Journal of the Korean Society of Environmental Restoration Technology (한국환경복원기술학회지)
- Volume 8 Issue 6
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- Pages.69-79
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- 2005
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- 1229-3032(pISSN)
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- 2733-5011(eISSN)
Vegetation Structure and Succession of Highway Cutting-slope Area
고속도로 절토비탈면의 식생구조와 천이
- Song, Hokyung (Department of Forest Resources, Chungnam National University) ;
- Jeon, Giseong (Korea Highway Corporation, Highway & Transportation Technology Institute) ;
- Lee, Sanghwa (Department of Forest Resources, Graduate School, Chungnam National University) ;
- Kim, Namchoon (Department of Landscape Architecture, Dankook University) ;
- Park, Gwansoo (Department of Forest Resources, Chungnam National University) ;
- Lee, Byungjun (Major in Environment Landscape Architecture, Graduate School, Dankook University)
- 송호경 (충남대학교 산림자원학과) ;
- 전기성 (한국도로공사 도로교통기술원) ;
- 이상화 (충남대학교 대학원 산림자원학과) ;
- 김남춘 (단국대학교 환경조경학과) ;
- 박관수 (충남대학교 산림자원학과) ;
- 이병준 (단국대학교 대학원 생명자원과학과)
- Received : 2005.10.24
- Published : 2005.12.30
Abstract
This study was carried out to select proper species for early stage replantation in highway cut-slope area. In highway cut-slope area, sample plots of 106 were selected, and their vegetations and environmental factors were investigated. 1. We found total 172 species in the 106 cutting area of highway. The species of high frequency of highway cut-slope were found in the order of Lespedeza bicolor, Artemisia princeps var. orientalis, Festuca arundinacea, Erigeron annuus, Lespedeza cuneata, Lactuca indica var. laciniata, Eragrostis curvula, Dactylis glomerata, Oenothera lamarckiana, Wistaria floribunda, Humulus japonica, Commelina communis, Miscanthus sinensis, Pueraria thunbergiana, Pinus densiflora, etc. 2. The average vegetation coverage was over 90% in the study sites and the average coverage was 91.4% in the total cut-slope area. The species of high coverage of highway cut-slope area were found in the order of Festuca arundinacea, Eragrostis curvula, Lespedeza bicolor, Wistaria floribunda, Lespedeza cuneata, Dactylis glomerata, Artemisia princeps var. orientalis, Humulus japonica, Pueraria thunbergiana, Robinia pseudoacacia, Poa pratensis, Medicago sativa, Festuca ovina, Pinus densiflora, Parthenocissua tricuspidata, etc. 3. The total coverage in the foreign plants of Festuca arundinacea, Eragrostis curvula, Dactylis glomerata, Poa pratensis, Medicago sativa, Coreopsis drummondii and native plants of Lespedeza bicolor, Wistaria floribunda, Lespedeza cuneata, Amorpha fruticosa, Indigofera pseudotinctoria, Lespedeza cyrtobotrya were 57.52%. That is, the ecological succession of native herbs and parachute shrubs have delayed because the afforested plants occupy 57.52%. In future, the coverage of foreign herbs have to reduce, and the coverage of the native herbs and parachute shrubs must be increased. 4. The native seed of Artemisia sp., Miscanthus sinensis, Smilax china, Pueraria thunbergiana, Rubus crataegifolius, Rubus parvifolius, Pinus densiflora, Rhus chinensis, Albizzia julibrissin, Rhododendron mucronulatum, Clematis apiifolia, Zanthoxylum schinifolium, Prunus sargentii could be added in the seedling of the temperate south zone highway with the used seeds. The native seed of Artemisia sp., Miscanthus sinensis, Rubus crataegifolius, Rhododendron mucronulatum, Weigela subsessilis, Stephanandra incisa, Rhus chinensis, Pinus densiflora, Salix koreensis, Cocculus trilobus, Populus alba, Spiraea prunifolia for. simpliciflora, Clematis apiifolia, Lindera obtusiloba, Quercus serrata, etc., could be added in the seedling of the temperate middle zone highway with the used seeds. 5. We have some recommendation. The native plants have to growth in the highway cut-slope area instead of foreign plants to have good environmental ecology. The role of the foreign plants should be the plant for the initial several years in the highway cut-slope area. And, the native plants should growth in the next season. 6. We should protect shrubs and trees in the highway slope area because shrubs and trees can be more helpful in stabilizing of the slope area than herbs.