<?xml version="1.0" encoding="UTF-8"?>
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<title>멸종위기 야생생물 Ⅰ급 관련 논문</title>
<link href="http://117.16.248.84:8080/xmlui/handle/123456789/734" rel="alternate"/>
<subtitle/>
<id>http://117.16.248.84:8080/xmlui/handle/123456789/734</id>
<updated>2026-05-22T06:13:22Z</updated>
<dc:date>2026-05-22T06:13:22Z</dc:date>
<entry>
<title>멸종위기식물 풍란의 복원 후 시간경과에 따른 생육특성</title>
<link href="http://117.16.248.84:8080/xmlui/handle/123456789/771" rel="alternate"/>
<author>
<name>황, 부영</name>
</author>
<author>
<name>Hwang, Boo Yeong</name>
</author>
<id>http://117.16.248.84:8080/xmlui/handle/123456789/771</id>
<updated>2024-06-04T12:48:18Z</updated>
<published>2019-02-01T00:00:00Z</published>
<summary type="text">멸종위기식물 풍란의 복원 후 시간경과에 따른 생육특성
황, 부영; Hwang, Boo Yeong
The purpose of this study was to analyze the flora and growth characteristic of restoration sites to investigate the efficient restoration method of endangered species of N. falcata. Analysis of investigating the growth medium, flora, growth and interaction of N. falcata by the number and method of attachment, correlation between growth and meteorological factors, coefficient estimate in a logistic regression model for the probability of survival was conducted.1. The floraThe flora of N. falcata habitat site was a total of 48 taxa including 29 families, 45 genera, 40 species and 8 varieties, and restoration site was a total of 48 taxa including 26 families, 42 genera, 43 species and 5 varieties. Among the plant species, 5 taxa were endemic plants in habitat site, and 1 taxa were endemic plant. 2 taxa were naturalized plants only in restoration site. There were a total of 24 taxa for the floristic regional indicator plants in habitat site, and a total of 16 taxa for the floristic regional indicator plants in restoration site. For a quantitative and objective analysis and evaluation of the flora, endemic index in habitat site (10.4%); restroration site (4.2%), specific index in habitat site (50.0%); restoration site (33.4%) and Pte-Q in habitat and restoration site (0.53), unaturalized index (4.2%), urbanized index (0.5%) only in restoration site used in this study.2. Gathering the seeds and investigating the growth medium of N. falcataAs to the result of an analysis of four culture media, including LMWP, MS, MS+Charcoal and Hyponex for an investigation of the appropriate growth medium for the seeds, the width of the plant, the number of leaves, the length of the leaves and the number of roots, overall, the figure of growth were highest in the LMWP culture medium.3. Growth monitoring of N. falcata after restorationAccording to the result of the growth monitoring of N. falcata , The survival rate was 27.0%, the death rate was 24.0%, the loss rate was 48.0%. According to the result of survival status by method of attachment, individual attached to the moss (35.4%) ＞ individual attached to the stone (22.2%) ＞ individual attached to the tree (8.3%) survived in order. According to the result of survival status by number of attachment, 1 individual (28.9%), 2 individuals(27.8%), 3 individuals(26.6%) survived in order.4. Growth of N. falcata over time after restorationAccording to the result of the overall growth rate analysis, shoot number increased to 190%, plant length to 134%, plant width to 121%, leaf number to 126%, and leaf length to 114%, however, the leaf width decreased. According to the result of the growth rate analysis by method of attachment, shoot number, plant length, plant width, leaf number, leaf width, leaf length were all found to have a positive effect on growth. According to the result of the growth rate analysis based on number of attachment, single shoot attached on plants has shown better growth than two or three attachment. Whereas 2 individuals attached to the plant shown better plant width, leaf width and growth. On the other hand, leaf number and leaf length were found to have a positive difference on the growth of 3 individuals. 5. Statistical analysisAccording to the result of analysis of the interaction effect between the method of attachment and the number of attachment after restoration, attachment method of tree, moss was relatively good for growth compared to stone
</summary>
<dc:date>2019-02-01T00:00:00Z</dc:date>
</entry>
<entry>
<title>멸종위기 야생생물Ⅰ급 나도풍란의 서식지 적합성 지수(HSI) 개발 - 다도해해상국립공원을 중심으로 -</title>
<link href="http://117.16.248.84:8080/xmlui/handle/123456789/758" rel="alternate"/>
<author>
<name>김, 선령</name>
</author>
<author>
<name>Kim, Sun Ryoung</name>
</author>
<author>
<name>박, 용수</name>
</author>
<author>
<name>Park, Yong Su</name>
</author>
<author>
<name>심, 윤진</name>
</author>
<author>
<name>Shim, Yun Jin</name>
</author>
<author>
<name>윤, 영준</name>
</author>
<author>
<name>Yoon, Young Jun</name>
</author>
<author>
<name>장, 래하</name>
</author>
<author>
<name>Jang, Rae Ha</name>
</author>
<author>
<name>한, 승현</name>
</author>
<author>
<name>Han, Seung Hyun</name>
</author>
<id>http://117.16.248.84:8080/xmlui/handle/123456789/758</id>
<updated>2024-06-04T13:26:51Z</updated>
<published>2020-04-30T00:00:00Z</published>
<summary type="text">멸종위기 야생생물Ⅰ급 나도풍란의 서식지 적합성 지수(HSI) 개발 - 다도해해상국립공원을 중심으로 -
김, 선령; Kim, Sun Ryoung; 박, 용수; Park, Yong Su; 심, 윤진; Shim, Yun Jin; 윤, 영준; Yoon, Young Jun; 장, 래하; Jang, Rae Ha; 한, 승현; Han, Seung Hyun
본 연구는 나도풍란(Sedirea japonica (Rchb. f.) Garay &amp; H.R. Sweet)의 문헌조사 및 서식지 현황 조사를 바탕으로 나도풍란의 HSI(Habitat Suitability Index) 모델을 개발하는 것을 목적으로 하며, 이를 통해 향후 나도풍란 대체서식지 평가 및 복원 연구의 기초 자료로 제시하고자 한다. 현재 나도풍란은 국내 자연 상태에서 절멸된 것으로 간주되어 멸종위기 야생생물 1급으로 지정되었고 멸종위기 야생생물 보전 종합계획(2018~2027)에 따라 우선복원대상종(총 25종)으로 선정되었다. 나도풍란의 서식변수로 최고우기 월강수량, 연간 기온 차이, 월평균 기온차, 최저기온, 해발고도, 경사, 도로와의 거리를 제안하였다. 전문가 자문을 통해 상대습도, 안개일수, 광환경, 향, 인위적 남획 등이 추가적으로 제시되었으나 데이터 구축 여부를 고려하여 상대습도, 향, 인위적 남획을 선정하였다. 이중 인위적 남획을 간접적으로 평가하기 위해 보호지역 포함 여부를 제시하였다. 최고우기 월강수량, 연간 기온 차이, 월평균 기온차, 최저기온 등은 모두 적합하나 나도풍란에 대한 자료가 부족하여 변수로 선정되지 않았다. 위의 과정을 통해 최종 변수는 상대습도, 해발고도, 경사, 향, 인위적 남획으로 선정하였다. 문헌조사와 현장조사 결과 및 전문가 자문을 통하여 SI(Suitability Index) 모델과 HSI 모델을 개발하였으며, 적용 가능성을 시험하기 위해 대상지에 적용하였다. HSI가 가장 높은 값은 1.0이며 해당 면적은 16,040,000㎡로 나타났다. 그 외0.8(148,280,000㎡), 0.7(57,940,000㎡), 0.6(5,320,000㎡)으로 도출되었다. 그 결과, 다도해해상국립공원에서 HSI가 1.0인 지역을 나도풍란의 대체서식지로 제시하였다. 이 모델은 나도풍란의 서식지 평가와 복원 모델의 제시하는데 중요한 근거가 될 것이며, 특히 나도풍란의 대체서식지 선정과 평가에 활용도가 매우 높다. 그러나 본 연구결과로 제시된 나도풍란의 대체서식지는 국내·외 구축되어 있는 공간 자료의 한계로 100 m×100 m의 격자 크기로 평가되었다. 따라서 일차적인 후보지 선정에 의미가 있으며, 세부 대상지 확정을 위해 서는 이차적인 현장조사가 필요하다. 후속연구를 통해 국내 미기후에 대한 공간자료와 나도풍란 서식지에 대한 장기 모니터링 데이터가 구축된다면 보다 정밀한 공간분석으로 세부적인 대체서식지를 제시할 수 있을 것이다. 서식지 적합성 모델의 정확도를 높이기 위해 향후 나도풍란의 서식지에 대한 다양한 실태조사를 구축해야 할 것으로 보인다.; The purpose of this study was conducted to suggest the HSI(Habitat Suitability Index) model of Sedirea japonica (Rchb. f.) Garay &amp; H.R. Sweet based on the research on the ecological and habitat status of S. japonica and the literature research on the HSI model. Currently, S. japonica is considered extinct in the wild and has been designated as an endangered wildlife species level 1. Thus, S. japonica has been selected as a priority restoration target species(a total of 25 species) according to the Endangered Wildlife Conservation Comprehensive Plan (2018~2027). The habitat variables of S. japonica are the relative humidity, the altitude, the gradient, the slope, and the artificial over-exploitation. Based on the existing literature of S. japonica, the results of field surveys and expert opinions, the SI(Suitability Index) model and HSI model were developed and applied to the site to examine the applicability of the HSI model. The SI model and HSI model were developed through literature search, field survey results, and expert advice, and applied to the site to test the applicability. The highest value for HSI was 1.0, with an area of 16,040,000 m2, and 0.9 with an area of 106,510,000 m2. As a result, the area with an HSI of 1.0 was presented as an alternative habitat for the S. japonica. As a result, the area with 1.0 of HSI value in Dadohaehaesang National Park was proposed as an alternative habitat for S. japonica. The HSI model can be an important basis for the habitat evaluation and restoration model of S. japonica. In particular, it is highly applicable to the selection and evaluation of alternative habitats for S. japonica. However, the alternative habitat of S. japonica presented as a result of this study was evaluated by a 100 m × 100 m grid size due to the limitations of the spatial data established. Therefore, it is meaningful to select a primary candidate site, and a secondary on-site investigation is necessary to determine the detailed target site. If the spatial data on the micro-climate and the long-term monitoring of the S. japonica habitat are constructed through follow-up studies, detailed alternative habitats can be suggested by the more precise spatial analysis. However, as a future study, various status-finding data on the habitat of S. japonica should be established to improve the accuracy of the existing HSI model.
</summary>
<dc:date>2020-04-30T00:00:00Z</dc:date>
</entry>
<entry>
<title>멸종위기 야생생물Ⅰ급 털복주머니란 서식지 복원을 위한 서식지 적합성 지수(HSI) 개발</title>
<link href="http://117.16.248.84:8080/xmlui/handle/123456789/755" rel="alternate"/>
<author>
<name>김, 선령</name>
</author>
<author>
<name>Kim, Sun Ryoung</name>
</author>
<author>
<name>박, 용수</name>
</author>
<author>
<name>Park, Yong Su</name>
</author>
<author>
<name>심, 윤진</name>
</author>
<author>
<name>Shim, Yun Jin</name>
</author>
<author>
<name>윤, 영준</name>
</author>
<author>
<name>Yoon, Young Jun</name>
</author>
<author>
<name>이, 동진</name>
</author>
<author>
<name>Lee, Dong Jin</name>
</author>
<author>
<name>장, 래하</name>
</author>
<author>
<name>Jang, Rae Ha</name>
</author>
<author>
<name>한, 승현</name>
</author>
<author>
<name>Han, Seung Hyun</name>
</author>
<id>http://117.16.248.84:8080/xmlui/handle/123456789/755</id>
<updated>2024-06-04T13:25:23Z</updated>
<published>2020-08-31T00:00:00Z</published>
<summary type="text">멸종위기 야생생물Ⅰ급 털복주머니란 서식지 복원을 위한 서식지 적합성 지수(HSI) 개발
김, 선령; Kim, Sun Ryoung; 박, 용수; Park, Yong Su; 심, 윤진; Shim, Yun Jin; 윤, 영준; Yoon, Young Jun; 이, 동진; Lee, Dong Jin; 장, 래하; Jang, Rae Ha; 한, 승현; Han, Seung Hyun
This study aimed to develop the HSI (Habitat Suitability Index) model of Cypripedium guttatum. and to verify this model by applying to the candidate sites for replacement habitat. The development of HSI and SI (Suitability Index) model was conducted based on the existing literature, field surveys, and expert opinions for information on ecological habitat characteristics. Seven variables were selected as habitat variables including mean maximum temperature in Jul.-Aug., lighting, slope, altitude, effective soil depth, soil texture, and artificial overexploitation (i.e. protected areas). HSI model was developed for C. guttaum based on these variables. This HSI model showed high applicability to selection and evaluation of replacement habitats for C. guttaum. Our findings could provide the basic information on habitat assessment to prevent the extinction of endangered C. guttatum. However, since there is a limitation that the survey data were insufficient, further field surveys should be conducted on several habitat types to improve the accuracy of the HSI model.
</summary>
<dc:date>2020-08-31T00:00:00Z</dc:date>
</entry>
<entry>
<title>희귀 및 멸종위기식물 광릉요강꽃 개체군 구조 특성 및 지속성</title>
<link href="http://117.16.248.84:8080/xmlui/handle/123456789/754" rel="alternate"/>
<author>
<name>이, 동형</name>
</author>
<author>
<name>Lee, Dong hyoung</name>
</author>
<id>http://117.16.248.84:8080/xmlui/handle/123456789/754</id>
<updated>2024-06-04T12:54:21Z</updated>
<published>2022-02-01T00:00:00Z</published>
<summary type="text">희귀 및 멸종위기식물 광릉요강꽃 개체군 구조 특성 및 지속성
이, 동형; Lee, Dong hyoung
광릉요강꽃(Cypripedium Japonicum Thunb.)은 한국, 중국, 일본에 분포하는 동아시아 특산식물로, 지구 수준의 IUCN Red List “위기(Endangered, EN)”로 평가되며, 한국의 국가 Red List에서는 “멸종위기(Critically Endangered, CR)”에 포함된다. 본 연구는 광릉요강꽃 자생지에서 8년 동안 수행된 개체통계학적(demographic) 모니터링 자료를 바탕으로 개체군 구조 및 변화양상을 분석하고, 개체군의 지속성에 대하여 예측하였다. 광릉요강꽃은 국내 7개 지역(포천, 가평, 화천, 춘천, 영동, 무주, 광양)에서 자생지가 관찰되었고, 15개 아개체군에 4,360개체가 생육하는 것으로 확인되었다. 이 중 조사된 4개 지역(포천, 광양, 화천, 춘천)에서 개체군 크기 및 구조는 지역별로 상이하였으며, 일부 인위적 관리가 개체군 크기 및 구조 변화에 중요한 영향을 미치고 있었다. 8년 동안 개체수 변화를 모니터링 결과를 바탕으로 분석한 광릉요강꽃의 개체군 생존력(Population Viability Analysis, PVA)은 지역별로 다른 결과를 보였다. 향후 1세기 안에 멸절할 가능성은 포천 0.00%, 광양 53.95%, 춘천 56.26%, 화천 96.90%로 예측되었다. 모니터링이 수행된 위 연구지역은 현지 내 보호시설로 인위적 출입을 제한하고 있어 광릉요강꽃의 최대 위협요인인 인위적 남획 변수가 개체군 생존력에 반영되지 않았다. 즉, 실질적인 멸절 위험도는 본 연구에서 추정된 값보다 현저하게 클 것으로 예상된다. 국내 광릉요강꽃 개체군의 멸절위험도의 객관적 판단을 위해서는 향후 다양한 위협요인이 있는 여러 지역의 개체군 정보가 반영될 필요가 있으며, 국내·외로 광릉요강꽃 개체군에 대한 개체통계학적 모니터링을 확대해 나가야 할 것이다.
</summary>
<dc:date>2022-02-01T00:00:00Z</dc:date>
</entry>
</feed>
