• 제목/요약/키워드: maximowiczii$

검색결과 149건 처리시간 0.028초

설악산 국립공원의 등산로 훼손 및 주연부식생 (Use Impacts on Environmental Deteriorations of and around Trails in Soraksan National Park)

  • 이준우;오구균;권태호
    • 한국환경생태학회지
    • /
    • 제10권2호
    • /
    • pp.191-204
    • /
    • 1997
  • 설악산 국립공원의 8개 주요 등산로에 대해 이용강도에 따른 등산로 및 주변 환경훼손상태를 조사하였다. 총 31.9km, 188개 지점에서 등산로 상태를 조사한 바, 등산로폭, 나지노출폭, 최대침식깊이 및 등산로물매는 이용강도에 따른 차이가 인정되었다. 훼손유형의 출현빈도는 뿌리노출, 노출확대, 암석노출, 분기 등의 순이였으며, 이들 지점의 등산로 상태는 건전한 지점과 뚜렷한 차이를 보였다. 등산로 주변의 환경피해도 4등급 이상인 나지의 면적은 전체 10,864m$^{2}$이며 희운각대피소-무너미고개 구간이 4,560m$^{2}$로서 가장 많이 발생되어 있었다. 주연부 상층식생의 우점종은 신갈나무였고, 하층식생은 계곡부에서 서어나무와 조록싸리, 능선부에서는 서어나무, 털진달래, 미역줄나무가 우점종이었다. 주연부 하층식생의 피도 및 개체수는 특이하게 이용강도가 높은 무너미고개-대청봉 구간에서 가낭 높았으며, 등산로간의 하층식생의 종구성은 대체로 이질적이었다.

  • PDF

소흑산도(小黑山島)와 홍도(紅島)의 식물자원(植物資源) 조사(調査) (Investigation of Vegetation in Soheuksan-do and Hong-do)

  • 이종석;김일중
    • 농업과학연구
    • /
    • 제5권2호
    • /
    • pp.145-148
    • /
    • 1978
  • 우리나라의 최남서단(最南西端)에 위치(位置)하는 전라남도(全羅南道) 신안군(新案郡) 흑산면(黑山面)에 속(屬)하는 소흑산도(小黑山島)와 홍도(紅島)의 식물자원(植物資源)을 조사(調査)하였다. 소흑산도(小黑山島)의 식물상(植物相)은 매우 다양(多樣)하였으며, 이중 출현빈도(出現頻度)가 많고 관상식물(觀賞植物)로도 개발(開發) 가능(可能)한 27과(科) 54종(種)을 보고(報告)하였다. 그중 난과식물(蘭科植物)은 새우난(Calanthe discolor)등(等) 8종(種)이었다. 홍도(紅島)의 식물상(植物相)은 소흑산도(小黑山島)와 매우 유사(類似)하였으나 덜 풍부(豊富)해 보였으며, 아직 미기록(未記錄)된 1종(種)을 추가보고(追加報告)하였다. 풍란(風蘭), 석곡 등(等) 기호도(嗜好度)가 높은 관상식물(觀賞植物)은 이미 절종상태(絶種狀態)에 이르고 있어 이의 보호(保護)가 절실(切實)히 요청(要請)되었다.

  • PDF

노랑무늬붓꽃(Iris odaesanensis Y.N.Lee) 자생지의 환경특성 (Environmental Characteristics of Habitats of Iris odaesanensis Y.N.Lee)

  • 천경식;한준수;서원복;김경아;유기억
    • 한국환경과학회지
    • /
    • 제19권11호
    • /
    • pp.1337-1353
    • /
    • 2010
  • This study intended to investigate environmental factors including soil and vegetation in order to understand the environmental and ecological characteristics of 12 different habitats of Iris odaesanensis. These habitats, according to investigations, are mostly located at elevation of 280 m to 1,555 m with angles of inclination ranging from 2 degree to 30 degrees. A total of 273 vascular plants are identified in 23 quadrates of 12 habitats. Dominant species of woody plants in 12 habitats are represented as Quercus mongolica in the tree layer (T1) and the subtree (T2) layer, and Lespedeza maximowiczii, Lindera obtusiloba, Rhododendron schlippenbachii in the shrub (S) layer. The importance value of Iris odaesanensis is 9.65%, as regards the herbaceous layer, and 6 highly ranked species such as Carex siderosticta (3.92%), Meehania urticifolia (2.67%), Spodiopogon cotulifer (2.58%), Aconitum pseudolaeve (2.51%), Carex bostrychostigma (2.28%) and Disporum smilacinum (2.09%) are considered to be an affinity with Iris odaesanensis in their habitats. The degree of their average species diversity is 1.32, and that of dominance and evenness are 0.08 and 0.89, respectively. The type of soil is sandy loam and loam, and the average field capacity of soil is 28.31%. Their average organic matter is 16.71%, soil pH 5.29, and available phosphorus is 9.29%. Correlation coefficients analysis based on environmental factors, vegetation and soil analysis shows that the coverage of Iris odaesanensis is correlated with pH and dominance, and species richness is positive related with species diversity.

탐진강 하구역 일대(강진군)의 관속식물상 (Floristic Study of Tamjin River Estuary in Gangjin-gun, Korea)

  • 장현도;임효선;한세희;오아미;오병운;양선규
    • 한국환경과학회지
    • /
    • 제29권6호
    • /
    • pp.579-603
    • /
    • 2020
  • In order to provide fundamental information about the floristic composition of the area along with an assessment of the environmental impact, a floristic study of the vascular plants in the Tamjin River estuary in Gangjin-gun was conducted for a total of nine days, in the period from June 2014 to September 2014. We found that the vascular plants in this region comprised 424 taxa belong to 102 families, 281 genera, 390 species, 5 subspecies, 26 varieties, and 3 forma. Five taxa of Korean endemic plants including Weigela subsessilis (Nakai) L.H.Bailey, Lespedeza maximowiczii var. tricolor (Nakai) Nakai, and Clematis trichotoma Nakai were collected. Two least concern (LC) taxa of rare plants (as designated by the Korea Forest Service) were collected: Hydrocharis dubia (Blume) Backer and Platycladus orientalis (L.) Franco. Ten the floristic regional indicator taxa from the third to the fifth grade were identified: two taxa belonged to grade IV, and eight taxa belonged to grade III. Twenty-four taxa of salt-tolerant plants, including Artemisia fukudo Makino, Carex rugulosa Kuk., and Suaeda glauca (Bunge) Bunge, as well as 44 taxa of aquatic plants, including Najas marina L., Nuphar oguraensis Miki, and Nymphoides indica (L.) Kuntze, were investigated in this region. Fifty-nine taxa of naturalized plants were recorded, among which the following six taxa were plants that caused ecosystem disturbance: Ambrosia artemisiifolia L., Humulus scandens (Lour.) Merr., Lactuca scariola L., Rumex acetosella L., Solidago altissima L., and Symphyotrichum pilosum (Willd.) G.L.Nesom.

지리산 자연생태계보전구역의 식생 (The Actual Vegetation of Nature Ecology Con-servation Area in Mt. Chiri)

  • 김준선;김갑태;주혜란
    • 한국환경생태학회지
    • /
    • 제5권1호
    • /
    • pp.9-24
    • /
    • 1991
  • 지리산 국립공원중 반야봉을 중심으로 피아골과 심원계곡을 포함하는 자연생태계보전구역의 현존식생을 파악하기 위하여 총 43개 조사지의 종조성 및 식생상관에 의하여 삼림군집을 구분하였으며 이를 토대로 현존식생도를 작성하였다. 지리산 자연생태계보전구역의 식생은 냉온대남부에서 아한대에 이르기까지 13개의 삼림군집이 형성되었으며 확인된 삼림군집은 다음과 같다. 1. 졸참나무군집 2. 서어나무군집 3. 졸참나무-서어나무군집 4. 노각나무군집 5. 고로쇠나무군집 6. 까치박달나무군집 7. 들메나무군집 8. 개서나무군집 9. 소나무군집 10. 신갈나무군집 1) 신갈나무-철쭉 하위군집 2) 신갈나무-조록싸리 하위군집 11. 분비나무군집 12. 구상나무군집 1) 구상나무-신갈나무 하위군집 2) 구상나무-잣나무 하위군집 13. 철쭉군집 확인된 삼림식생중에서 졸참나무군집은 해발 700m에서 1,000m에 분포하였으며 서어나무군집, 개서나무군집은 동지역의 계곡부에 분포하였다. 해발 1,000m에서 1,400m에는 신갈나무군집이 그 이상 1,700m까지에는 구상나무군집, 분비나무군집등 아고산대림이 발달하였다.

  • PDF

계룡산 상부 지역의 산림식생 (Forest Vegetation of Upper Zone in Gyeryongsan National Park)

  • 김효정;이미정;이규석;박관수;송호경
    • 환경생물
    • /
    • 제22권1호
    • /
    • pp.127-132
    • /
    • 2004
  • 본 연구는 계룡산 국립공원내 해발 650 m이상의 산림식생을 대상으로 식물사회학적 방법_으로_ 산림군락을 분류하여 계룡산 국립공원 관리에 필요한 기초자료를 제공하고자 수행되었다. 계룡산 상부지역의 총 51개 조사구를 분석한 결과, 산림군락은 신갈나무군락, 서어나무군락, 소나무군락 및 굴참나무군락으로 구분되었다. 신갈나무군락은 29개 조사구에서 나타났으며, 군락 구분종은 신갈나무, 좁은단풍, 천남성, 용수염, 은분취이다. 서어나무군락은 10개 조사구에서 나타났으며, 군락 구분종은 서어나무, 까치박달, 층층나무, 대사초, 산수국이다. 소나무군락은 7개 조사구에서 나타났으며, 군락 구분종은 소나무, 조록싸리, 산딸기, 참억새, 이삭여러, 맑은대쑥, 큰기름새 이다. 굴참나무군락은 5개 조사구에서 나타났으며, 군락 구분종은 굴참나무이다.

한라산 구상나무림의 사면별 식생구조와 치수발생 특성 (Vegetation Structure at the Slope Direction and Characteristic of Seedlings of Abies koreana in Hallasan Mountain)

  • 송국만;강영제;현화자
    • 한국환경과학회지
    • /
    • 제23권1호
    • /
    • pp.39-46
    • /
    • 2014
  • This study surveyed Abies koreana to identify the correlation between its vegetation structure according to its slope direction and seedling establishment in a bid to build basic research data on the changes and conservation of the A. koreana in Hallasan Mountain. The findings of its vegetation structure revealed that in both areas, Importance value was given to the A. koreana for its tree layer, the Taxus cuspidata for its shrub layer, and the Sasa quelpaertensis for its herb layer. However, in the Youngsil area with the tree layer, high importance was given to deciduous broad-leaved trees such as Prunus maximowiczii, Quercus mongolica, and the young species of the A. koreana in the shrub layer that can maintain the A. koreana forest's greater importance in the Jindallebat than in the Youngsil. Thus, the A. koreana forest in the Jindallebat is believed to lastlonger. The findings of correlation between the quantity of seedlings and their location by area revealed that in each tiny quadrat, the A. koreana seedling averaged 5.3 in the Youngsil and 2.9 in the Jindallebat. Both areas were all found to have a positive correlation in terms of rock exposure ratio and dead tree ratio as well as a negative correlation with regard to the cover degree of S. quelpaertensis, the canopy gap, the total vegetation, and the herb layer. It was found that the cover degree of the herb layer in the Youngsil and the S. quelpaertensis in the Jindallebat had the largest impact on the A. koreana seedlings.

Phyllactinia guttata (Wallr. ex Fr.) Lév에 의(依)한 포플러흰가루병(病) (Powdery mildew of Populus spp. caused by Phyllactinia guttata(Waller. ex Fr.) Lév)

  • 이종규;김경희;이창근
    • 한국산림과학회지
    • /
    • 제58권1호
    • /
    • pp.54-59
    • /
    • 1982
  • 10월(月) 중순(中旬)경, 충청남도(忠淸南道)와 강원도임업시험장(江原道林業試驗場)(대전(大田), 춘천(春川)) 묘포장 구내(構內)에서 흰가루병(病)에 감염(感染)된 포플러 도입종(導入種), Populus euramericana, P. deltoides, P. del${\times}$P. max의 여러 clone에서 채취(採取)한 병원균(病原菌)을 형태적(形態的) 특징(特徵)에 의(依)하여 동정(同定)한 결과(結果), Populus spp.에서는 P. tomentosa Carr.에서만 보고(報告)되어 있는 흰가루 병균(病菌)인 Phyllactinia guttata(Wallr. ex Fr.)로 동정(同定)되었고 Populus spp.에서 Phyllactinia gutata에 의(依)한 흰가루병(病)은 우리나라에서는 처음으로 보고(報告)되었다. 발병상황(發病狀況)을 조사(調査)한 결과(結果) P. deltoides R-89에서 가장 심하게 발병(發病)되었다.

  • PDF

도시지역 곰솔림의 식생복원모델 (Vegetation Restoration Model of Pinus thunbergii in Urban Areas)

  • 김석규
    • 환경영향평가
    • /
    • 제20권2호
    • /
    • pp.151-162
    • /
    • 2011
  • The purpose of this study is suggest to restoration model of Pinus thunbergii in Saha-gu, Busan Metropolitan City. The result of this study is summarized as follows; As the results of this study, vegetation restoration model is presented by separating community planting and edge planting. The community planting species of tree layer were Pinus thunbergii and Quercus acutissima and Quercus dentata and Quercus serrata and Quercus alienna and Quercus variabilis. The community planting species of subtree layer were Platycarya strobilacea and Prunus sargentii and Styrax japonica and Eurya japonica and Morus bombycis. The community planting species of shrub layer are Ulmus pavifolia and Ulmus davidiana and Lindera obtusiloba and Elaeagnus macrophylla and Mallotus japonicus and Ligustrum obtusifolium and Sorbus alnifolia and Rhus trichocarpa and Zanthoxylum schinifolium and Rosa wichuraiana and Rhus chinensis and Viburnum erosum and Rhododendron mucronulatum and Rhododendron yedoense and Indigofera pseudotinctoria. And the planting species of edge vegetation are Japanese Angelica and Symplocos chinensis and Pittosporum tobira and Lespedeza maximowiczii and Lespedeza bicolor and Rubus coreanus and Rubus idaeus and Vitis thunbergii and Ampelopsis brevipedunculata and Rosa multiflora. Considering the population of individuals up to layers in each $400m^2$ area, it was composed of 24 in tree layer, 35 in subtree layer, 410 in shrub layer and 34% herb layer in the Pinus thunbergii community. And the average of breast-high area and canopy area was $10,852cm^2$ in tree layer, in subtree layer $1,546cm^2$, in shrub layer $1,158,660cm^2$. The shortest distance between trees was calculated as 2.0m in tree layer, 1.9m in subtree layer.

도시림 식생의 생태적 특성과 복원모델 (Ecological Characteristics and Restoration Model of Vegetation in the Urban Forest)

  • 김석규;주경중;남정칠;박승범
    • 한국환경복원기술학회지
    • /
    • 제13권2호
    • /
    • pp.80-94
    • /
    • 2010
  • The purpose of this study is suggest to restoration model of Pinus thunbergii in Saha-gu, Busan. The result of this study is summarized as follows. As the results of this study, vegetation restoration model is presented by separating community planting and edge planting. In community planting, as a group of canopy, there are 6 species; Pinus thunbergii, Quercus acutissima, Quercus dentata, Quercus serrata, Quercus alienna, Quercus variabilis. As a group of understory, there are 5 species; Platycarya strobilacea, Prunus sargentii, Styrax japonica, Eurya japonica, Morus bombycis. Also as a group of shrub, there were 15 kinds of species; Ulmus pavifolia, Ulmus davidiana, Lindera obtusiloba, Elaeagnus macrophylla, Mallotus japonicus, Ligustrum obtusifolium, Sorbus alnifolia, Rhus trichocarpa, Zanthoxylum schinifolium, Rosa wichuraiana, Rhus chinensis, Viburnum erosum, Rhododendron mucronulatum, Rhododendron yedoense, Indigofera pseudotinctoria. And as a group of edge vegetation, there were 10 kinds of species; Japanese Angelica, Symplocos chinensis, Pittosporum tobira, Lespedeza maximowiczii, Lespedeza bicolor, Rubus coreanus, Rubus idaeus, Vitis thunbergii, Ampelopsis brevipedunculata, Rosa multiflora. Vegetation restoration models of Pinus thunbergii community were calculated the units $400m^2$ for the average populations of the woody layer is 24 in canopy layer, 35 in understory layer, 410 in shrub layer, 34% herbaceous layer ground cover. And the average of breast-high area and canopy area is $10,852cm^2$ in canopy layer, in understory layer $1,546cm^2$, in shrub layer $1,158,660cm^2$. The shortest distance between trees is calculated as 2.0m in canopy layer, 1.9m in understory layer.