Kim, Seongjun
(Division of Restoration Research, Restoration Center for Endangered Species, National Institute of Ecology)
,
Lee, Chang-Woo
(Division of Restoration Research, Restoration Center for Endangered Species, National Institute of Ecology)
,
Park, Hwan-Joon
(Division of Restoration Research, Restoration Center for Endangered Species, National Institute of Ecology)
,
Lee, Byoung-Doo
(Division of Restoration Research, Restoration Center for Endangered Species, National Institute of Ecology)
,
Hwang, Jung Eun
(Division of Restoration Research, Restoration Center for Endangered Species, National Institute of Ecology)
,
An, Jiae
(Division of Restoration Research, Restoration Center for Endangered Species, National Institute of Ecology)
,
Park, Hyung Bin
(Division of Restoration Research, Restoration Center for Endangered Species, National Institute of Ecology)
,
Baek, Ju Hyeong
(Division of Restoration Research, Restoration Center for Endangered Species, National Institute of Ecology)
,
Kim, Pyoung Beom
(Division of Restoration Research, Restoration Center for Endangered Species, National Institute of Ecology)
,
Kim, Nam Young
(Division of Restora)
The present study aimed to clarify flora living at the area of Restoration Center for Endangered Species in Yeongyang, Gyeongbuk Province. In May, August, and September 2019 and in May and July 2020, all of vascular plants were recorded, and endangered, Korea endemic, and exotic plant species were f...
The present study aimed to clarify flora living at the area of Restoration Center for Endangered Species in Yeongyang, Gyeongbuk Province. In May, August, and September 2019 and in May and July 2020, all of vascular plants were recorded, and endangered, Korea endemic, and exotic plant species were further identified. The study site contained a total of 418 floral taxa (98 families, 261 genera, 384 species, 4 subspecies, 27 variations, and 3 formations), in which Magnoliophyta accounted for larger proportion (95.2%) than Pteridophyta (3.6%) and Pinophyta (1.2%). In addition, 1 endangered (Cypripedium macranthos Sw.) and 5 Korea endemic species (Aconitum pseudolaeve Nakai, Eleutherococcus divaricatus var. chiisanensis [Nakai] C.H. Kim & B.-Y. Sun, Lonicera subsessilis Rehder, Paulownia coreana Uyeki, and Weigela subsessilis [Nakai] L.H. Bailey) were detected. The number of exotic species was 33, consisting of 4 invasive-exotic, 4 potentially invasive-exotic, and 25 non-invasive species. Compared to a previous assessment before the establishment of the center (in 2014), there were increases in total floral taxa (from 361 to 418), endangered species (from 0 to 1), and exotic species (from 26 to 33). These results possibly reflect temporal changes in floral community, which should be confirmed through subsequent long term monitoring.
The present study aimed to clarify flora living at the area of Restoration Center for Endangered Species in Yeongyang, Gyeongbuk Province. In May, August, and September 2019 and in May and July 2020, all of vascular plants were recorded, and endangered, Korea endemic, and exotic plant species were further identified. The study site contained a total of 418 floral taxa (98 families, 261 genera, 384 species, 4 subspecies, 27 variations, and 3 formations), in which Magnoliophyta accounted for larger proportion (95.2%) than Pteridophyta (3.6%) and Pinophyta (1.2%). In addition, 1 endangered (Cypripedium macranthos Sw.) and 5 Korea endemic species (Aconitum pseudolaeve Nakai, Eleutherococcus divaricatus var. chiisanensis [Nakai] C.H. Kim & B.-Y. Sun, Lonicera subsessilis Rehder, Paulownia coreana Uyeki, and Weigela subsessilis [Nakai] L.H. Bailey) were detected. The number of exotic species was 33, consisting of 4 invasive-exotic, 4 potentially invasive-exotic, and 25 non-invasive species. Compared to a previous assessment before the establishment of the center (in 2014), there were increases in total floral taxa (from 361 to 418), endangered species (from 0 to 1), and exotic species (from 26 to 33). These results possibly reflect temporal changes in floral community, which should be confirmed through subsequent long term monitoring.
* AI 자동 식별 결과로 적합하지 않은 문장이 있을 수 있으니, 이용에 유의하시기 바랍니다.
제안 방법
Vascular plants were investigated in May, August, and September 2019 and in May and July 2020. The field survey was based on the line transect method (Braun- Blanquet, 1964), which targeted on the area of Restoration Center for Endangered Species.
대상 데이터
Study site covered overall area of Restoration Center for Endangered Species (255 ha) in Yeongyang (N36°38'10.30 E129°09'13.69), which was located at the northeastern part of Gyeongbuk Province (Fig. 1). Topographically, approximately 77% of the site area were mountainous (slope >15°), but there were plain and stream inside as well.
There were 418 floral taxa (98 families, 261 genera, 384 species, 4 subspecies, 27 variations, and 3 formations) in the study site (Table 1). Magnoliophyta occupied the largest proportion (95.
이론/모형
2019 and in May and July 2020. The field survey was based on the line transect method (Braun- Blanquet, 1964), which targeted on the area of Restoration Center for Endangered Species. Any vascular plants were identified in the field using the characteristics of organs (e.
성능/효과
2%). The dominant families within Magnoliophyta were Asteraceae (51 taxa), Fabaceae (25 taxa), Rosaceae (25 taxa), Poaceae (24 taxa), Liliaceae (17 taxa), and Lamiaceae (16 taxa), while the dominant genera within Magnoliophyta were Artemisia (9 taxa), Carex (8 taxa), Persicaria (8 taxa), Viola (8 taxa), Dioscorea (6 taxa), and Quercus (6 taxa). On the other hand, the dominant family and genus within Pinophyta were Pinaceae (4 taxa) and Pinus (2 taxa), whereas those within Pteridophyta were Dryopteridaceae (4 taxa) and Dryopteris (4 taxa).
species (Table 3). The invasive-exotic species consisted of 3 North American species (Ambrosia artemisiifolia L., Ambrosia trifida L., and Aster pilosus Willd.) and 1 European species (Lactuca scariola L.). The potentially invasive-exotic species contained 2 North American species (Amorpha fruticosa L.
). The potentially invasive-exotic species contained 2 North American species (Amorpha fruticosa L. and Bidens frondosa L.), 1 European species (Festuca arundinacea Schreb.), and 1 Eurasian species (Rumex obtusifolius L.). These species were either herbaceous weeds living along road- and stream side (A.
후속연구
, 2015). As C. macranthos has been unreported around the study site until the present study, detailed investigations should be necessary to ensure whether that species habituate in the surrounding area of Restoration Center for Endangered Species.
, 2016). Given that the present study covered a relatively short period of time, this aspect should be confirmed through further monitoring in the long-term.
참고문헌 (23)
Beon, M.S., Oh, H.K., Kim, Y.H., and Kim, Y. (2005). Vascular plants and urbanization index in the Jeoniu stream area. Korean Journal of Environment and Ecology, 19, 231-245.
Braun-Blanquet, J. (1964). [Pflanzensoziologie: grundzuge der Vegetationskunde], 3rd ed. Vienna: Springer.
Chapin, F., McFarland, J., McGuire, A., Euskirchen, E., Ruess, R., and Kielland, K. (2009). The changing global carbon cycle: linking plant-soil carbon dynamics to global consequences. Journal of Ecology, 97, 840-850.
Chung, G.Y., Jeong, H.J., Nam, G.H., and Park, J.H. (2005). Flora of vascular plants in Irwolsan of Gyeongbuk. Korean Journal of Plant Resources, 18, 131-147.
Chung, G.Y., Yu, B.C., Jeong, H.J., Park, M.S., Lee, S.H., Choi, H.N., et al. (2007). Distribution of vascular plants in Geommasan (Yeongyang, Gyeongbuk). Korean Journal of Plant Resources, 20, 281-291.
Chung, G.Y., Park, M.S., Jung, S.Y., Lee, S.H., Choi, H.N., Nam, B.M., et al. (2008). Distribution of vascular plants in Podosan (Yeongyang, Gyeongbuk). Korean Journal of Plant Resources, 21, 281-291.
De Martis, G., Mulas, B., Malavasi, V., and Marignani, M. (2016). Can artificial ecosystems enhance local biodiversity? The case of a constructed wetland in a Mediterranean urban context. Environmental Management, 57, 1088-1097.
Kim, Y.H., Kil, J.H., Hwang, S.M., and Lee, C.W. (2013). Spreading and distribution of Lactuca scariola, invasive alien plant, by habitat types in Korea. Weed & Turfgrass Science, 2, 138-151.
Korean Ministry of Environment. (2014a). Environmental risk assessment for the construction of the national Restoration Center for Endangered Species, Sejong: Ministry of Environment.
Korean Ministry of Environment. (2014b). A study on long-term management of exotic species, Sejong: Ministry of Environment.
Lee, C.B. (2003). Coloured flora of Korea, Seoul: Hyangmunsa.
Lee, J.H., Bae, K.H., and Cho, H.J. (2006). Forest vegetation classification and species composition of Mt. Ilwol, Yeongyang-Gun, Korea. Korean Journal of Agricultural and Forest Meteorology, 8, 132-140.
Lee, S.H., Kim, S., and Kim, H.J. (2018). Effects of thinning intensity on understory vegetation in Chamaecyparis obtusa stands in South Korea. Forest Science and Technology, 14, 7-15.
Mora, C., Tittensor, D.P., Adl, S., Simpson, A.G., and Worm, B. (2011). How many species are there on Earth and in the ocean? PLoS Biology, 9, e1001127.
Numata, M., and Kotaki, O. (1975). [Naturalized plants], Tokyo: Japan Society of Library.
Oh, H.K., Sagong, J.H., and You, J.H. (2011). Analysis on environmental indices and naturalized plants distributed in Gyeryong-si, Korea. Korean Journal of Environment and Ecology, 25, 479-489.
Oh, H.K., Son, B.Y., and You, J.H. (2015). Vascular plants and characteristics by type in Mt. Ilwolsan (Yeongyang, Gyeong buk) for designating an ecological and landscape conservation area. Journal of the Korean Society of Environmental Restoration Technology, 18, 43-62.
Onaindia, M., Dominguez, I., Albizu, I., Garbisu, C., and Amezaga, I. (2004). Vegetation diversity and vertical structure as indicators of forest disturbance. Forest Ecology and Management, 195, 341-354.
Shanmugam, S.G., and Kingery, W.L. (2018). Changes in soil microbial community structure in relation to plant succession and soil properties during 4000 years of pedogenesis. European Journal of Soil Biology, 88, 80-88.
Wurzburger, N., and Hendrick, R.L. (2009). Plant litter chemistry and mycorrhizal roots promote a nitrogen feedback in a temperate forest. Journal of Ecology, 97, 528-536.
Yim, Y.J., and Jeon, E.S. (1980). Distribution of naturalized plants in the Korean Peninsula. Korean Journal of Botany, 23, 69-83.
Yirga, F., Marie, M., Kassa, S., and Haile, M. (2019). Impact of altitude and anthropogenic disturbance on plant species composition, diversity, and structure at the Wof-Washa highlands of Ethiopia. Heliyon, 5, e02284.
※ AI-Helper는 부적절한 답변을 할 수 있습니다.