구조 및 생태적 복원기법 (Vegetation Structure and Ecological Restoration of Disturbed Forest due to Artificial Plant)

  • 배병호;윤용한;김정호
    • 한국환경과학회지
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    • 제20권6호
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    • pp.701-710
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    • 2011
  • The purpose of this study is to investigate the vegetation structure and ecological restoration of disturbed forest due to artificial plant. To this end, 12 plots were set up and surveyed. The result analyzed considering mean importance percentage(M.I.P) showed that the types were divided into three groups which are artificial planted forest type(three plots), natural forest-artificial planted forest type(four plots), natural forest type(five plots). Dominant proportion of artificial planted species were as follows: artificial planted forest type was over 60%, natural forest-artificial planted forest types were 14~49%. The range of Shannon's index of all associations was from 0.7131 to 0.7771(natural forest-artificial planted forest > natural forest > artificial planted forest). Also we suggested restoration method of vegetation for ecological value as follow: Control of density considering step and Remove of Pinus koraiensis seedlings of understory layer and shurb layer.

인천광역시 산지형 도시녹지의 식생구조 및 관리계획: 육지지역을 중심으로 (Vegetation Structure and Management Planning of Mountain Type Urban Green Space in Inchon, Korea : a case study of land area)

  • 조우
    • 한국조경학회지
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    • 제26권2호
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    • pp.15-27
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    • 1998
  • The purposes of this study were to investigate vegetation structure and present management planning of mountain type green space using the green space changes during the 20 years, actual vegetation, and plant community structure in land area of Inchon, Korea. The actual vegetation area in survey sites was consisted of Quercus acutissima community, Robinia pseudoacacia forest, Pinus rigida forest, Q. mongolica-Pinus rigida community, P. rigida-Q. mongolica community, Q. monogolica community and so on. According to the classification by TWINSPAN, 61 survey plots were divided into 9 groups; Q. mongolica-Alnus japonica-R. pseudoacacia-P. densiflora, R. pseudoacacia-Styrax japonica, P. rigida-R. pseudoacacia-Q. mongolica, R. pseudoacacia-P. rigida-Q. mongolica-A. hirusta, Q. mongolica-P. thunbergii, and prunus sargentii-Zelkova serrata community. From this result, ecological succession trend of vegetation seems to be change from artificial result, ecological succession trend of vegetation seems to be change from artificial planting forest to native plant community which was dominated by Quercus spp.. This study area need to manage for the increase of biodiversity through the restoration of naturalness by ecological management of artificial planting forest and ecological planting of injured green space.

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위성영상을 이용한 산불피해 이후 자연복원과 인공복원 방법에 따른 식생회복 모니터링 (Monitoring of Vegetation Recovery According to Natural and Artificial Restoration Methods After Forest Fire Damage Using Satellite Imagery)

  • 황영인;강원석;박기형;이경철;한상균;권형근
    • 현장농수산연구지
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    • 제24권3호
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    • pp.33-43
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    • 2022
  • This study was conducted to monitor the vegetation recovery in the areas damaged by the forest fires on the east coast that occurred in April 2000. The study site was a forest fire-damaged area in Samcheok-si, Gangwon-do, and 21 monitoring areas (12 natural restoration sites, 9 artificial restoration sites) were selected to analyze the vegetation recovery trend since 1998. The vegetation recovery trend was compared by calculating the values according to the year using the difference Normalized Burn Ratio (dNBR) and Normalized Difference Vegetation Index (NDVI) based on satellite images (Landsat TM/ETM+ and Sentinel-2A). As the result of this study, all 21 sites, vegetation was recovered, and both groups showed the greatest recovery in summer. In the case of the dNBR, the artificial restored sites showed higher values than the natural restored sites, and in the case of the NDVI, the natural restored sites were higher than the artificially restored sites in summer and autumn. However, the difference between the two groups of natural and artificial restoration sites was not significant. Therefore, the direction of forest restoration after forest fire damage can be effectively restored if properly implemented for the purpose of restoration of the target site.

조성 후 15년이 경과한 인공습지의 식물상과 식생구조 (Flora and Vegetation Structure in a 15-Year-Old Artificial Wetland)

  • 손덕주;이효혜미;이은주;조강현;권동민
    • Ecology and Resilient Infrastructure
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    • 제2권1호
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    • pp.54-63
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    • 2015
  • 본 연구에서는 충북 진천에 위치한 총 면적 $3,000m^2$ 인 수질정화용 인공습지에서 조성 15년 후의 식물상과 식생구조를 파악하였다. 이곳 인공습지에서는 총 93종의 식물종이 출현하였고, 절대습지식물과 임의습지식물의 비율이 40%, 절대육상식물과 임의육상식물의 비율은 57%로 나타나 천이에 의하여 인공습지가 점차 육상화되었음을 확인할 수 있었다. 천이가 진행됨에 따라 천이 선구자 종인 1, 2년생 식물보다 다년생 식물의 종수 비율이 높아졌다. DCA (detrended correspondence analysis) 결과, 습지 군집 구조를 결정하는 중요한 환경요인은 수심이었다. 군집별 종다양성은 노랑꽃창포 군집, 벌개미취 군집 등의 육상화된 군집에서 높았다. 식물 군집별 습지지수는 벌개미취 군집은 육상, 삿갓사초 및 노랑꽃창포 군집은 임의습지, 노랑어리연꽃, 수련, 갈대, 새우가래 및 애기부들 군집은 절대습지로 나타났다. 결론적으로 인공습지에서는 천이에 의하여 식물 군집의 육상화가 진행되므로 퇴적과 수문 체계를 지속적으로 관리하여 습지식생을 유지할 필요가 있을 것으로 판단되었다.

산불발생 후 소나무 피해 및 식생복원 실태분석 (Mortality in Pine Stand and Vegetation Recovery after Forest Fire)

  • 이시영;전계원;이명욱;전근우
    • 한국방재학회 논문집
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    • 제8권1호
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    • pp.71-79
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    • 2008
  • 산불피해 임지의 식생복원 정도 및 문제점을 파악하기 위하여 산불발생 후 임목피해, 식생회복력 등의 조사 연구를 수행하였다. 소나무 고사율은 수간 및 수관의 피해흔적이 심할수록 피해율이 높았다. 산불피해지에 있어서 수관화에 의해 임분이 전소되는 피해를 받은 지역에서의 식생회복은 대부분이 매토종자 및 맹아에 의한 식생의 회복이 진행되었다. 식생회복과 복원력은 전생 임분의 식생상태와 토심에 따라서 차이가 나타났다. 인공복원의 경우 자작나무 조림지의 경우에는 병충해에 의한 피해가 발생하기도 하였다. 소나무, 해송 조림지의 경우 입지에 따른 생장차이 보다는 조사지내 개체목간의 생장차이가 다소 나타났다.

남산의 생태학적 진단 (Ecological Diagnosis on Mt. nam in Seoul, Korea)

  • 이창석;문정숙;김재은;조현제;이남주
    • The Korean Journal of Ecology
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    • 제21권5_3호
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    • pp.713-721
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    • 1998
  • The effects of artificial interference on the vegetation landscape in Mt. Nam of Seoul, Korea were clarified by analysing the distribution of vegetation landscape element and the number and size of patch depicted as a vegetation map in terms of landscape ecological principles. The effects of artificial interference on vegetation were also confirmed from the environmental gradient analysis on plant community extended from the lowland to the peak of that mountain. Vegetation landscape elements were divided into plantation and secondary forest in actual vegtation map. The ratio of plantation to secondary forest was higher in the lowland below mid-slope and the southern slope. Most afforested land were occupied by Robinia pseudoacacia and Populus tomentoglandulosa, Pinus rigida, P. koraiensis, Metasequoia glyptostroboides, Alnus hirsuta and so on are localy planted. In addition, projects to replace those afforested trees by P. densiflora as a kind of campaign for "Restoration of the one original feature of Mt. Nam" or to replace those tree species by planting young Abies holophylla or P. koraiensis under the mature afforested trees are also carried out in recent years. In cases of secondary forest, the southern slope was dominated by P. densiflora and the northern one by Q. mongolica. But the lowland of the northern slope is dominated by P. densiflora as the same as that in the southern slope. Vegetation landscape elements in Mt. Nam were much simplified comparing with that of suburban area around Seoul. The number of patches, which reflects the degree of diverse artificial interference was more in the lower area than in the upper area and more in the southern slope than in the northern one. On the other hand, the size of patch showed the antagonistic tendency to that of the number of patch. As a result of environmental gradient analysis, vegetation distribution in Mt. Nam was different from that in suburban area around Seoul. For example, Alnus japonica community, Zelkova serrata community, and Carpinus laxiflora community, which is established in mountain comparatively rare in artificial interference disappeared in Mt. Nam. As a result of analysis on vegetational succession in P. densiflora community and Q. mongolica community, both communities showed a tendency of retrogressive succession differently from that in control site located in suburban area around Seoul. In addition, species composition of P. densiflora and Q. mongolica communities in Mt. Nam were also different from those in Mt. Surak located around Seoul. It was interpreted that those results were originated from the environmental pollution and excessive arti ficial interferences.rferences.

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Estimation of Plant Seed Dispersal through Artificial Soil Movement in Incheon Urban Area

  • Kim, Kee-Dae
    • 환경생물
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    • 제21권2호
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    • pp.181-188
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    • 2003
  • In this study, soil seed and bud bank analysis were performed to abbess the mass of potential vegetation in soils less than 1 year old after covered and estimate the amount of seed bank transport through construction in urban area. The ratio of exotic species number to total species number in study sites and the landfill control site was 0.29 and 0.39, respectively. All plots pooled, mean species number and total mean seedling density per $\m^2$ in the top 10 cm of soil was 11$\pm$0 (average$\pm$S.E.) and 8037$\pm$221.Total plant seeds by artificial soil trasnsfer were estimated to be 53 thousand million $m^{-2}yr^{-1}$ in 10 cm soil depth. It reveals that soil transfer accelerates seeds and vegetation movement and makes urban vegetation mixed and common.

Comparison of vegetation recovery according to the forest restoration technique using the satellite imagery: focus on the Goseong (1996) and East Coast (2000) forest fire

  • Yeongin Hwang;Hyeongkeun Kweon;Wonseok Kang;Joon-Woo Lee;Semyung Kwon;Yugyeong Jung;Jeonghyeon Bae;Kyeongcheol Lee;Yoonjin Sim
    • 농업과학연구
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    • 제50권3호
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    • pp.555-567
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    • 2023
  • This study was conducted to compare the level of vegetation recovery based on the forest restoration techniques (natural restoration and artificial restoration) determined using the satellite imagery that targeted forest fire damaged areas in Goseong-gun, Gangwon-do. The study site included the area affected by the Goseong forest fire (1996) and the East Coast forest fire (2000). We conducted a time-series analysis of satellite imagery on the natural restoration sites (19 sites) and artificial restoration sites (12 sites) that were created after the forest fire in 1996. In the analysis of satellite imagery, the difference normalized burn ratio (dNBR) and normalized difference vegetation index (NDVI) were calculated to compare the level of vegetation recovery between the two groups. We discovered that vegetation was restored at all of the study sites (31 locations). The satellite image-based analysis showed that the artificial restoration sites were relatively better than the natural restoration sites, but there was no statistically significant difference between the two groups (p > 0.05). Therefore, it is necessary to select a restoration technique that can achieve the goal of forest restoration, taking the topography and environment of the target site into account. We also believe that in the future, accurate diagnosis and analysis of the vegetation will be necessary through a field survey of the forest fire-damaged sites.

편백림의 식생구조 특성 분석 (Characteristics of Vegetation Structure in Chamaecyparis Obtusa Stands)

  • 박석곤;강현미
    • 한국환경생태학회지
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    • 제29권6호
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    • pp.907-916
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    • 2015
  • 본 연구에서는 인공조림된 편백림을 대상으로 식생구조 및 식생천이, 종다양성의 특성을 밝히고자 전남지역의 8곳에 편백림을 대상으로 식생조사를 실시하였다. 이 식생조사 데이터를 활용하여 군집분석 및 서열분석을 실시한 결과 5개 군락으로 단순화되었다. 군락I은 다른 군락에 비해 종다양성지수가 상당히 낮았는데 이는 교목층에 우점한 편백의 수관이 울폐되어 하층식생이 발달하지 않았거나 잡초목(경쟁 자생수종) 제거로 하층식생이 거의 남아있지 않았기 때문이었다. 반면, 군락 II~IV는 하층에 다양한 자생수종이 유입되어 아교목층과 관목층에서 서로 경쟁하여 어느 정도 안정되거나 식생발달 초기라서 종다양성지수가 높은 편이었다. 마지막, 군락 V는 휴양림으로서 이용강도가 높아 식생구조가 단순하였다. 또한, 임상에 유입되는 광합성유효광과 출현종수 종다양성지수 사이에는 정의 상관관계를 보였다. 이러한 편백림의 식생구조 특성은 과거 개벌 이후 묘목심기, 솎아베기, 풀베기 등의 산림시업과 밀접하게 관련된다. 편백림의 산림시업에 의한 교란빈도와 함께 식생천이프로세스 회전시간에 따라 군락별 식생구조와 종다양성은 약간의 차이를 보였지만, 천연림에 비해 편백림은 단순한 식생구조를 보였다. 인공림은 생물다양성이 낮고 생태계 서비스가 취약하기 때문에 공익적 기능을 발휘할 수 있는 인공림으로 전환하는 한 가지 수단으로써 생태적 관리가 필요할 것이다.

도시 내 습지의 식생구조 변화 모니터링 (Monitoring Vegetation Structure Changes in Urban Wetlands)

  • 김나영;남종민;이경연;이근호;송영근
    • 한국환경복원기술학회지
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    • 제26권6호
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    • pp.135-154
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    • 2023
  • Urban wetlands provide various ecosystem services and are subject to restoration and creation projects due to their increased value in the context of climate change. However, the vegetation structure of wetlands is sensitive to environmental changes, including artificial disturbances, and requires continuous maintenance. In this study, we conducted a vegetation survey of three wetlands created as part of a project to restore urban degraded natural ecosystems and monitored the quantitative changes in wetland vegetation structure using an unmanned aerial vehicle. The vegetation survey revealed 73 species in Incheon Yeonhui wetland, and the change in vegetation composition based on wetland occurrence frequency was 11.5% on average compared to the 2018 vegetation survey results. The vegetation survey identified 44 species in Busan Igidae wetland, and the proportion of species classified as obligate upland plants was the highest at 48.8% among all plants, while the proportion of naturalized plants accounted for 15.9% of all plants. The open water surface area decreased from 10% in May 2019 to 6.7% in May 2020. Iksan Sorasan wetland was surveyed and 44 species were confirmed, and it was found that the proportion of facultative wetland plant decreased compared to the 2018 vegetation survey results, and the open water surface area increased from 0.4% in May 2019 to 4.1% in May 2020. The results of this study showed that wetlands with low artificial management intensity exhibited a tendency for stabilization of vegetation structure, with a decrease in the proportion of plants with high wetland occurrence frequency and a relatively small number of new species. Wetlands with high artificial management intensity required specific management, as they had a large change in vegetation structure and a partially high possibility of new invasion. We reaffirmed the importance of continuous monitoring of vegetation communities and infrastructure for wetlands considering the function and use of urban wetlands, and restoration stages. These research results suggest the need to establish a sustainable wetland maintenance system through the establishment of long-term maintenance goals and monitoring methods that consider the environmental conditions and vegetation composition of wetlands.