http://chineseinput.net/에서 pinyin(병음)방식으로 중국어를 변환할 수 있습니다.
변환된 중국어를 복사하여 사용하시면 됩니다.
- 中文 을 입력하시려면 zhongwen을 입력하시고 space를누르시면됩니다.
- 北京 을 입력하시려면 beijing을 입력하시고 space를 누르시면 됩니다.
RISS 인기검색어
- 검색키워드
- 저자 : 설정욱 ( Jeong Wook Seol ) (검색결과 4 건)
- 무료
- 기관 내 무료
- 유료
-
권영수,전세근,설정욱,김임규,Kwon, Young Soo,Jeon, Se Kun,Seol, Jeong Wook,Kim, Im Gyu 강원대학교 산림과학연구소 2012 Journal of Forest Science Vol.28 No.4
This study was conducted from April 2012 to June 2012 to analyze breeding status of Black woodpeckers (Dryocopus martius) in the Gayasan National Park. Nest height, tree diameter which a nest built and altitude at the nest site of Black woodpeckers were 17.4 m, 63.8 cm and 587 m, respectively. A pair of Black woodpeckers completed a clutch in 4 eggs on 7 May and 3 of eggs hatched on 24 May 2012. Both female and male incubated eggs and never left eggs without one of parents. A male more contributed to build a nest than a female. Incubation duration was higher in a male than in a female. Nestlings made a begging call in a nest during the growing period. Begging frequency of nestlings increased from 11 days up to 20 days after hatching. After then, nestlings reduced begging and fledged a nest 24 days after hatching. This study provided information of breeding ecology to protect and manage population of Black woodpeckers which are endangered species in South Korea.
-
-
유주한 ( Ju Han You ),전세근 ( Se Kun Jeon ),설정욱 ( Jeong Wook Seol ) 한국환경복원기술학회 2013 한국환경복원기술학회지 Vol.16 No.1
This study is to offer the raw data for conservation and restoration of national park by surveying and analysing the vascular plants in the Gayasan national park. The flora were summarized as 102 families, 328 genera, 469 species, 4 subspecies, 59 varieties and 9 forms. The endangered plants designated by Ministry of Environment were 2 taxa; Pedicularis hallaisanensis Hurus. and Gymnadenia conopsea for. albiflora Y.N.Lee. The rare plants designated by Korea Forest service were 13taxa; crypsinus hastanus (Thunb.) Copel Ligusticum tachiroei (Franch.& Sav.) M. Hiroe & constance, primula modesta var fauriae (Franch.)Takeda, Lilum distichum Nakai ex Kamibay and so forth. The Korean endemic plants were 15taxa; Betula ermanii Cham., Carpinus laxiflora (siebold& Zucc.) Blume, stewartia peseudocamellia Maxim., Galium koreanum (Nakai) Nakai, Heloniopsis koreana Fuse, N.S.Lee&M.N Tamura and so forth, The Pecific plants by floristic region were 66taxa; Betula chinensis heracleifolia Kom, Adoxa moshatekkina L. and so forth. The plants with approval for delivering oversea were 22taxa; salix hallaisanensis H.Lev, sanguisoba argutidens Nakai, Viola albida Palib, Weigela subsessilos(Nakai) L,H.Bailey and so forth. The naturalized plants were 30taxa; Chenopodium album :, Lepidium apetalum WIlld., Trifolium pretense L, Bidens frondosa L, Helianthus tuberosus L. and so forth.
-
유주한(Ju-Han You),문성주(Sung-Ju Mun),정철운(Chul-Un Chung),설정욱(Jeong-Wook Seol) 국립공원연구원 2011 국립공원연구지 Vol.2 No.3
본 연구는 산철쭉과 가시오갈피 특별보호구에 대한 생태적 특성을 분석하여 자생지의 보전과 복원을 위한 기초자료 제공에 그 목적이 있다. 연구결과를 요약하면 다음과 같다. 7개 특별보호구 내외부의 식물상은 58과 103속 122종 1아종 16변종 3품종 등 총 142분류군이 확인되었다. 층위별 우점종 분석 결과, 교목층은 갈참나무(1번·2번·3번 조사구), 졸참나무(4번 조사구), 까치박달(5번 조사구), 느티나무(6번 조사구), 물박달나무(7번 조사구), 아교목층의 경우 굴참나무(1번 조사구), 갈참나무(3번·6번 조사구), 굴피나무(4번 조사구), 물푸레나무와 산벚나무(7번 조사구)로 나타났다. 관목 1층의 우점종은 느릅나무(1번 조사구), 회잎나무(2번 조사구), 산뽕나무와 덜꿩나무(3번 조사구), 신나무(4번 조사구), 생강나무(6번 조사구), 개암나무와 신갈나무(7번 조사구)이며, 관목 2층은 국수나무(1번 조사구), 생강나무(2번 조사구), 조록싸리(3번·4번 조사구), 고광나무(5번 조사구), 고추나무와 줄딸기(6번 조사구), 생강나무·노린재나무, 가시오갈피(7번 조사구)로 나타났다. 초본층의 우점종은 쑥과 돌콩(1번 조사구), 담쟁이덩굴·산새콩·대사초(2번 조사구), 맑은대쑥·김의털·털대사초(3번 조사구), 김의털(4번 조사구), 산새콩·멸가치·주름조개풀(5번 조사구), 주름조개풀(6번 조사구), 오미자(7번 조사구)로 나타났다. The purpose of this study is to offer the raw data for conserving and restoring habitats by analysing the ecological characteristics about special protected area of Rhododendron yedoense var. poukhanense (H.Lév) Sugim. and Eleutherococcus senticosus (Rupr.&Maxim.) Maxim. The results are as follows. The numbers of vascular plants surveyed inside and outside were 142 taxa; 58 families, 103 genera, 122 species, 1 subspecies, 16 varieties and 3 forma. The dominant species of tree layer were Quercus aliena(plot 1·2·3), Quercus serrata(plot 4), Carpinus cordata(plot 5), Zelkova serrata(plot 6) and Betula davurica(plot 7). The dominant species of subtree layer were Quercus variabilis(plot 1), Quercus aliena(plot 3·6), Platycarya strobilacea(plot 4), Fraxinus rhynchophylla·Prunus sargentii(plot 7). The dominant species of shrub first layer were Ulmus davidiana var. japonica(plot 1), Euonymus alatus for. ciliatodentatusa(plot 2), Morus bombycis·Viburnum erosum(plot 3), Acer pictum subsp. mono(plot 4), Lindera obtusiloba(plot 6) and Corylus heterophylla·Quercus mongolica(plot 7), in case of shrub second layer, the dominant species were Stephanandra incisa(plot 1), Lindera obtusiloba(plot 2), Lespedeza maximowiczii(plot 3·4), Philadelphus schrenckii(plot 5), Staphylea bumalda·Rubus oldhamii(plot 6) and Lindera obtusiloba·Symplocos cinensis for. Pilosa·Eleutherococcus senticosus(plot 7). The dominant species of herbage layer were Artemisia princeps·Glycine soja(plot 1), Parthenocissus tricuspidata·Lathyrus vaniotii·Carex ciliatomarginata(plot 2), Artemisia keiskeana ·Festuca ovina·Carex ciliatomarginata(plot 3), Festuca ovina(plot 4), Lathyrus vaniotii·Adenocaulon himalaicum·Oplismenus undulatifolius(plot 5), Oplismenus undulatifolius(plot 6) and Schisandra chinensis(plot 7).
ScienceON
eArticle연관 검색어 추천
이 검색어로 많이 본 자료
활용도 높은 자료
